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Global Change Abstracts The Swiss Contribution - SCNAT

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<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong><br />

<strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong><br />

O8.1


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong><br />

<strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong><br />

August 2007 – January 2008<br />

Published and distributed by:<br />

ProClim-<br />

Forum for Climate and <strong>Global</strong> <strong>Change</strong><br />

<strong>Swiss</strong> Academy of Sciences<br />

Schwarztorstrasse 9 | CH-3007 Bern<br />

T (+41 31) 328 23 23 | F (+41 31) 328 23 20<br />

proclim@scnat.ch | www.proclim.ch<br />

Editor:<br />

Gabriele Müller-Ferch, ProClimmueller@scnat.ch<br />

Source:<br />

Science Citation Index®<br />

Social Science Citation Index®<br />

Institute for Scientific Information®<br />

Cover Pictures:<br />

Library: Image provided by H. Diaz<br />

Issue: GCA 08.1, May 2008, Bern, Switzerland


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Contents 3<br />

Contents<br />

Concept and Methods 4<br />

Short List of all <strong>Abstracts</strong> 5<br />

1 Earth System Process Studies and Methodologies 37<br />

1.1 Atmosphere 37<br />

1.2 Terrestrial Ecosystems 67<br />

1.3 Soil and Litosphere 113<br />

1.4 Cryosphere 121<br />

1.5 Oceans and Fresh Water Systems 126<br />

1.6 Energy Balance 149<br />

1.7 Coupled Systems and Cycles 151<br />

2 Past <strong>Global</strong> <strong>Change</strong>s 156<br />

3 Human Dimensions 184<br />

4 Mitigation and Adaptation Technologies 194<br />

5 General Topics 200<br />

Index of Authors 208<br />

Index of Disciplines 229


4 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Methods and Statistic<br />

Concept and Methods<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong>: <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong><br />

(GCA) is a compendium of abstracts for papers on<br />

the topic of global environmental change. <strong>The</strong><br />

abstracts are written or co-authored by <strong>Swiss</strong> scientists<br />

and other experts working in Switzer land.<br />

<strong>The</strong> papers are published in one of the 6000 journals<br />

covered by the data bases Science Citation<br />

Index® and Social Sciences Citation Index®, which<br />

are compiled by the Institute for Scientific<br />

Information®.<br />

A total of 447 papers that were published during<br />

the period August 2007 – January 2008 are included<br />

in this issue. <strong>The</strong>se papers are classified according<br />

to the following categories, which are also<br />

used to order the abstracts in GCA (refer to the<br />

Table of Contents):<br />

1 Earth system process studies and<br />

methodologie<br />

1.1 Atmosphere<br />

1.2 Terrestrial Ecosystems<br />

1.3 Soil and Lithosphere<br />

1.4 Cryosphere<br />

1.5 Ocean/Fresh Water Systems<br />

1.6 Energy Balance<br />

1.7 Coupled Systems and Cycles<br />

2 Past <strong>Global</strong> <strong>Change</strong>s<br />

3 Human Dimensions<br />

4 Mitigation and Adaptation Technologies<br />

5 General Topics<br />

<strong>The</strong> papers are also referenced by an alphabetical<br />

list of authors and by scientific discipline<br />

(as preassigned by the Institute for Scientific<br />

Information®).<br />

We use three different searches to identify the<br />

papers in GCA, namely: (i) a search in both databases<br />

mentioned above for the names of the principal<br />

investigators and their coworkers contained in<br />

the ProClim- Infosystem (about 800 names) or for<br />

projects with Switzer land as a country of origin;<br />

(ii) a search for additional <strong>Swiss</strong> papers that have<br />

been published in a selection of journals chosen<br />

from the Science Citation Index® based on the<br />

themes they cover (using “journal catagory codes”<br />

assigned by the database producer); (iii) a search<br />

in the database Social Sciences Citation Index® for<br />

<strong>Swiss</strong> papers in the social sciences that contain<br />

one of over 50 keywords on the topic of global<br />

change. ProClim- staff then scan these selected<br />

papers to determine which are relevant for inclusion<br />

in GCA.<br />

GCA is available as PDF document only and is<br />

distributed by e-mail. Please send your request to<br />

proclim@scnat.ch. As a novelty, hyperlinks to the<br />

full text are included (in blue color, sources of<br />

the articles) whenever possible. So you can easily<br />

find the scientific article on the web by clicking<br />

on the corresponding link in the electronic GCA.<br />

Searching for keywords is also possible.<br />

You can also find all papers published in GCA on<br />

the ProClim- web site at www.proclim.ch/<br />

Publications.html. On this site you will find a<br />

database including all <strong>Swiss</strong> articles of the GCAs.<br />

If you are interested in ordering a copy of a paper<br />

quoted in this issue, you can get further information<br />

in the ProClim- database, for example the<br />

address of the first author. A double click on the<br />

selected article will show you more detailed information<br />

not printed in the following document.<br />

If you think a paper should be published in an<br />

issue of GCA, you can send it to ProClim- and we<br />

will consider including it in a future issue. We<br />

hope that <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong>: <strong>The</strong> <strong>Swiss</strong><br />

<strong>Contribution</strong> will facilitate the exchange of<br />

information and with it the interdisciplinarity<br />

among the global change research community.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong> 5<br />

Short List of all <strong>Abstracts</strong><br />

1 Earth System Process Studies and Methodologies<br />

Identification of the mass spectral signature of organic aerosols from wood burning emissions<br />

(08.1-1)<br />

Alfarra M R, Prevot A S H, Szidatt S, Sandradewi J, Weimer S, Lanz V A, Schreiber D, Mohr M, Baltensperger U<br />

A new atmospheric aerosol phase equilibrium model (UHAERO): organic systems (08.1-2)<br />

Amundson N R, Caboussat A, He J W, Martynenko A V, Landry C, Tong C, Seinfeld J H<br />

Equilibrium sorption of gaseous organic chemicals to fiber filters used for aerosol studies (08.1-3)<br />

Arp H P H, Schwarzenbach R P, Goss K U<br />

Interference of organic signals in highly time resolved nitrate measurements by low mass resolution<br />

aerosol mass spectrometry (08.1-4)<br />

Bae M S, Schwab F J, Zhang Q, Hogrefe O, Demerjian K L, Weimer A, Rhoads K, Orsini D, Venkatachari P, Hopke P K<br />

Small-scale cloud processes and climate (08.1-5)<br />

Baker M B, Peter T<br />

Chemical analysis of atmospheric aerosols (08.1-6)<br />

Baltensperger U, Prevot A S H<br />

Entering into the “greenhouse century”: Recent record temperatures in Switzerland are comparable<br />

to the upper temperature quantiles in a greenhouse climate (08.1-7)<br />

Beniston M<br />

Civil Aircraft for the regular investigation of the atmosphere based on an instrumented container:<br />

<strong>The</strong> new CARIBIC system (08.1-8)<br />

Brenninkmeijer C A M, Crutzen P, Boumard F, Dauer T, Dix B, Ebinghaus R, Filippi D, Fischer H, Franke H, Friess<br />

U, Heintzenberg J, Helleis F, Hermann M, Kock H H, Koeppel C, Lelieveld J, Leuenberger M, Martinsson B G,<br />

Miemczyk S, Moret H P, Nguyen H N, Nyfeler P, Oram D, Osullivan D, Penkett S, Platt U, Pupek M, Ramonet M,<br />

Randa B, Reichelt M, Rhee T S, Rohwer J, Rosenfeld K, Scharffe D, Schlager H, Schumann U, Slemr F, Sprung D,<br />

Stock P, Thaler R, Valentino F, van Velthoven P, Waibel A, Wandel A, Waschitschek K, Wiedensohler A, Xueref Remy<br />

I, Zahn A, Zech U, Ziereis H<br />

Fires and climate linked in nineteenth century (08.1-9)<br />

Brönnimann S<br />

Reconstructing the quasi-biennial oscillation back to the early 1900s (08.1-10)<br />

Brönnimann S, Annis J L, Vogler C, Jones P D<br />

Temporal and spatial temperature variability and change over Spain during 1850-2005 (08.1-11)<br />

Brunet M, Jones P D, Sigro J, Saladie O, Aguilar E, Moberg A, Della Marta P M, Lister D, Walther A, Lopez D<br />

A concept for a satellite mission to measure cloud ice water path, ice particle size, and cloud altitude<br />

(08.1-12)<br />

Bühler S A, Jimenez C, Evans K F, Eriksson P, Rydberg B, Heymsfield A J, Stubenrauch C J, Lohmann U, Emde C, John<br />

V O, Sreerekha T R, Davis C P<br />

Concentration profiles of particles settling in the neutral and stratified atmospheric boundary layer<br />

(08.1-13)<br />

Chamecki M, van Hout R, Meneveau C, Parlange M B<br />

37


6<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

<strong>The</strong> influence of small aerosol particles on the properties of water and ice clouds (08.1-14)<br />

Choularton T, Bower K N, Weingartner E, Crawford I, Coe H, Gallagher M W, Flynn M, Crosier J, Connolly P, Targino<br />

A, Alfarra M R, Baltensperger U, Sjogren S, Verheggen B, Cozic J, Gysel M<br />

Limits on climate sensitivity derived from recent satellite and surface observations (08.1-15)<br />

Chylek P, Lohmann U, Dubey M, Mishchenko M, Kahn R, Ohmura A<br />

Long-term trend analysis of aerosol variables at the high-alpine site Jungfraujoch (08.1-16)<br />

Collaud Coen M, Weingartner E, Nyeki S, Cozic J, Henning S, Verheggen B, Gehrig R, Baltensperger U<br />

Atmospheric blocking: space-time links to the NAO and PNA (08.1-17)<br />

Croci Maspoli M, Schwierz C, Davies H C<br />

FinROSE - middle atmospheric chemistry transport model (08.1-18)<br />

Damski J, Thlix L, Backman L, Taalas P, Kulmala M<br />

Doubled length of western European summer heat waves since 1880 (08.1-19)<br />

Della Marta P M, Haylock M R, Luterbacher J, Wanner H<br />

Summer heat waves over western Europe 1880-2003, their relationship to large-scale forcings and<br />

predictability (08.1-20)<br />

Della Marta P M, Luterbacher J, von Weissenfluh H, Xoplaki E, Brunet M, Wanner H<br />

Effects of convective ice lofting on H 2O and HDO in the tropical tropopause layer (08.1-21)<br />

Dessler A E, Hanisco T F, Füglistaler S<br />

Some factors in the design of a regional prediction model: an examination based upon two MAP<br />

events (08.1-22)<br />

Didone M, Lüthi D, Davies H C<br />

Föhn in the Rhine Valley during MAP: A review of its multiscale dynamics in complex valley geo<br />

metry (08.1-23)<br />

Drobinski P, Steinacker R, Richner H, Baumann Stanzer K, Beffrey G, Benech B, Berger H, Chimani B, Dabas A,<br />

Dorninger M, Dürr B, Flamant C, Frioud M, Furger M, Gröhn I, Gubser S, Gutermann T, Häberli C, Häller<br />

Scharnhorst E, Ratheiser G, Ruffieux D, Seiz G, Spatzierer M, Tschannett S, Vogt S, Werner R, Zängl G<br />

Multimodel projections of stratospheric ozone in the 21st century (08.1-24)<br />

Eyring V, Waugh D W, Bodeker G E, Cordero E, Akiyoshi H, Austin J, Beagley S R, Boville B A, Braesicke P, Brühl C,<br />

Butchart N, Chipperfield M P, Dameris M, Deckert R, Deushi M, Frith S M, Garcia R R, Gettelman A, Giorgetta M<br />

A, Kinnison D E, Mancini E, Manzini E, Marsh D R, Matthes S, Nagashima T, Newman P A, Nielsen J E, Pawson S,<br />

Pitari G, Plummer D A, Rozanov E, Schraner M, Scinocca J F, Semeniuk K, Shepherd T G, Shibata K, Steil B, Stolarski<br />

R S, Tian W, Yoshiki M<br />

Middle atmosphere water vapour and dynamical features in aircraft measurements and ECMWF<br />

analyses (08.1-25)<br />

Feist D G, Geer A J, Müller S, Kämpfer N<br />

An improved low-flow thermodenuder (08.1-26)<br />

Fierz M, Vernooij M G C, Burtscher H<br />

Dynamics of orographically triggered banded convection in sheared moist orographic flows<br />

(08.1-27)<br />

Fuhrer O, Schär C


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong> 7<br />

A satellite- and model-based assessment of the 2003 Russian fires: Impact on the Arctic region<br />

(08.1-28)<br />

Generoso S, Bey I, Attie J L, Breon F M<br />

GEM/POPs: a global 3-D dynamic model for semi-volatile persistent organic pollutants - Part 1:<br />

Model description and evaluations of air concentrations (08.1-29)<br />

Gong S L, Huang P, Zhao T L, Sahsuvar L, Barrie L A, Kaminski J W, Li Y F, Niu T<br />

A global model study of ozone enhancement during the August 2003 heat wave in Europe (08.1-30)<br />

Guerova G, Jones N<br />

Velocity and temperature derivatives in high-Reynolds-number turbulent flows in the atmospheric<br />

surface layer. Part 1. Facilities, methods and some general results (08.1-31)<br />

Gulitski G, Kholmyansky M, Kinzelbach W, Lüthi B, Tsinober A, Yorish S<br />

Velocity and temperature derivatives in high-Reynolds-number turbulent flows in the atmospheric<br />

surface layer. Part 2. Accelerations and related matters (08.1-32)<br />

Gulitski G, Kholmyansky M, Kinzelbach W, Lüthi B, Tsinober A, Yorish S<br />

Velocity and temperature derivatives in high-Reynolds-number turbulent flows in the atmospheric<br />

surface layer. Part 3. Temperature and joint statistics of temperature and velocity derivatives<br />

(08.1-33)<br />

Gulitski G, Kholmyansky M, Kinzelbach W, Lüthi B, Tsinober A, Yorish S<br />

Comparison and synergy of stratospheric ozone measurements by satellite limb sounders and the<br />

ground-based microwave radiometer SOMORA (08.1-34)<br />

Hocke K, Kämpfer N, Ruffieux D, Froidevaux L, Parrish A, Boyd I, von Clarmann T, Steck T, Timofeyev Y M, Polyakov<br />

A V, Kyrola E<br />

Atmospheric predictability at synoptic versus cloud-resolving scales (08.1-35)<br />

Hohenegger C, Schär C<br />

Predictability and error growth dynamics in cloud-resolving models (08.1-36)<br />

Hohenegger C, Schär C<br />

Upper-tropospheric flow features and the Alps: An overview (08.1-37)<br />

Hoinka K P, Davies H C<br />

GEM/POPs: a global 3-D dynamic model for semi-volatile persistent organic pollutants - Part 2:<br />

<strong>Global</strong> transports and budgets of PCBs (08.1-38)<br />

Huang P, Gong S L, Zhao T L, Neary L, Barrie L A<br />

Validation of Aura Microwave Limb Sounder Ozone by ozonesonde and lidar measurements<br />

(08.1-39)<br />

Jiang Y B, Froidevaux L, Lambert A, Livesey N J, Read W G, Waters J W, Bojkov B, Leblanc T, Mcdermid I S, Godin<br />

Beekmann S, Filipiak M J, Harwood R S, Fuller R A, Daffer W H, Drouin B J, Cofield R E, Cuddy D T, Jarnot R F,<br />

Knosp B W, Perun V S, Schwartz M J, Snyder W V, Stek P C, Thurstans R P, Wagner P A, Allaart M, Andersen S B,<br />

Bodeker G E, Calpini B, Claude H, Coetzee G, Davies J, de Backer H, Dier H, Fujiwara M, Johnson B, Kelder H, Leme<br />

N P, Koenig Langlo G, Kyro E, Laneve G, Fook L S, Merrill J, Morris G, Newchurch M, Oltmans S J, Parrondos M C,<br />

Posny F, Schmidlin F, Skrivankova P, Stubi R, Tarasick D, Thompson A, Thouret V, Viatte P, Vomel H, von der Gathen<br />

P, Yela M, Zablocki G<br />

<strong>The</strong> impact of reducing the maximum speed limit on motorways in Switzerland to 80 km h(-1) on<br />

emissions and peak ozone (08.1-40)<br />

Keller J, Andreani Aksoyoglu S, Tinguely M, Flemming J, Heldstab J, Keller M, Zbinden R, Prevot A S H


8<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

<strong>The</strong> evolution of ERA-40 surface temperatures and total ozone compared to observed <strong>Swiss</strong> time<br />

series (08.1-41)<br />

Kunz H, Scherrer S C, Liniger M A, Appenzeller C<br />

<strong>Global</strong> model simulations of the impact of ocean-going ships on aerosols, clouds, and the radiation<br />

budget (08.1-42)<br />

Lauer A, Eyring V, Hendricks J, Joeckel P, Lohmann U<br />

Measurements of OVOCs and NMHCs in a swiss highway tunnel for estimation of road transport<br />

emissions (08.1-43)<br />

Legreid G, Reimann S, Steinbacher M, Stähelin J, Young D, Stemmler K<br />

A photochemical modeling study of ozone and formaldehyde generation and budget in the Po basin<br />

(08.1-44)<br />

Liu L, Andreani Aksoyoglu S, Keller J, Ordonez C, Junkermann W, Hak C, Braathen G O, Reimann S, Astorga Llorens<br />

C, Schultz M, Prevot A S H, Isaksen I S A<br />

Cloud microphysics and aerosol indirect effects in the global climate model ECHAM5-HAM<br />

(08.1-45)<br />

Lohmann U, Stier P, Hoose C, Ferrachat S, Kloster S, Röckner E, Zhang J<br />

A thermophoretic precipitator for the representative collection of atmospheric ultrafine particles<br />

for microscopic analysis (08.1-46)<br />

Lorenzo R, Kägi R, Gehrig R, Scherrer L, Grobety B, Burtscher H<br />

Evidence for a modest undercount bias in early historical Atlantic tropical cyclone counts (08.1-47)<br />

Mann M E, Sabbatelli T A, Neu U<br />

Efficiency of immersion mode ice nucleation on surrogates of mineral dust (08.1-48)<br />

Marcolli C, Gedamke S, Peter T, Zobrist B<br />

Aerosol scattering as a function of altitude in a coastal environment (08.1-49)<br />

Marshall J, Lohmann U, Leaitch W R, Lehr P, Hayden K<br />

Breaking waves at the tropopause in the wintertime Northern Hemisphere: Climatological analyses<br />

of the orientation and the theoretical LC1/2 classification (08.1-50)<br />

Martius O, Schwierz C, Davies H C<br />

Comparison between backscatter lidar and radiosonde measurements of the diurnal and nocturnal<br />

stratification in the lower troposphere (08.1-51)<br />

Martucci G, Matthey R, Mitev V, Richner H<br />

Counterflow virtual impact or based collection of small ice particles in mixed-phase clouds for the<br />

physico-chemical characterization of tropospheric ice nuclei : Sampler description and first case<br />

study (08.1-52)<br />

Mertes S, Verheggen B, Walter S, Connolly P, Ebert M, Schneider J, Bower K N, Cozic J, Weinbruch S, Baltensperger<br />

U, Weingartner E<br />

A one-dimensional ensemble forecast and assimilation system for fog prediction (08.1-53)<br />

Müller M D, Schmutz C, Parlow E<br />

Ozone air pollution effects on tree-ring growth, delta C-13, visible foliar injury and leaf gas exchange<br />

in three ozone-sensitive woody plant species (08.1-54)<br />

Novak K, Cherubini P, Saurer M, Fuhrer J, Skelly J M, Kräuchi N, Schaub M


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong> 9<br />

Perturbation of the European free troposphere aerosol by North American forest fire plumes during<br />

the ICARTT-ITOP experiment in summer 2004 (08.1-55)<br />

Petzold A, Weinzierl B, Huntrieser H, Stohl A, Real E, Cozic J, Fiebig M, Hendricks J, Lauer A, Law K, Roiger A,<br />

Schlager H, Weingartner E<br />

Long-term variability of daily North Atlantic-European pressure patterns since 1850 classified by<br />

simulated annealing clustering (08.1-56)<br />

Philipp A, Della Marta P M, Jacobeit J, Fereday D R, Jones P D, Moberg A, Wanner H<br />

Remote sensing of aerosol optical depth over central Europe from MSG- SEVIRI data and accuracy<br />

assessment with ground-based AERONET measurements (08.1-57)<br />

Popp C, Hauser A, Foppa N, Wunderle S<br />

Hydrological aspects of the Mesoscale Alpine Programme: Findings from field experiments and<br />

simulations (08.1-58)<br />

Ranzi R, Zappa M, Bacchi B<br />

Ice nucleation of ammonia gas exposed montmorillonite mineral dust particles (08.1-59)<br />

Salam A, Lohmann U, Lesins G<br />

A trajectory-based estimate of the tropospheric ozone column using the residual method (08.1-60)<br />

Schoeberl M R, Ziemke J R, Bojkov B, Livesey N J, Duncan B, Strahan S, Froidevaux L, Kulawik S, Bhartia P K,<br />

Chandra S, Levelt P F, Witte J C, Thompson A M, Cuevas E, Redondas A, Tarasick D W, Davies J, Bodeker G E, Hansen<br />

G, Johnson B J, Oltmans S J, Voemel H, Allaart M, Kelder H, Newchurch M, Godin Beekmann S, Ancellet G, Claude<br />

H, Andersen S B, Kyroe E, Parrondos M C, Yela M, Zablocki G, Moore D, Dier H, von der Gathen P, Viatte P, Stuebi<br />

R, Calpini B, Skrivankova P, Dorokhov V, de Backer H, Schmidlin F J, Coetzee G, Fujiwara M, Thouret V, Posny F,<br />

Morris G, Merrill J, Leong C P, König Langlo G, Joseph E<br />

<strong>The</strong> impact of NOx, CO and VOC emissions on the air quality of Zürich airport (08.1-61)<br />

Schürmann G, Schäfer K, Jahn C, Hoffman H, Bauerfeind M, Fleuti E, Rappenglück B<br />

Dewpoint and humidity measurements and trends at the summit of Mount Washington, New<br />

Hampshire, 1935-2004 (08.1-62)<br />

Seidel T M, Grant A N, Pszenny A A P, Allman D J<br />

Assessment of the performance of ECC-ozonesondes under quasi-flight conditions in the environmental<br />

simulation chamber: Insights from the Juelich Ozone Sonde Intercomparison Experiment<br />

(JOSIE) (08.1-63)<br />

Smit H G J, Straeter W, Johnson B J, Oltmans S J, Davies J, Tarasick D W, Hoegger B, Stubi R, Schmidlin F J, Northam<br />

T, Thompson A M, Witte J C, Boyd I, Posny F<br />

Modelling heavy metal fluxes from traffic into the environment (08.1-64)<br />

Steiner M, Boller M, Schulz T, Pronk W<br />

Ultrafine (aerosol) particles and their agglomerate and aggregate - revised international measuring<br />

convention (08.1-65)<br />

Steinle P<br />

Light induced conversion of nitrogen dioxide into nitrous acid on submicron humic acid aerosol<br />

(08.1-66)<br />

Stemmler K, Ndour M, Elshorbany Y, Kleffmann J, Danna B, George C, Bohn B, Ammann M<br />

Impact of scale and aggregation on the terrestrial water exchange: Integrating land surface models<br />

and Rhone catchment observations (08.1-67)<br />

Stöckli R, Vidale P L, Boone A, Schär C


10<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Direct assessment of international consistency of standards for ground-level ozone: strategy and<br />

implementation toward metrological traceability network in Asia (08.1-68)<br />

Tanimoto H, Mukai H, Sawa Y, Matsueda H, Yonemura S, Wang T, Poon S, Wong A, Lee G, Jung J Y, Kim K R, Lee<br />

M H, Lin N H, Wang J L, Ou Yang C F, Wu C F, Akimoto H, Pochanart P, Tsuboi K, Doi H, Zellwegern C,<br />

Klausenn J<br />

<strong>The</strong> influence of a weakening of the Atlantic meridional overturning circulation on ENSO (08.1-69)<br />

Timmermann A, Okumura Y, An S I, Clement A, Dong B, Guilyardi E, Hu A, Jungclaus J H, Renold M, Stocker T F,<br />

Stouffer R J, Sutton R, Xie S P, Yin J<br />

Aerosols in polar regions: A historical overview based on optical depth and in situ observations<br />

(08.1-70)<br />

Tomasi C, Vitale V, Lupi A, Di Carmine C, Campanelli M, Herber A, Treffeisen R, Stone R S, Andrews E, Sharma S,<br />

Radionov V, von Hoyningen Huene W, Stebel K, Hansen G H, Myhre C L, Wehrli C, Aaltonen V, Lihavainen H,<br />

Virkkula A, Hillamo R, Stroem J, Toledano C, Cachorro V E, Ortiz P, de Frutos A M, Blindheim S, Frioud M, Gausa<br />

M, Zielinski T, Petelski T, Yamanouchi T<br />

Aerosol partitioning between the interstitial and the condensed phase in mixed-phase clouds<br />

(08.1-71)<br />

Verheggen B, Cozic J, Weingartner E, Bower K, Mertes S, Connolly P, Gallagher M W, Flynn M, Choularton T,<br />

Baltensperger U<br />

Alpha-Pinene oxidation in the presence of seed aerosol: Estimates of nucleation rates, growth rates,<br />

and yield (08.1-72)<br />

Verheggen B, Mozurkewich M, Caffrey P, Frick G, Hoppel W, Sullivan W<br />

Dobson total ozone series of Oxford: Reevaluation and applications (08.1-73)<br />

Vogler C, Brönnimann S, Stähelin J, Griffin R E M<br />

Road vehicle emissions of molecular hydrogen (H-2) from a tunnel study (08.1-74)<br />

Vollmer M K, Jürgens N, Steinbacher M, Reimann S, Weilenmann M, Buchmann B<br />

<strong>The</strong> effect of mountainous topography on moisture exchange between the “surface” and the free<br />

atmosphere (08.1-75)<br />

Weigel A P, Chow F K, Rotach M W<br />

Source apportionment of PM2.5 and selected hazardous air pollutants in Seattle (08.1-76)<br />

Wu C F, Larson T V, Wu S Y, Williamson J, Westberg H H, Liu L J S<br />

Gas temperature measurement in thermal radiating environments using a suction thermocouple<br />

apparatus (08.1-77)<br />

Z’graggen A, Friess H, Steinfeld A<br />

Air quality modelling over Bogota, Colombia: Combined techniques to estimate and evaluate emission<br />

inventories (08.1-78)<br />

Zarate E, Belalcazar L C, Clappier A, Manzi V, van den Bergh H<br />

Ubiquity and dominance of oxygenated species in organic aerosols in anthropogenically-influenced<br />

Northern Hemisphere midlatitudes (08.1-79)<br />

Zhang Q, Jimenez J L, Canagaratna M R, Allan J D, Coe H, Ulbrich I, Alfarra M R, Takami A, Middlebrook A 67<br />

M, Sun Y L, Dzepina K, Dunlea E, Docherty K, Decarlo P F, Salcedo D, Onasch T, Jayne J T, Miyoshi T, Shimono<br />

A, Hatakeyama S, Takegawa N, Kondo Y, Schneider J, Drewnick F, Borrmann S, Weimer S, Demerjian K L, Williams<br />

P, Bower K, Bahreini R, Cottrell L, Griffin R J, Rautiainen J, Sun J Y, Zhang Y M, Worsnop D R


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong> 11<br />

1.2 Terrestrial Ecosystems<br />

<strong>The</strong> <strong>Swiss</strong> agri-environment scheme enhances pollinator diversity and plant reproductive<br />

success in nearby intensively managed farmland (08.1-80)<br />

Albrecht M, Duelli P, Müller C, Kleijn D, Schmid B<br />

Interaction diversity within quantified insect food webs in restored and adjacent intensively managed<br />

meadows (08.1-81)<br />

Albrecht M, Duelli P, Schmid B, Müller C B<br />

Sustaining agricultural production and food security in Southern Africa: an improved role for climate<br />

prediction? (08.1-82)<br />

Archer E, Mukhala E, Walker S, Dilley M, Masamvu K<br />

Importance of ecological compensation areas for small mammals in intensively farmed areas<br />

(08.1-83)<br />

Aschwanden J, Holzgang O, Jenni L<br />

Effects of agri-environmental measures, site and landscape conditions on butterfly diversity of <strong>Swiss</strong><br />

grassland (08.1-84)<br />

Aviron S, Jeanneret P, Schüpbach B, Herzog F<br />

Conservation of butterfly populations in dynamic landscapes: <strong>The</strong> role of farming practices and<br />

landscape mosaic (08.1-85)<br />

Aviron S, Kindlmann P, Burel F<br />

Nitrogen deposition but not ozone affects productivity and community composition of subalpine<br />

grassland after 3 yr of treatment (08.1-86)<br />

Bassin S, Volk M, Suter M, Buchmann N, Fuhrer J<br />

Volcanic explosive eruptions of the Vesuvio decrease tree-ring growth but not photosynthetic rates<br />

in the surrounding forests (08.1-87)<br />

Battipaglia G, Cherubini P, Saurer M, Siegwolf R T W, Strumia S, Cotrufo M F<br />

Intensified grazing affects endemic plant and gastropod diversity in alpine grasslands of the<br />

Southern Carpathian mountains (Romania) (08.1-88)<br />

Baur B, Cremene C, Groza C, Schileyko A A, Baur A, Erhardt A<br />

Effect of rock climbing on the calcicolous lichen community of limestone cliffs in the northern<br />

<strong>Swiss</strong> Jura Mountains (08.1-89)<br />

Baur B, Froeberg L, Müller S W<br />

Evaluating macrolichens and environmental variables as predictors of the diversity of epiphytic<br />

microlichens (08.1-90)<br />

Bergamini A, Stofer S, Bolliger J, Scheidegger C<br />

Which species will succesfully track climate change? <strong>The</strong> influence of intraspecific competition and<br />

density dependent dispersal on range shifting dynamics (08.1-91)<br />

Best A S, Johst K, Münkemüller T, Travis J M J<br />

Drought induces lagged tree mortality in a subalpine forest in the Rocky Mountains (08.1-92)<br />

Bigler C, Gavin D G, Gunning C, Veblen T T<br />

Conservation of high-altitude wetlands: 368 experiences of the WWF network (08.1-93)<br />

Biksham G<br />

67


12<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Restoration of montane fen meadows by mowing remains possible after 4-35 years of abandonment<br />

(08.1-94)<br />

Billeter R, Peintinger M, Diemer M<br />

Dynamics in debris-flow activity on a forested cone - A case study using different dendroecological<br />

approaches (08.1-95)<br />

Bollschweiler M, Stoffel M, Schneuwly D M<br />

Methanol exchange between grassland and the atmosphere (08.1-96)<br />

Brunner A, Ammann C, Neftel A, Spirig C<br />

A standardized procedure for surveillance and monitoring European habitats and provision of spatial<br />

data (08.1-97)<br />

Bunce R G H, Metzger M J, Jongman R H G, Brandt J, de Blust G, Elena Rossello R, Groom G B, Halada L, Hofer G,<br />

Howard D C, Kovar P, Mucher C A, Padoa Schioppa E, Paelinx D, Palo A, Perez Soba M, Ramos I L, Roche P, Skanes<br />

H, Wrbka T<br />

Three objectives of historical ecology: the case of litter collecting in Central European forests<br />

(08.1-98)<br />

Bürgi M, Gimmi U<br />

Response to ozone of beech (Fagus sylvatica L.) seedlings under competition, in an open-top chamber<br />

experiment. A chlorophyll fluorescence analysis (08.1-99)<br />

Bussotti F, Cascio C, Strasser R<br />

Comparative typology in six european low-intensity systems of grassland management (08.1-100)<br />

Caballero R, Riseth J A, Labba N, Tyran E, Musial W, Motik E, Boltshauser A, Hofstetter P, Gueydon A, Roeder N,<br />

Hoffmann H, Moreira M B, Coelho Inockdo S, Brito O, Gil A<br />

Identification of priority areas for plant conservation in Madagascar using Red List criteria: rare and<br />

threatened Pandanaceae indicate sites in need of protection (08.1-101)<br />

Callmander M W, Schatz G E, Lowry P P Ii, Laivao M O, Raharimampionona J, Andriambololonera S, Raminosoa<br />

T, Consiglio T K<br />

Heavy metal contamination in the semiarid area of Cartagena-La Union (SE Spain) and its implications<br />

for revegetation (08.1-102)<br />

Conesa H M, Faz A, Garcia G, Arnaldos R<br />

Dynamics of metal tolerant plant communities’ development in mine tailings from the Cartagena-<br />

La Union Mining District (SE Spain) and their interest for further revegetation purposes (08.1-103)<br />

Conesa H M, Garcia G, Faz A, Arnaldos R<br />

Water-use strategies in two co-occurring Mediterranean evergreen oaks: surviving the summer<br />

drought (08.1-104)<br />

David T S, Henriques M O, Kurz Besson C, Nunes J, Valente F, Vaz M, Pereira J S, Siegwolf R, Chaves M M, Gazarini<br />

L C, David J S<br />

Impact of <strong>Swiss</strong> agricultural policies on nitrate leaching from arable land (08.1-105)<br />

Decrem M, Spiess E, Richner W, Herzog F<br />

Competition between Lythrum salicaria and a rare species: combining evidence from experiments<br />

and long-term monitoring (08.1-106)<br />

Denoth M, Myers J H


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong> 13<br />

Effects of landscape structure and land-use intensity on similarity of plant and animal communities<br />

(08.1-107)<br />

Dormann C F, Schweiger O, Augenstein I, Bailey D, Billeter R, de Blust G, Defilippi R, Frenzel M, Hendrickx F,<br />

Herzog F, Klotz S, Liira J, Maelfait J P, Schmidt T, Speelmans M, van Wingerden W K R E, Zobel M<br />

Weak and variable relationships between environmental severity and small-scale co-occurrence in<br />

alpine plant communities (08.1-108)<br />

Dullinger S, Kleinbauer I, Pauli H, Gottfried M, Brooker R, Nagy L, <strong>The</strong>urillat J P, Holten J I, Abdaladze O, Benito J<br />

L, Borel J L, Coldea G, Ghosn D, Kanka R, Merzouki A, Klettner C, Moiseev P, Molau U, Reiter K, Rossi G, Stanisci A,<br />

Tomaselli M, Unterlugauer P, Vittoz P, Grabherr G<br />

Minor changes in soil organic carbon and charcoal concentrations detected in a temperate deciduous<br />

forest a year after an experimental slash-and-burn (08.1-109)<br />

Eckmeier E, Gerlach R, Skjemstad J O, Ehrmann O, Schmidt M W I<br />

Conversion of biomass to charcoal and the carbon mass balance from a slash-and-burn experiment<br />

in a temperate deciduous forest (08.1-110)<br />

Eckmeier E, Rosch M, Ehrmann O, Schmidt M W I, Schier W, Gerlach R<br />

Simulating future changes in Arctic and subarctic vegetation (08.1-111)<br />

Epstein H E, Yu Qin, Kaplan J O, Lischke H<br />

Response of soil microbial biomass and community structures to conventional and organic farming<br />

systems under identical crop rotations (08.1-112)<br />

Esperschuetz J, Gattinger A, Mäder P, Schloter M, Fliessbach A<br />

Methodical study of nitrous oxide eddy covariance measurements using quantum cascade laser<br />

spectrometery over a <strong>Swiss</strong> forest (08.1-113)<br />

Eugster W, Zeyer K, Zeeman M, Michna P, Zingg A, Buchmann N, Emmenegger L<br />

Improving predictive mapping in <strong>Swiss</strong> mire ecosystems through re- calibration of indicator values<br />

(08.1-114)<br />

Feldmeyer C E, Ecker K, Kuechler M, Graf U, Waser L<br />

Effects of an extended drought period on grasslands at various altitudes in Switzerland (08.1-115)<br />

Feller U, Signarbieux C<br />

Secondary succession and loss in plant diversity following a grazing decrease in a wooded pasture<br />

of the central <strong>Swiss</strong> Alps (08.1-116)<br />

Frelechoux F, Meisser M, Gillet F<br />

<strong>Change</strong>s of photosynthetic traits in beech saplings (Fagus sylvatica) under severe drought stress and<br />

during recovery (08.1-117)<br />

Galle A, Feller U<br />

Stochastic gene expression in switching environments (08.1-118)<br />

Gander M J, Mazza C, Rummler H<br />

Natural forest regrowth as a proxy variable for agricultural land abandonment in the <strong>Swiss</strong> mountains:<br />

a spatial statistical model based on geophysical and socio-economic variables (08.1-119)<br />

Gellrich M, Baur P, Zimmermann N E<br />

Challenges to the uptake of the ecosystem service rationale for conservation (08.1-120)<br />

Ghazoul J<br />

What you see is where you go? Modeling dispersal in mountainous landscapes (08.1-121)<br />

Graf R F, Kramer Schadt S, Fernandez N, Grimm V


14<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

A predictive model of the density of airborne insects in agricultural environments (08.1-122)<br />

Grübler M U, Morand M, Naef Dänzer B<br />

Measured microwave radiative transfer properties of a deciduous forest canopy (08.1-123)<br />

Guglielmetti M, Schwank M, Mätzler C, Oberdoerster C, Vanderborght J, Flühler H<br />

What matters for predicting the occurrences of trees: Techniques, data, or species’ characteristics?<br />

(08.1-124)<br />

Guisan A, Zimmermann N E, Elith J, Graham C H, Phillips S, Peterson A T<br />

Temporal changes in grazing intensity and herbage quality within a <strong>Swiss</strong> fen meadow (08.1-125)<br />

Güsewell S, Pohl M, Gander A, Strehler C<br />

Biodiversity and ecosystem functioning: reconciling the results of experimental and observational<br />

studies (08.1-126)<br />

Hector A, Joshi J, Scherer Lorenzen M, Schmid B, Spehn E M, Wacker L, Weilenmann M, Bazeley White E,<br />

Beierkuhnlein C, Caldeira M C, Dimitrakopoulos P G, Finn J A, Huss Danell K, Jumpponen A, Leadley P W, Loreau<br />

M, Mulder C P H, Nesshoever C, Palmborg C, Read D J, Siamantziouras A S D, Terry A C, Troumbis A Y<br />

<strong>The</strong> generality of habitat suitability models: A practical test with two insect groups (08.1-127)<br />

Hein S, Binzenhöfer B, Poethke H J, Biedermann R, Settele J, Schroeder B<br />

Fragmented environment affects birch leaf endophytes (08.1-128)<br />

Helander M, Ahlholm J, Sieber T N, Hinneri S, Saikkonen K<br />

Host-parasitoid spatial dynamics in heterogeneous landscapes (08.1-129)<br />

Hirzel A H, Nisbet R M, Murdoch W W<br />

Mating patterns and contemporary gene flow by pollen in a large continuous and a small isolated<br />

population of the scattered forest tree Sorbus torminalis (08.1-130)<br />

Hoebee S E, Arnold U, Düggelin C, Gugerli F, Brodbeck S, Rotach P, Holderegger R<br />

Time series of landscape fragmentation caused by transportation infrastructure and urban development:<br />

a case study from Baden- Wurttemberg, Germany (08.1-131)<br />

Jäger J, Schwarz von Raumer H G , Esswein H, Müller M, Schmidt Lüttman M<br />

Rapid mixing between old and new C pools in the canopy of mature forest trees (08.1-132)<br />

Keel S G, Siegwolf R T W, Jäggi M, Körner C<br />

Identifying the early genetic consequences of habitat degradation in a highly threatened tropical<br />

conifer, Araucaria nemorosa Laubenfels (08.1-133)<br />

Kettle C J, Hollingsworth P M, Jaffre T, Moran B, Ennos R A<br />

Arbuscular mycorrhizal symbiosis can counterbalance the negative influence of the exotic tree species<br />

Eucalyptus camaldulensis on the structure and functioning of soil microbial communities in a<br />

sahelian soil (08.1-134)<br />

Kisa M, Sanon A, Thioulouse J, Assigbetse K, Sylla S, Spichiger R, Dieng L, Berthelin J, Prin Y, Galiana A, Lepage M,<br />

Duponnois R<br />

Response of net ecosystem productivity of three boreal forest stands to drought (vol 9, pg 1128, 2006)<br />

(08.1-135)<br />

Kljun N, Black T A, Griffis T J, Barr A G, Gaumont Guay D, Morgenstern K, Mccaughey J H, Nesic Z<br />

Assessment of land use impacts on the natural environment - Part 2: Generic characterization factors<br />

for local species diversity in central Europe (08.1-136)<br />

Köllner T, Scholz R W


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong> 15<br />

<strong>The</strong> use of ‘altitude’ in ecological research (08.1-137)<br />

Körner C<br />

Creative use of mountain biodiversity databases: <strong>The</strong> Kazbegi research agenda of GMBA-DIVERSITAS<br />

(08.1-138)<br />

Körner C, Donoghue M, Fabbro T, Hauser C, Nogues Bravo D, Kalin Arroyo M T, Soberon J, Speers L, Spehn E M,<br />

Sun H, Tribsch A, Tykarski P, Zbinden N<br />

Mobility of black carbon in drained peatland soils (08.1-139)<br />

Leifeld J, Fenner S, Müller M<br />

Tree species diversity affects canopy leaf temperatures in a mature temperate forest (08.1-140)<br />

Leuzinger S, Körner C<br />

Water savings in mature deciduous forest trees under elevated CO 2 (08.1-141)<br />

Leuzinger S, Körner C<br />

Anchorage of mature conifers: Resistive turning moment, root-soil plate geometry and root growth<br />

orientation (08.1-142)<br />

Lundstroem T, Jonas T, Stöckli V, Ammann W<br />

Wheat quality in organic and conventional farming: results of a 21 year field experiment (08.1-143)<br />

Mäder P, Hahn D, Dubois D, Gunst L, Alföldi T, Bergmann H, Oehme M, Amado R, Schneider H, Graf U, Velimirov<br />

A, Fliebbach A, Niggli U<br />

No difference in competitive ability between invasive North American and native European<br />

Lepidium draba populations (08.1-144)<br />

Mckenney J L, Cripps M G, Price W J, Hinz H L, Schwarzlaender M<br />

Effects of heavy metal soil pollution and acid rain on growth and water use efficiency of a young<br />

model forest ecosystem (08.1-145)<br />

Menon M, Hermle S, Günthardt Goerg M S, Schulin R<br />

Distribution of polychlorinated biphenyls and polybrominated diphenyl ethers in birds of prey from<br />

Switzerland (08.1-146)<br />

Naert C, van Peteghem C, Kupper J, Jenni L, Nägeli H<br />

Effects of experimental lead pollution on the microbial communities associated with Sphagnum<br />

fallax (Bryophyta) (08.1-147)<br />

Nguyen Viet H, Gilbert D, Mitchell E A D, Badot P M, Bernard N<br />

High specificity but contrasting biodiversity of Sphagnum-associated bacterial and plant communities<br />

in bog ecosystems independent of the geographical region (08.1-148)<br />

Opelt K, Berg C, Schönmann S, Eberl L, Berg G<br />

Degradation of an arid coastal landscape in relation to land use changes in Southern Tenerife<br />

(Canary Islands) (08.1-149)<br />

Otto R, Krüsi B O, Kienast F<br />

Probing the responses of barley cultivars (Hordeum vulgare L.) by chlorophyll a fluorescence OLKJIP<br />

under drought stress and re- watering (08.1-150)<br />

Oukarroum A, El Madidi S, Schansker G, Strasser R J<br />

Integrating environmental and economic performance to assess modern silvoarable agroforestry in<br />

Europe (08.1-151)<br />

Palma J, Graves A R, Burgess P J, van der Werf W, Herzog F


16<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

<strong>The</strong> odd man out? Might climate explain the lower tree alpha-diversity of African rain forests relative<br />

to Amazonian rain forests? (08.1-152)<br />

Parmentier I, Malhi Y, Senterre B, Whittaker R J, Alonso A, Balinga M P B, Bakayoko A, Bongers F, Chatelain C,<br />

Comiskey J A, Cortay R, Kamdem M N D, Doucet J L, Gautier L, Hawthorne W D, Issembe Y A, Kouame F N, Kouka<br />

L A, Leal M E, Lejoly J, Lewis S L, Nusbaumer L, Parren M P E, Peh K S H, Phillips O L, Sheil D, Sonke B, Sosef M S<br />

M, Sunderland T C H, Stropp J, Ter Steege H, Swaine M D, Tchouto M G P, van Gemerden Barend S, van Valkenburg<br />

J L C H, Wöll H<br />

Are the living collections of the world’s botanical gardens following species-richness patterns<br />

observed in natural ecosystems? (08.1-153)<br />

Pautasso M, Parmentier I<br />

Common species determine richness patterns in biodiversity indicator taxa (08.1-154)<br />

Pearman P B, Weber D<br />

Earthworm populations in two low-input cereal farming systems (08.1-155)<br />

Pfiffner L, Luka H<br />

Combining probabilistic land-use change and tree population dynamics modelling to simulate<br />

responses in mountain forests (08.1-156)<br />

Rickebusch S, Gellrich M, Lischke H, Guisan A, Zimmermann N E<br />

Understanding the low-temperature limitations to forest growth through calibration of a forest<br />

dynamics model with tree-ring data (08.1-157)<br />

Rickebusch S, Lischke H, Bugmann H, Guisan A, Zimmermann N E<br />

Effects of grazing and soil micro-climate on decomposition rates in a spatio-temporally heterogeneous<br />

grassland (08.1-158)<br />

Risch A C, Jurgensen M F, Frank D A<br />

Natural avalanche disturbance shapes plant diversity and species composition in subalpine forest<br />

belt (08.1-159)<br />

Rixen C, Haag S, Kulakowski D, Bebi P<br />

<strong>The</strong> Rauischholzhausen agenda for road ecology (08.1-160)<br />

Roedenbeck I A, Fahrig L, Findlay C S, Houlahan J E, Jäger J, Klar N, Kramer Schadt S, van der Grift E A<br />

Detecting the role of individual species for overyielding in experimental grassland communities<br />

composed of potentially dominant species (08.1-161)<br />

Roscher C, Schumacher J, Weisser W W, Schmid B, Schulze E D<br />

A Bayesian state-space formulation of dynamic occupancy models (08.1-162)<br />

Royle J A, Kery M<br />

Microsatellite diversity of the agriculturally important alpine grass Poa alpina in relation to land<br />

use and natural environment (08.1-163)<br />

Rudmann Maurer K, Weyand A, Fischer M, Stöcklin J<br />

Recent decline in precipitation and tree growth in the eastern Mediterranean (08.1-164)<br />

Sarris D, Christodoulakis D, Körner C<br />

Modeling the forest transition: Forest scarcity and ecosystem service hypotheses (08.1-165)<br />

Satake A, Rudel T K


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong> 17<br />

Ecological niche modelling of two cryptic bat species calls for a reassessment of their conservation<br />

status (08.1-166)<br />

Sattler T, Bontadina F, Hirzel A H, Arlettaz R<br />

Use of integrated modeling to enhance estimates of population dynamics obtained from limited<br />

data (08.1-167)<br />

Schaub M, Gimenez O, Sierro A, Arlettaz R<br />

Tree species richness affects litter production and decomposition rates in a tropical biodiversity<br />

experiment (08.1-168)<br />

Scherer Lorenzen M, Bonilla J L, Potvin C<br />

Exploring the functional significance of forest diversity: A new long-term experiment with temperate<br />

tree species (BIOTREE) (08.1-169)<br />

Scherer Lorenzen M, Schulze E D, Don A, Schumacher J, Weller E<br />

Patterns of variation of a common fern (Athyrium filix-femina; Woodsiaceae): Population structure<br />

along and between altitudinal gradients (08.1-170)<br />

Schneller J, Liebst B<br />

Examining native and exotic species diversity in European riparian forests (08.1-171)<br />

Schnitzler A, Hale B W, Alsum E M<br />

Speciation reversal and biodiversity dynamics with hybridization in changing environments<br />

(08.1-172)<br />

Seehausen O, Takimoto G, Roy D, Jokela J<br />

Altitudinal and horizontal shifts of the upper boundaries of open and closed forests in the Polar<br />

Urals in the 20th century (08.1-173)<br />

Shiyatov S G, Terentev M M, Fomin V V, Zimmermann N E<br />

Temperate grasslands and global atmospheric change: a review (08.1-174)<br />

Soussana J F, Lüscher A<br />

Conservation of grasshopper diversity in a changing environment (08.1-175)<br />

Steck C E, Bürgi M, Bolliger J, Kienast F, Lehmann A, Gonseth Y<br />

Hotspots and richness pattern of grasshopper species in cultural landscapes (08.1-176)<br />

Steck C E, Bürgi M, Coch T, Duelli P<br />

Floral free fall in the <strong>Swiss</strong> lowlands: environmental determinants of local plant extinction in a<br />

peri-urban landscape (08.1-177)<br />

Stehlik I, Caspersen J P, Wirth L, Holderegger R<br />

Cooccurring Gentiana verna and Gentiana acaulis and their neighboring plants in two swiss upper<br />

montane meadows harbor distinct arbuscular mycorrhizal fungal communities (08.1-178)<br />

Sykorova Z, Wiemken A, Redecker D<br />

An improved canopy integration scheme for a land surface model with prognostic canopy structure<br />

(08.1-179)<br />

Thornton P E, Zimmermann N E<br />

Fitness-related parameters improve presence-only distribution modelling for conservation practice:<br />

<strong>The</strong> case of the red-backed shrike (08.1-180)<br />

Titeux N, Dufrene M, Radoux J, Hirzel A H, Defourny P


18<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Response of Pinus leucodermis to climate and anthropogenic activity in the National Park of Pollino<br />

(Basilicata, Southern Italy) (08.1-181)<br />

Todaro L, Andreu L, D’alessandro C M, Gutirrez E, Cherubinic P, Saracino A<br />

Regional assessment of climate change impacts on maize productivity and associated production<br />

risk in Switzerland (08.1-182)<br />

Torriani D S, Calanca P, Lips M, Ammann H, Beniston M, Fuhrer J<br />

Potential effects of changes in mean climate and climate variability on the yield of winter and<br />

spring crops in Switzerland (08.1-183)<br />

Torriani D S, Calanca P, Schmid S, Beniston M, Fuhrer J<br />

Effect of supplementation of fresh and ensiled clovers to ryegrass on nitrogen loss and methane<br />

emission of dairy cows (08.1-184)<br />

van Dorland H A, Wettstein H R, Leuenberger H, Kreuzer M<br />

Invasion biology and conservation biology: time to join forces to explore the links between species<br />

traits and extinction risk and invasiveness (08.1-185)<br />

van Kleunen M, Richardson D M<br />

How patch configuration affects the impact of disturbances on metapopulation persistence<br />

(08.1-186)<br />

Vuilleumier S, Wilcox C, Cairns B J, Possingham H P<br />

Prediction of lichen diversity in an UNESCO biosphere reserve - correlation of high resolution<br />

remote sensing data with field samples (08.1-187)<br />

Waser L T, Küchler M, Schwarz M, Ivits E, Stofer S, Scheidegger C<br />

Radial growth responses to drought of Pinus sylvestris and Quercus pubescens in an inner-Alpine<br />

dry valley (08.1-188)<br />

Weber P, Bugmann H, Rigling A<br />

Landscape-level gene flow in Lobaria pulmonaria, an epiphytic lichen (08.1-189)<br />

Werth S, Gugerli F, Holderegger R, Wagner H H, Csencsics D, Scheidegger C<br />

Rhizodeposition of C and N in peas and oats after C-13-N-15 double labelling under field conditions<br />

(08.1-190)<br />

Wichern F, Mayer J, Jörgensen R G, Müller T<br />

Genetic rescue persists beyond first-generation outbreeding in small populations of a rare plant<br />

(08.1-191)<br />

Willi Y, van Kleunen M, Dietrich S, Fischer M<br />

Vegetation effects on pedogenetic forms of Fe, Al and Si and on clay minerals in soils in southern<br />

Switzerland and northern Italy (08.1-192)<br />

Zanelli R, Egli M, Mirabella A, Giaccai D, Abdelmoula M<br />

Importance of dispersal for the expansion of a Eurasian lynx Lynx lynx population in a fragmented<br />

landscape (08.1-193)<br />

Zimmermann F, Breitenmoser Wursten C, Breitenmoser U<br />

Remote sensing-based predictors improve distribution models of rare, early successional and broadleaf<br />

tree species in Utah (08.1-194)<br />

Zimmermann N E, Edwards T C, Moisen G G, Frescino T S, Blackard J A


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Stomatal regulation by microclimate and tree water relations: interpreting ecophysiological field<br />

data with a hydraulic plant model (08.1-195)<br />

Zweifel R, Steppe K, Sterck F J<br />

1.3 Soil and Litosphere<br />

Quantification of soil erosion rates related to ancient Maya deforestation (08.1-196)<br />

Anselmetti F S, Hodell D A, Ariztegui D, Brenner M, Rosenmeier M F<br />

Soil biogeochemical processes within the Critical Zone (08.1-197)<br />

Chorover J, Kretzschmar R, Garcia Pichel F, Sparks D L<br />

Scale-dependent relationships between soil organic carbon and urease activity (08.1-198)<br />

Corstanje R, Schulin R, Lark R M<br />

Effect of climate and vegetation on soil organic carbon, humus fractions, allophanes, imogolite,<br />

kaolinite, and oxyhydroxides in volcanic soils of Etna (Sicily) (08.1-199)<br />

Egli M, Alioth L, Mirabella A, Raimondi S, Nater M, Verel R<br />

Soil moisture - Atmosphere interactions during the 2003 European summer heat wave (08.1-200)<br />

Fischer E M, Seneviratne S I, Vidale P L, Lüthi D, Schär C<br />

Numerical modelling of the hydrogeological and geomechanical behaviour of a large slope movement:<br />

the Triesenberg landslide (Liechtenstein) (08.1-201)<br />

Francois B, Tacher L, Bonnard Ch, Laloui L, Triguero V<br />

Formation of hydrozincite, Zn layered double hydroxide and Zn phyllosilicates in contaminated<br />

calcareous soils (08.1-202)<br />

Jacquat O, Vögelin A, Kretzschmar R<br />

<strong>The</strong> impact of Fe isotope fractionation by plants on the isotopic signature of soils (08.1-203)<br />

Kiczka M, Wiederhold J G, Krämer S M, Bourdon B, Kretzschmar R<br />

Sulphur behaviour in forest soils near the largest SO 2 emitter in northern Europe (08.1-204)<br />

Koptsik G, Alewell C<br />

Evidence for in situ degradation of mono-and polyaromatic hydrocarbons in alluvial sediments<br />

based on microcosm experiments with C-13-labeled contaminants (08.1-205)<br />

Morasch B, Höhener P, Hunkeler D<br />

Acidification and recovery of soil at a heavily impacted forest catchment (Lysina, Czech Republic) -<br />

SAFE modeling and field results (08.1-206)<br />

Navratil T, Kurz D, Kram P, Hofmeister J, Hruska J<br />

Elucidating differences in the sorption properties of 10 humic and fulvic acids for polar and nonpolar<br />

organic chemicals (08.1-207)<br />

Niederer C, Schwarzenbach R P, Goss K U<br />

Bioavailability of pollutants and soil remediation (08.1-208)<br />

Ortega Calvo J J, Ball W P, Schulin R, Semple K T, Wick L Y<br />

New method for in situ characterization of loose material for landslide mapping purpose<br />

(08.1-209)<br />

Pantet A, Parriaux A, <strong>The</strong>lin P<br />

19<br />

113


20 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Poplar for the phytomanagement of boron contaminated sites (08.1-210)<br />

Robinson B H, Green S R, Chancerel B, Mills T M, Clothier B E<br />

<strong>Change</strong>s in the macro-pore structure of restored soil caused by compaction beneath heavy agricultural<br />

machinery: a morphometric study (08.1-211)<br />

Schäffer B, Stauber M, Müller R, Schulin R<br />

Reducing phosphorus losses from over-fertilized grassland soils proves difficult in the short term<br />

(08.1-212)<br />

Schärer M, Stamm C, Vollmer T, Frossard E, Oberson A, Flühler H, Sinaj S<br />

Heavy metal contamination along a soil transect in the vicinity of the iron smelter of Kremikovtzi<br />

(Bulgaria) (08.1-213)<br />

Schulin R, Curchod F, Mondeshka M, Daskalova A, Keller A<br />

Slip rates variability and sediment mobilization on a shallow landslide in the northern <strong>Swiss</strong> Alps<br />

(08.1-214)<br />

Schwab M, Läderach C, Rieke Zapp D, Schlunegger F<br />

Dry-end surface soil moisture variability during NAFE’06 (08.1-215)<br />

Teuling A J, Uijlenhoet R, Hurkmans R, Merlin O, Panciera R, Walker J P, Troch P A<br />

Dynamics of soil organic matter turnover and soil respired CO 2 in a temperate grassland labelled<br />

with C-13 (08.1-216)<br />

<strong>The</strong>is D E, Jäggi M, Aeschlimann D, Blum H, Frossard E, Siegwolf R T W<br />

Methanotrophic activity in a diffusive methane/oxygen counter- gradient in an unsaturated porous<br />

medium (08.1-217)<br />

Urmann K, Norina E S, Schroth M H, Zeyer J<br />

Release of C and N from roots of peas and oats and their availability to soil microorganisms<br />

(08.1-218)<br />

Wichern F, Mayer J, Joergensen R G, Müller T<br />

Coupled mobilization of dissolved organic matter and metals (Cu and Zn) in soil columns<br />

(08.1-219)<br />

Zhao L Y L, Schulin R, Weng L, Nowack B<br />

1.4 Cryosphere<br />

ADEOS-II/GLI snow/ice products - Part II: Validation results using GLI and MODIS data (08.1-220)<br />

Aoki T, Hori M, Motoyoshi H, Tanikawa T, Hachikubo A, Sugiura K, Yasunari T J, Storvold R, Eide H A, Stamnes K,<br />

Li W, Nieke J, Nakajima Y, Takahashi F<br />

Current status of Andean glaciers (08.1-221)<br />

Casassa G, Rivera A, Haeberli W, Jones G, Käser G, Ribstein P, Rivera A, Schneider C<br />

Diurnal production of gaseous mercury in the alpine snowpack before snowmelt (08.1-222)<br />

Fain X, Grangeon S, Bahlmann E, Fritsche J, Obrist D, Dommergue A, Ferrari C P, Cairns W, Ebinghaus R, Barbante<br />

C, Cescon P, Boutron C<br />

Validation of operational AVHRR subpixel snow retrievals over the European Alps based on ASTER<br />

data (08.1-223)<br />

Foppa N, Hauser A, Oesch D, Wunderle S, Meister R<br />

121


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

An overview of snow photochemistry: evidence, mechanisms and impacts (08.1-224)<br />

Grannas A M, Jones A E, Dibb J, Ammann M, Anastasio C, Beine H J, Bergin M, Bottenheim J, Boxe C S, Carver G,<br />

Chen G, Crawford J H, Domine F, Frey M M, Guzman M I, Heard D E, Helmig D, Hoffmann M R, Honrath R E, Huey<br />

L G, Hutterli M, Jacobi H W, Klan P, Lefer B, Mc Connell J, Plane J, Sander R, Savarino J, Shepson P B, Simpson W<br />

R, Sodeau J R, von Glasow R, Weller R, Wolff E W, Zhu T<br />

Snow avalanche hazard modelling of large areas using shallow water numerical methods and GIS<br />

(08.1-225)<br />

Gruber U, Bartelt P<br />

Retreat scenarios of Unteraargletscher, Switzerland, using a combined ice-flow mass-balance model<br />

(08.1-226)<br />

Huss M, Sugiyama S, Bauder A, Funk M<br />

Hazard assessment of potential periglacial debris flows based on GIS- based spatial modelling and<br />

geophysical field surveys: A case study in the <strong>Swiss</strong> Alps (08.1-227)<br />

Kneisel C, Rothenbühler C, Keller F, Haeberli W<br />

Tracing glacier wastage in the Northern Tien Shan (Kyrgyzstan/Central Asia) over the last 40 years<br />

(08.1-228)<br />

Niederer P, Bilenko V, Ershova N, Hurni H, Yerokhin S, Maselli D<br />

Validation of the SNOWPACK model in five different snow zones in Finland (08.1-229)<br />

Rasmus S, Gronholm T, Lehning M, Rasmus K, Kulmala M<br />

Rockglacier activity studies on a regional scale: comparison of geomorphological mapping and photogrammetric<br />

monitoring (08.1-230)<br />

Roer I, Nyenhuis M<br />

Influence of different digital terrain models (DTMs)on alpine permafrost modeling (08.1-231)<br />

Salzmann N, Gruber S, Hugentobler M, Hölzle M<br />

Modeling the effect of snow and ice on the global environmental fate and long-range transport<br />

potential of semivolatile organic compounds (08.1-232)<br />

Stocker J, Scheringer M, Wegmann F, Hungerbühler K<br />

Climate warming revealed by englacial temperatures at Col du Dome (4250 m, Mont Blanc area)<br />

(08.1-233)<br />

Vincent C, Le Meur E, Six D, Possenti P, Lefebvre E, Funk M<br />

Introduction to special section: Permafrost and seasonally frozen ground under a changing climate<br />

(08.1-234)<br />

Zhang T, Nelson F E, Gruber S<br />

1.5 Oceans and Fresh Water Systems<br />

Impact of monsoonal rains on spatial scaling patterns in water chemistry of a semiarid river<br />

network (08.1-235)<br />

Acuna V, Dahm C N<br />

<strong>The</strong> tracing of riverine U in Arctic seawater with very precise U-234 /U-238 measurements<br />

(08.1-236)<br />

Andersen M B, Stirling C H, Porcelli D, Halliday A N, Andersson P S, Baskaran M<br />

21<br />

126


22 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Effects of Alpine hydropower dams on particle transport and lacustrine sedimentation (08.1-237)<br />

Anselmetti F S, Bühler R, Finger D, Girardclos S, Lancini A, Rellstab C, Sturm M<br />

Flood events overrule fertiliser effects on biomass production and species richness in riverine grasslands<br />

(08.1-238)<br />

Beltman B, Willems J H, Güsewell S<br />

Large-scale climatic signatures in lakes across Europe: a meta- analysis (08.1-239)<br />

Blenckner T, Adrian R, Livingstone D M, Jennings E, Weyhenmeyer G A, George D G, Jankowski T, Jarvinen M,<br />

Aonghusa Caitriona N, Noges T, Straile D, Teubner K<br />

<strong>The</strong> ecology of European ponds: defining the characteristics of a neglected freshwater habitat<br />

(08.1-240)<br />

Cereghino R, Biggs J, Oertli B, Declerck S<br />

Biodiversity and distribution patterns of freshwater invertebrates in farm ponds of a south-western<br />

French agricultural landscape (08.1-241)<br />

Cereghino R, Ruggiero A, Marty P, Angelibert S<br />

<strong>The</strong> Mar Menor lagoon (SE Spain): A singular natural ecosystem threatened by human activities<br />

(08.1-242)<br />

Conesa H M, Jimenez Carceles F J<br />

Earth Observation for wetland inventory, assessment and monitoring (08.1-243)<br />

Davidson N C, Finlayson C M<br />

Biodegradation and environmental behavior of biodiesel mixtures in the sea: An initial study<br />

(08.1-244)<br />

Demello J A, Carmichael C A, Peacock E E, Nelson R K, Arey J S, Reddy C M<br />

Effect of water-table fluctuation on dissolution and biodegradation of a multi-component, light<br />

nonaqueous-phase liquid (08.1-245)<br />

Dobson R, Schroth M H, Zeyer J<br />

Ecosystem expansion and contraction dynamics along a large Alpine alluvial corridor (Tagliamento<br />

River, Northeast Italy) (08.1-246)<br />

Doering M, Uehlinger U, Rotach A, Schlaepfer D R, Tockner K<br />

Field evidence of a dynamic leakage coefficient for modelling river- aquifer interactions (08.1-247)<br />

Doppler T, Franssen H J H, Kaiser H P, Kuhlman U, Stauffer F<br />

<strong>The</strong> GLOWA Jordan river project: Integrated research for sustainable water management (08.1-248)<br />

Drexler C, Tielbörger K<br />

Hydropower production and river rehabilitation: A case study on an alpine river (08.1-249)<br />

Fette M, Weber C, Peter A, Wehrli B<br />

Effects of alpine hydropower operations on primary production in a downstream lake (08.1-250)<br />

Finger D, Bossard P, Schmid M, Jaun L, Müller B, Steiner D, Schäffer E, Zeh M, Wüest A<br />

Comparing effects of oligotrophication and upstream hydropower dams on plankton and productivity<br />

in perialpine lakes (08.1-251)<br />

Finger D, Schmid M, Wüest A


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Characterizing water circulation and contaminant transport in Lake Geneva using bacteriophage<br />

tracer experiments and limnological methods (08.1-252)<br />

Goldscheider N, Haller L, Pote J, Wildi W, Zopfi J<br />

Bubble gas-exchange in an artificially aerated lake traced using noble gases (08.1-253)<br />

Holzner C P, Graser N, Kipfer R<br />

Accumulation of cyanobacterial toxins in freshwater “seafood” and its consequences for public<br />

health: A review (08.1-254)<br />

Ibelings B W, Chorus I<br />

Effects of upstream hydropower operation and oligotrophication on the light regime of a turbid<br />

peri-alpine lake (08.1-255)<br />

Jaun L, Finger D, Zeh M, Schurter M, Wüest A<br />

Decadal water mass variations along 20 degrees W in the Northeastern Atlantic Ocean (08.1-256)<br />

Johnson G C, Gruber N<br />

Relationships among recent Alpine Cladocera remains and their environment: Implications for climate-change<br />

studies (08.1-257)<br />

Kamenik C, Szeroczynska K, Schmidt R<br />

Implementation of a process-based catchment model in a poorly gauged, highly glacierized<br />

Himalayan headwater (08.1-258)<br />

Konz M, Uhlenbrook S, Braun L, Shrestha A, Demuth S<br />

Effects of impoundment on nutrient availability and productivity in lakes (08.1-259)<br />

Matzinger A, Pieters R, Ashley K I, Lawrence G A, Wüest A<br />

Eutrophication: are mayflies (Ephemeroptera) good bioindicators for ponds? (08.1-260)<br />

Menetrey N, Oertli B, Sartori M, Wagner A, Lachavanne J B<br />

Inorganic carbon fixation by sulfate-reducing bacteria in the Black Sea water column (08.1-261)<br />

Neretin L N, Abed R M M, Schippers A, Schubert C J, Kohls K, Kuypers M M M<br />

Impacts of environmental change on water resources in the Mt. Kenya region (08.1-262)<br />

Notter B, Macmillan L, Viviroli D, Weingartner R, Liniger H P<br />

Influence of temperature and high acetate concentrations on methanogenensis in lake sediment<br />

slurries (08.1-263)<br />

Nozhevnikova A N, Nekrasova V, Ammann A, Zehnder A J B, Wehrli B, Holliger C<br />

Macroinvertebrate assemblages in 25 high alpine ponds of the <strong>Swiss</strong> National Park (Cirque of<br />

Macun) and relation to environmental variables (08.1-264)<br />

Oertli B, Indermühle N, Angelibert S, Hinden H, Stoll A<br />

Aquatic macroinvertebrate response along a gradient of lateral connectivity in river floodplain<br />

channels (08.1-265)<br />

Paillex A, Castella E, Carron G<br />

Bipolar gene flow in deep-sea benthic foraminifera (08.1-266)<br />

Pawlowski J, Fahrni J, Lecroq B, Longet D, Cornelius N, Excoffier L, Cedhagen T, Gooday A J<br />

Earlier onset of the spring phytoplankton bloom in lakes of the temperate zone in a warmer climate<br />

(08.1-267)<br />

Peeters F, Straile D, Lorke A, Livingstone D M<br />

23


24 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Water level fluctuations and dynamics of amphibious plants at Lake Constance: Long-term study<br />

and simulation (08.1-268)<br />

Peintinger M, Prati D, Winkler E<br />

Phytoplankton blooms in the Ross Sea, Antarctica: Interannual variability in magnitude, temporal<br />

patterns, and composition (08.1-269)<br />

Peloquin J A, Smith W O Jr<br />

One-year survey of a single Micronesian reef reveals extraordinarily rich diversity of Symbiodinium<br />

types in soritid foraminifera (08.1-270)<br />

Pochon X, Garcia Cuetos L, Baker A C, Castella E, Pawlowski J<br />

Continuous measurement of sediment transport in the Erlenbach stream using piezoelectric bedload<br />

impact sensors (08.1-271)<br />

Rickenmann D, Mcardell B W<br />

Cadmium isotope fractionation in seawater - A signature of biological activity (08.1-272)<br />

Ripperger S, Rehkamper M, Porcelli D, Halliday A N<br />

Density-dependent life history differences in a stream mayfly (Deleatidium) inhabiting permanent<br />

and intermittent stream reaches (08.1-273)<br />

Robinson C T, Buser T<br />

Macroinvertebrate assemblages of a high elevation stream/lake network with an emphasis on the<br />

Chironomidae (08.1-274)<br />

Robinson C T, Hieber M, Wenzelides V, Lods Crozet B<br />

Hydrological heterogeneity of an alpine stream-lake network in Switzerland (08.1-275)<br />

Robinson C T, Matthaei S<br />

Sources and sinks of methane in Lake Baikal: A synthesis of measurements and modeling<br />

(08.1-276)<br />

Schmid M, de Batist M, Granin N G, Kapitanov V A, Mcginnis D F, Mizandrontsev I B, Obzhirov A I, Wüest A<br />

Towards a hydrological classification of European soils: preliminary test of its predictive power for<br />

the base flow index using river discharge data (08.1-277)<br />

Schneider M K, Brunner F, Hollis J M, Stamm C<br />

Selecting scenarios to assess exposure of surface waters to veterinary medicines in Europe<br />

(08.1-278)<br />

Schneider M K, Stamm C, Fenner K<br />

Assessing iron-mediated oxidation of toluene and reduction of nitroaromatic contaminants in<br />

anoxic environments using compound- specific isotope analysis (08.1-279)<br />

Tobler N B, Hofstetter T B, Schwarzenbach R P<br />

Iron-mediated microbial oxidation and abiotic reduction of organic contaminants under anoxic<br />

conditions (08.1-280)<br />

Tobler N B, Hofstetter T B, Straub K L, Fontana D, Schwarzenbach R P<br />

Probabilistic flood forecasting with a limited-area ensemble prediction system: Selected case studies<br />

(08.1-281)<br />

Verbunt M, Walser A, Gurtz J, Montani A, Schär C<br />

Where a springhead becomes a springbrook - a regional zonation of springs (08.1-282)<br />

von Fumetti S, Nagel P, Baltes B


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Nitrate-depleted conditions on the increase in shallow northern European lakes (08.1-283)<br />

Weyhenmeyer G A, Jeppesen E, Adrian R, Arvola L, Blenckner T, Jankowski T, Jennings E, Noges P, Noges T,<br />

Straile D<br />

Differential decline and recovery of haplochromine trophic groups in the Mwanza Gulf of Lake<br />

Victoria (08.1-284)<br />

Witte F, Wanink J H, Kishe Machumu M, Mkumbo O C, Goudswaard P C, Seehausen O<br />

Oxygen isotope biogeochemistry of pore water sulfate in the deep biosphere: Dominance of isotope<br />

exchange reactions with ambient water during microbial sulfate reduction (ODP Site 1130)<br />

(08.1-285)<br />

Wortmann U G, Chernyavsky B, Bernasconi S M, Brunner B, Böttcher M E, Swart P K<br />

Virtual water: An unfolding concept in integrated water resources management (08.1-286)<br />

Yang H, Zehnder A<br />

Hydrological modelling of the chaohe basin in china: Statistical model formulation and Bayesian<br />

inference (08.1-287)<br />

Yang J, Reichert P, Abbaspour K C, Yang H<br />

Bayesian uncertainty analysis in distributed hydrologic modeling: A case study in the Thur River<br />

basin (Switzerland) (08.1-288)<br />

Yang J, Reichert P, Abbaspour K C<br />

Salinization of groundwater in the Nefzawa oases region, Tunisia: results of a regional-scale hydrogeologic<br />

approach (08.1-289)<br />

Zammouri M, Siegfried T, El Fahem T, Kriaa S, Kinzelbach W<br />

Extreme heat and runoff extremes in the <strong>Swiss</strong> Alps (08.1-290)<br />

Zappa M, Kan C<br />

Insights into the management of sea turtle internesting area through satellite telemetry (08.1-291)<br />

Zbinden J A, Aebischer A, Margaritoulis D, Arlettaz R<br />

1.6 Energy Balance<br />

Impact of ice supersaturated regions and thin cirrus on radiation in the midlatitudes<br />

(08.1-292)<br />

Fusina F, Spichtinger P, Lohmann U<br />

Year-round observation of longwave radiative flux divergence in Greenland (08.1-293)<br />

Hoch S W, Calanca P, Philipona R, Ohmura A<br />

Long-term changes in the cosmic ray intensity at Earth, 1428-2005 (08.1-294)<br />

Mccracken K G, Beer J<br />

Modelling the ground heat flux of an urban area using remote sensing data (08.1-295)<br />

Rigo G, Parlow E<br />

25<br />

149


26 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

1.7 Coupled Systems and Cycles<br />

An Earth-system perspective of the global nitrogen cycle (08.1-296)<br />

Gruber N, Galloway J N<br />

Comparison of quantification methods to measure fire-derived (black /elemental) carbon in soils<br />

and sediments using reference materials from soil, water, sediment and the atmosphere (08.1-297)<br />

Hammes K, Schmidt M W I, Smernik R J, Currie L A, Ball W P, Nguyen T H, Louchouarn P, Houel S, Gustafsson O,<br />

Elmquist M, Cornelissen G, Skjemstad J O, Masiello C A, Song J, Peng P, Mitra S, Dunn J C, Hatcher P G, Hockaday<br />

W C, Smith Dwight M, Hartkopf Fröder C, Böhmer A, Lueer B, Huebert B J, Amelung W, Brodowski S, Huang L,<br />

Zhang W, Gschwend P M, Flores C D X, Largeau C, Rouzaud J N, Rumpel C, Guggenberger G, Kaiser K, Rodionov A,<br />

Gonzalez Vila F J, Gonzalez Perez J A, de La Rosa J M, Manning D A C, Lopez Capel E, Ding L<br />

Analysis of seasonal terrestrial water storage variations in regional climate simulations over Europe<br />

(08.1-298)<br />

Hirschi M, Seneviratne S I, Hagemann S, Schär C<br />

Evaluation of AMIP II global climate model simulations of the land surface water budget and its<br />

components over the GEWEX-CEOP regions (08.1-299)<br />

Irannejad P, Henderson Sellers A<br />

Comprehensive comparison of gap-filling techniques for eddy covariance net carbon fluxes<br />

(08.1-300)<br />

Moffat A M, Papale D, Reichstein M, Hollinger D Y, Richardson A D, Barr A G, Beckstein C, Braswell B H, Churkina<br />

G, Desai A R, Falge E, Gove J H, Heimann M, Hui D, Jarvis A J, Kattge J, Noormets Asko, Stauch V J<br />

Impact of circulation on export production, dissolved organic matter, and dissolved oxygen in the<br />

ocean: Results from Phase II of the Ocean Carbon-cycle Model Intercomparison Project (OCMIP-2)<br />

(08.1-301)<br />

Najjar R G, Jin X, Louanchi F, Aumont O, Caldeira K, Doney S C, Dutay J C, Follows M, Gruber N, Joos F, Lindsay K,<br />

Maier Reimer E, Matear R J, Matsumoto K, Monfray P, Mouchet A, Orr J C, Plattner G K, Sarmiento J L, Schlitzer R,<br />

Slater R D, Weirig M F, Yamanaka Y, Yool A<br />

Experimental assessment of N 2O background fluxes in grassland systems (08.1-302)<br />

Neftel A, Flechard C, Ammann C, Conen F, Emmenegger L, Zeyer K<br />

Effects of increased soil water availability on grassland ecosystem carbon dioxide fluxes (08.1-303)<br />

Risch A C, Frank D A<br />

Chemistry, transport and dry deposition of trace gases in the boundary layer over the tropical<br />

Atlantic Ocean and the Guyanas during the GABRIEL field campaign (08.1-304)<br />

Stickler A, Fischer H, Bozem H, Gurk C, Schiller C, Martinez Harder M, Kubistin D, Harder H, Williams J, Eerdekens<br />

G, Yassaa N, Ganzeveld L, Sander R, Lelieveld J<br />

Challenges in quantifying biosphere-atmosphere exchange of nitrogen species (08.1-305)<br />

Sutton M A, Nemitz E, Erisman J W, Beier C, Butterbach Bahl K, Cellier P, de Vries W, Cotrufo F, Skiba U, Di Marco<br />

C, Jones S, Laville P, Soussana J F, Loubet B, Twigg M, Famulari D, Whitehead J, Gallagher M W, Neftel A, Flechard<br />

C R, Herrmann B, Calanca P, Schjoerring J K, Daemmgen U, Horvath L, Tang Y S, Emmett B A, Tietema A, Penuelas<br />

J, Kesik M, Brueggemann N, Pilegaard K, Vesala T, Campbell C L, Olesen J E, Dragosits U, <strong>The</strong>obald M R, Levy P,<br />

Mobbs D C, Milne R, Viovy N, Vuichard N, Smith J U, Smith P, Bergamaschi P, Fowler D, Reis S<br />

Sensitivity of carbon cycling in the European Alps to changes of climate and land cover (08.1-306)<br />

Zierl B, Bugmann H<br />

151


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

2 Past <strong>Global</strong> <strong>Change</strong>s<br />

Pleistocene ice and paleo-strain rates at Taylor Glacier, Antarctica (08.1-307)<br />

Aciego S M, Cuffey K M, Kavanaugh J L, Morse D L, Severinghaus J P<br />

Sequencing events across the Permian-Triassic boundary, Guryul Ravine (Kashmir, India) (08.1-308)<br />

Algeo T J, Hannigan R, Rowe H, Brookfield M, Baud A, Krystyn L, Ellwood B B<br />

Sub-orbital sea-level change in early MIS 5e: New evidence from the Gulf of Corinth, Greece<br />

(08.1-309)<br />

Andrews J E, Portman C, Rowe P J, Leeder M R, Kramers J D<br />

Age and significance of former low-altitude corrie glaciers on Hoy, Orkney Islands (08.1-310)<br />

Ballantyne C K, Hall A M, Phillips W, Binnie S, Kubik P W<br />

Vegetation history, fire history and lake development recorded for 6300 years by pollen, charcoal,<br />

loss on ignition and chironomids at a small lake in southern Kyrgyzstan (Alay Range, Central Asia)<br />

(08.1-311)<br />

Beer R, Heiri O, Tinner W<br />

Pollen representation in surface samples of the Juniperus, Picea and Juglans forest belts of<br />

Kyrgyzstan, central Asia (08.1-312)<br />

Beer R, Tinner W, Carraro G, Grisa E<br />

Surface-exposure ages of Front Range moraines that may have formed during the Younger Dryas,<br />

8.2cal ka, and Little Ice Age events (08.1-313)<br />

Benson L, Madole R, Kubik P W, Mcdonald R<br />

Palaeoclimate-induced range shifts may explain current patterns of spatial genetic variation in<br />

renosterbos (Elytropappus rhinocerotis, Asteraceae) (08.1-314)<br />

Bergh N G, Hedderson T A, Linder H P, Bond W J<br />

Decadal-scale autumn temperature reconstruction back to AD 1580 inferred from the varved sediments<br />

of Lake Silvaplana (southeastern <strong>Swiss</strong> Alps) (08.1-315)<br />

Blass A, Bigler C, Grosjean M, Sturm M<br />

Signature of explosive volcanic eruptions in the sediments of a high- altitude <strong>Swiss</strong> lake (08.1-316)<br />

Blass A, Grosjean M, Livingstone D M, Sturm M<br />

A European pattern climatology 1766-2000 (08.1-317)<br />

Casty C, Raible C C, Stocker T F, Wanner H, Luterbacher J<br />

Reconstructing recent environmental changes from proglacial lake sediments in the western Alps<br />

(Lake blanc huez, 2543 m a.s.l., grandes rousses massif, france) (08.1-318)<br />

Chapron E, Faien X, Magand O, Charlet L, Debret M, Melieres M A<br />

Long-term interactions between Mediterranean climate, vegetation and fire regime at Lago di<br />

Massaciuccoli (Tuscany, Italy) (08.1-319)<br />

Colombaroli D, Marchetto A, Tinner W<br />

Using toponymy to reconstruct past land use: a case study of ‘brusada’ (burn) in southern Switzerland<br />

(08.1-320)<br />

Conedera M, Vassere S, Neff C, Meurer M, Krebs P<br />

27<br />

156


28 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Multiproxy late quaternary stratigraphy of the Nile deep-sea turbidite system - Towards a chronology<br />

of deep-sea terrigeneous systems (08.1-321)<br />

Ducassou E, Capotondi L, Murat A, Bernasconi S M, Mulder T, Gonthier E, Migeon S, Duprat J, Giraudeau J, Mascle<br />

J<br />

Paleoecology of Pennsylvanian phylloid algal buildups in south Guizhou, China (08.1-322)<br />

Enpu G, Samankassou E, Changqing G, Yongli Z Baoliang S<br />

Long-term drought severity variations in Morocco (08.1-323)<br />

Esper J, Frank D, Buentgen U, Verstege A, Luterbacher J<br />

Modern pollen assemblages as climate indicators in southern Europe (08.1-324)<br />

Finsinger W, Heiri O, Valsecchi V, Tinner W, Lotter A F<br />

Reconstruction of millennial changes in dust emission, transport and regional sea ice coverage<br />

using the deep EPICA ice cores from the Atlantic and Indian Ocean sector of Antarctica (08.1-325)<br />

Fischer H, Fundel F, Ruth U, Twarloh B, Wegner A, Udisti R, Becagli S, Castellano E, Morganti A, Severi M, Wolff<br />

E, Littot G, Röthlisberger R, Mulvaney R, Hutterli M A, Kaufmann P, Federer U, Lambert F, Bigler M, Hansson M,<br />

Jonsell U, de Angelis M, Boutron C, Siggaard Andersen M L, Steffensen J P, Barbante C, Gaspari V, Gabrielli P,<br />

Wagenbach D<br />

Adjustment for proxy number and coherence in a large-scale temperature reconstruction<br />

(08.1-326)<br />

Frank D, Esper J, Cook E R<br />

Carbon dioxide release from the North Pacific abyss during the last deglaciation (08.1-327)<br />

Galbraith E D, Jaccard S L, Pedersen T F, Sigman D M, Haug G H, Cook M, Southon J R, Francois R<br />

Smithian-Spathian boundary event: Evidence for global climatic change in the wake of the end-<br />

Permian biotic crisis (08.1-328)<br />

Galfetti T, Hochuli P A, Brayard A, Bucher H, Weissert H, Vigran J O<br />

Dating of syngenetic ice wedges in permafrost with Cl-36 (08.1-329)<br />

Gilichinsky D A, Nolte E, Basilyan A E, Beer J, Blinov A V, Lazarev V E, Kholodov A L, Meyer H, Nikolskiy P A,<br />

Schirrmeister L, Tumskoy V E<br />

Assimilation of the plutonic roots of the Andean arc: Evidence from CO 2-rich fluid inclusions in<br />

olivines (08.1-330)<br />

Ginibre C, Dungan M A<br />

Paleoecology of Late Carboniferous phylloid algae in southern Guizhou, SW China (08.1-331)<br />

Gong E, Mang Y, Guan C, Samankassou E, Sun B, Sun B L<br />

Late Quaternary river development in the southwest Chad Basin: OSL dating of sediment from the<br />

Komadugu palaeofloodplain (northeast Nigeria) (08.1-332)<br />

Gumnior M, Preusser F<br />

Radiocarbon ages of soil charcoals from the southern Alps, Ticino Switzerland (08.1-333)<br />

Hajdas I, Schlumpf N, Minikus Stary N, Hagedorn F, Eckmeier E, Schoch W, Burga C, Bonani G, Schmidt M W I,<br />

Cherubini P<br />

Cosmogenic Be-10-ages from the Store Koldewey island, NE Greenland (08.1-334)<br />

Hakansson L, Graf A, Strasky S, Ivy Ochs S, Kubik P W, Hjort C, Schlüchter C<br />

Evidence for recurrent changes in Lower Triassic oceanic circulation of the Tethys: <strong>The</strong> delta C-13<br />

record from marine sections in Iran (08.1-335)<br />

Horacek M, Richoz S, Brandner R, Krystyn L, Spoetl C


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

1. Flaje-Kiefern (Krusne Hory Mountains): Late Glacial and Holocene vegetation development<br />

(08.1-336)<br />

Jankovska V, Kunes P, van der Knaap W O<br />

Microgram level radiocarbon (C-14) determination on carbonaceous particles in ice (08.1-337)<br />

Jenk T M, Szidat S, Schwikowski M, Gäggeler H W, Wacker L, Synal H A, Saurer M<br />

Orbital and millennial Antarctic climate variability over the past 800,000 years (08.1-338)<br />

Jouzel J, Masson Delmotte V, Cattani O, Dreyfus G, Falourd S, Hoffmann G, Minster B, Nouet J, Barnola J M,<br />

Chappellaz J, Fischer H, Gallet J C, Johnsen S, Leuenberger M, Loulergue L, Lüthi D, Oerter H, Parrenin F, Raisbeck<br />

G, Raynaud D, Schilt A, Schwander J, Selmo E, Souchez R, Spahni R, Stauffer B, Steffensen J P, Stenni B, Stocker T<br />

F, Tison J L, Werner M, Wolff E W<br />

Applying SAR-IRSL methodology for dating fine-grained sediments from lake El’gygytgyn, northeastern<br />

Siberia (08.1-339)<br />

Juschus O, Preusser F, Melles M, Radtke U<br />

Unfractionated excess air: <strong>The</strong> result of incomplete dissolution of entrapped air? (08.1-340)<br />

Klump S, Cirpka O A, Kipfer R<br />

Excess air as a potential tracer for paleohydrological conditions (08.1-341)<br />

Klump S, Grundl T, Purtschert R, Kipfer R<br />

Bedrock landsliding, river incision, and transience of geomorphic hillslope-channel coupling:<br />

Evidence from inner gorges in the <strong>Swiss</strong> Alps (08.1-342)<br />

Korup O, Schlunegger F<br />

Millenial scale variations of the isotopic composition of atmospheric oxygen over Marine Isotopic<br />

Stage 4 (08.1-343)<br />

Landais A, Masson Delmotte V, Combourieu Nebout N, Jouzel J, Blunier T, Leuenberger M, Dahl Jensen D, Johnsen<br />

S<br />

Ages for the Big Stone Moraine and the oldest beaches of glacial Lake Agassiz: Implications for deglaciation<br />

chronology (08.1-344)<br />

Lepper K, Fisher T G, Hajdas I, Lowell T V<br />

Variable Be-10 fluxes in lacustrine sediments from Tristan da Cunha, South Atlantic: a solar record?<br />

(08.1-345)<br />

Ljung K, Bjorck S, Muscheler R, Beer J, Kubik P W<br />

Characterizing carbon isotopic variability in Sphagnum (08.1-346)<br />

Loader N J, Mccarroll D, van der Knaap W O, Robertson I, Gagen M<br />

Detailed record of the mid-Oxfordian (Late Jurassic) positive carbon- isotope excursion in two<br />

hemipelagic sections (France and Switzerland): A plate tectonic trigger? (08.1-347)<br />

Louis Schmid B, Rais P, Bernasconi S M, Pellenard P, Collin P Y, Weissert H<br />

Impact of methane seeps on the local carbon-isotope record: a case study from a Late Jurassic<br />

hemipelagic section (08.1-348)<br />

Louis Schmid B, Rais P, Logvinovich D, Bernasconi S M, Weissert H<br />

Plate tectonic trigger of changes in pCO(2) and climate in the Oxfordian (Late Jurassic): Carbon isotope<br />

and modeling evidence (08.1-349)<br />

Louis Schmid B, Rais P, Schäffer P, Bernasconi S M, Weissert H<br />

New constraints on the gas age-ice age difference along the EPICA ice cores, 0-50 kyr (08.1-350)<br />

Loulergue L, Parrenin F, Blunier T, Barnola J M, Spahni R, Schilt A, Raisbeck G, Chappellaz J<br />

29


30 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Comparison of techniques for dating of subsurface ice from Monlesi ice cave, Switzerland<br />

(08.1-351)<br />

Luetscher M, Bolius D, Schwikowski M, Schotterer U, Smart P L<br />

Detailed sedimentary N isotope records from Cariaco Basin for terminations I and V: Local and<br />

global implications (08.1-352)<br />

Meckler N A , Haug G H, Sigman D M, Plessen B, Peterson L C, Thierstein H R<br />

Grape harvest dates as a proxy for <strong>Swiss</strong> April to August temperature reconstructions back to AD<br />

1480 (08.1-353)<br />

Meier N, Rutishauser T, Pfister C, Wanner H, Luterbacher J<br />

Evidence of a two-fold glacial advance during the last glacial maximum in the Tagliamento end<br />

moraine system (eastern Alps) (08.1-354)<br />

Monegato G, Ravazzi C, Donegana M, Pini R, Calderoni G, Wick L<br />

European ammonoid diversity questions the spreading of anoxia as primary cause for the<br />

Cenomanian/Turonian (Late Cretaceous) mass extinction (08.1-355)<br />

Monnet C, Bucher H<br />

Phosphorus and the roles of productivity and nutrient recycling during oceanic anoxic event 2<br />

(08.1-356)<br />

Mort H P, Adatte T, Föllmi K B, Keller G, Steinmann P, Matera V, Berner Z, Stüben D<br />

<strong>The</strong> Cenomanian/Turonian anoxic event at the Bonarelli level in Italy and Spain: enhanced productivity<br />

and/or better preservation? (08.1-357)<br />

Mort H, Jacquat O, Adatte T, Steinmann P, Föllmi K B, Matera V, Berner Z, Stüben D<br />

Glacial in situ survival in the Western Alps and polytopic autopolyploidy in Biscutella laevigata L.<br />

(Brassicaceae) (08.1-358)<br />

Parisod C, Besnard G<br />

<strong>The</strong> EDC3 chronology for the EPICA dome C ice core (08.1-359)<br />

Parrenin F, Barnola J M, Beer J, Blunier T, Castellano E, Chappellaz J, Dreyfus G, Fischer H, Fujita S, Jouzel J,<br />

Kawamura K, Lemieux Dudon B, Loulergue L, Masson Delmotte V, Narcisi B, Petit J R, Raisbeck G, Raynaud D, Ruth<br />

U, Schwander J, Severi M, Spahni R, Steffensen J P, Svensson A, Udisti R, Waelbroeck C, Wolff E<br />

Palaeoceanographic and palaeoclimatic reorganization around the Middle-Late Jurassic transition<br />

(08.1-360)<br />

Rais P, Louis Schmid B, Bernasconi S M, Weissert H<br />

Direct north-south synchronization of abrupt climate change record in ice cores using Beryllium 10<br />

(08.1-361)<br />

Raisbeck G M, Yiou F, Jouzel J, Stocker T F<br />

Temporal stability of climate-isotope relationships in tree rings of oak and pine (Ticino, Switzerland)<br />

(08.1-362)<br />

Reynolds Henne C E, Siegwolf R T W, Treydte K S, Esper J, Henne S, Saurer M<br />

Climatic cycles during a Neoproterozoic “snowball” glacial epoch (08.1-363)<br />

Rieu R, Allen P A, Ploetze M, Pettke T<br />

EDML1: a chronology for the EPICA deep ice core from Dronning Maud Land, Antarctica, over the<br />

last 150 000 years (08.1-364)<br />

Ruth U, Barnola J M, Beer J, Bigler M, Blunier T, Castellano E, Fischer H, Fundel F, Huybrechts P, Kaufmann P,<br />

Kipfstuhl S, Lambrecht A, Morganti A, Oerter H, Parrenin F, Rybak O, Severi M, Udisti R, Wilhelms F, Wolff E


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Six millennia of atmospheric dust deposition in southern South America (Isla Navarino, Chile)<br />

(08.1-365)<br />

Sapkota A, Cheburkin A K, Bonani G, Shotyk W<br />

Siliceous algae-based seasonal temperature inference and indicator pollen tracking ca. 4,000 years<br />

of climate/land use dependency in the southern Austrian Alps (08.1-366)<br />

Schmidt R, Kamenik C, Roth M<br />

Synchronisation of the EDML and EDC ice cores for the last 52 kyr by volcanic signature matching<br />

(08.1-367)<br />

Severi M, Becagli S, Castellano E, Morganti A, Traversi R, Udisti R, Ruth U, Fischer H, Huybrechts P, Wolff E,<br />

Parrenin F, Kaufmann P, Lambert F, Steffensen J P<br />

A high-resolution, absolute-dated deglacial speleothem record of Indian Ocean climate from Socotra<br />

Island, Yemen (08.1-368)<br />

Shakun J D, Burns S J, Fleitmann D, Kramers J D, Matter A, Al Subary A<br />

Climate changes and volcanic signals during the Bronze Age: A stalagmite record (08.1-369)<br />

Siklosy Z, Demeny A, Vennemann T W, Hegner E, Kramers J D, Leel Ossy Sz<br />

Hyalinea marmarica, a new species of benthic foraminifera from the sea of Marmara (Turkey)<br />

(08.1-370)<br />

Spezzaferri S, Yanko Hombach V<br />

Mesolithic agriculture in Switzerland? A critical review of the evidence (08.1-371)<br />

Tinner W, Nielsen E H, Lotter A F<br />

Signal strength and climate calibration of a European tree-ring isotope network (08.1-372)<br />

Treydte K, Frank D, Esper J, Andreu L, Bednarz Z, Berninger F, Boettger T, Dalessandro C M, Etien N, Filot M,<br />

Grabner M, Guillemin M T, Gutierrez E, Haupt M, Helle G, Hilasvuori E, Jungner H, Kalela Brundin M, Krapiec M,<br />

Leuenberger M, Loader N J, Masson Delmotte V, Pazdur A, Pawelczyk S, Pierre M, Planells O, Pukiene R, Reynolds<br />

Henne C E, Rinne K T, Saracino A, Saurer M, Sonninen E, Stievenard M, Switsur V R, Szczepanek M, Szychowska<br />

Krapiec E, Todaro L, Waterhouse J S, Weigl M, Schleser G H<br />

Oncoid growth and distribution controlled by sea-level fluctuations and climate (Late Oxfordian,<br />

<strong>Swiss</strong> Jura Mountains) (08.1-373)<br />

Vedrine S, Strasser A, Hug W<br />

Interactions between climate and vegetation during the Lateglacial period as recorded by lake and<br />

mire sediment archives in Northern Italy and Southern Switzerland (08.1-374)<br />

Vescovi E, Ravazzi C, Arpenti E, Finsinger W, Pini R, Valsecchi V, Wick L, Ammann B, Tinner W<br />

Primary carbonates and Ca-chloride brines as monitors of a paleo- hydrological regime in the Dead<br />

Sea basin (08.1-375)<br />

Waldmann N, Starinsky A, Stein M<br />

16 000 years of vegetation and settlement history from Egelsee (Menzingen, central Switzerland)<br />

(08.1-376)<br />

Wehrli M, Tinner W, Ammann B<br />

Surface topography and ice flow in the vicinity of the EDML deep- drilling site, Antarctica<br />

(08.1-377)<br />

Wesche C, Eisen O, Oerter H, Schulte D, Steinhage D<br />

Leaf area index for northern and eastern North America at the Last Glacial Maximum: a data-model<br />

comparison (08.1-378)<br />

Williams J W, Gonzales L M, Kaplan J O<br />

31


32 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

A matter of divergence: Tracking recent warming at hemispheric scales using tree ring data<br />

(08.1-379)<br />

Wilson R, D’arrigo R, Buckley B, Büntgen U, Esper J, Frank D, Luckman B, Payette S, Vose R, Youngblut D<br />

Relation between rock uplift and denudation from cosmogenic nuclides in river sediment in the<br />

Central Alps of Switzerland (08.1-380)<br />

Wittmann H, von Blanckenburg F, Kruesmann T, Norton K P, Kubik P W<br />

<strong>The</strong> prelude of the end-Permian mass extinction predates a postulated bolide impact (08.1-381)<br />

Yin H, Feng Q, Baud A, Xie S, Benton M J, Lai X, Bottjer D J<br />

3 Human Dimensions<br />

Linking extreme climate events and economic impacts: Examples from the <strong>Swiss</strong> Alps<br />

(08.1-382)<br />

Beniston M<br />

Reduced exposure to PM10 and attenuated age-related decline in lung function (08.1-383)<br />

Downs S H, Schindler C, Liu L J S, Keidel D, Bayer Oglesby L, Brutsche M H, Gerbase M W, Keller R, Kuenzli N,<br />

Leuenberger P, Probst Hensch N M, Tschopp J M, Zellweger J P, Rochat T, Schwartz J, Ackermann Liebrich U<br />

Climate change-related health impacts in the Hindu Kush-Himalayas (08.1-384)<br />

Ebi K L, Woodruff R, von Hildebrand A, Corvalan C<br />

Lasting management of the countryside. <strong>The</strong> lessons that new regional natural parks must take<br />

from the experience of old communities (08.1-385)<br />

Gerber J D, Rodewald R, Knoepfel P<br />

<strong>The</strong> sustainable management of the landscape: the lessons the new regional nature parks must<br />

draw from the experience of the old corporations (08.1-386)<br />

Gerber J D, Rodewald R, Knoepfel P<br />

Recognising the complexities of ecosystem management and the ecosystem service concept<br />

(08.1-387)<br />

Ghazoul J<br />

Sink or Swim? Water security for growth and development (08.1-388)<br />

Grey D, Sadoff C W<br />

Carbon constraints in the fourteenth and twenty-first centuries (08.1-389)<br />

Hoffmann V, Busch T<br />

Assessing psycho-social effects of participatory landscape planning (08.1-390)<br />

Höppner C, Frick J, Buchecker M<br />

Local learning-networks on energy efficiency in industry - Successful initiative in Germany<br />

(08.1-391)<br />

Jochem E, Gruber E<br />

Objectives of public participation: Which actors should be involved in the decision making for river<br />

restorations? (08.1-392)<br />

Junker B, Buchecker M, Müller Böker U<br />

184


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Portfolio screening to support the mainstreaming of adaptation to climate change into development<br />

assistance (08.1-393)<br />

Klein R J T, Eriksen S E H, Naess L O, Hammill A, Tanner T M, Robledo C, O’brien K L<br />

A MERGE model with endogenous technological change and the cost of carbon stabilization<br />

(08.1-394)<br />

Kypreos S<br />

Characterization of source-specific air pollution exposure for a large population-based <strong>Swiss</strong> Cohort<br />

(SAPALDIA) (08.1-395)<br />

Liu L J S, Curjuric I, Keidel D, Heldstab J, Künzli N, Bayer Oglesby L, Ackermann Liebrich U, Schindler C<br />

Climate risks and peak oil: Challenge for the trans disciplinary research (08.1-396)<br />

Maibach M, Guyer M, Kläy A<br />

Does climate policy promote development? (08.1-397)<br />

Michaelowa A, Michaelowa K<br />

Climate or development: is ODA diverted from its original purpose? (08.1-398)<br />

Michaelowa A, Michaelowa K<br />

Phenology of Ixodes ricinus and infection with Borrelia burgdorferi sensu lato along a North- and<br />

South-facing altitudinal gradient on Chaumont Mountain, Switzerland (08.1-399)<br />

Moran Cadenas F, Rais O, Jouda F, Douet V, Humair P F, Moret J, Gern L<br />

Integrated assessment of global climate change with learning-by-doing and energy-related research<br />

and development (08.1-400)<br />

Müller Fürstenberger G, Stephan G<br />

CDM potential of bagasse cogeneration in India (08.1-401)<br />

Purohita P, Michaelowa A<br />

<strong>The</strong> economic potential of bagasse cogeneration as CDM projects in Indonesia (08.1-402)<br />

Restuti D, Michaelowa A<br />

Short-term effects of carbon monoxide on mortality: An analysis within the APHEA project<br />

(08.1-403)<br />

Samoli E, Touloumi G, Schwartz J, Anderson H R, Schindler C, Forsberg B, Vigotti M A, Vonk J, Kosnik M, Skorkovsky<br />

J, Katsouyanni K<br />

A synopsis of land use, land-use change and forestry (LULUCF) under the Kyoto Protocol and<br />

Marrakech Accords (08.1-404)<br />

Schlamadinger B, Bird N, Johns T, Brown S, Canadell J, Ciccarese L, Dutschke M, Fiedler J, Fischlin A, Fearnside P,<br />

Forner C, Freibauer A, Frumhoff P, Hoehne N, Kirschbaum M U F, Labat A, Marland G, Michaelowa A, Montanarella<br />

L, Moutinho P, Murdiyarso D, Pena N, Pingoud K, Rakonczay Z, Rametsteiner E, Rock J, Sanz M J, Schneider U A,<br />

Shuidenko A, Skutsch M, Smith P, Somogyi Z, Trines E, Ward M, Yamagata Y<br />

How is climate change perceived in relation to other socioeconomic and environmental threats in<br />

Nairobi, Kenya? (08.1-405)<br />

Shisanya C A, Khayesi M<br />

<strong>The</strong> future of the <strong>Swiss</strong> Alps: A participatory sustainability assessment of agricultural and landscape<br />

scenarios (08.1-406)<br />

Soliva R<br />

33


34 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Output and abatement effects of allocation readjustment in permit trade (08.1-407)<br />

Sterner T, Müller A<br />

Does the current Clean Development Mechanism (CDM) deliver its sustainable development claim?<br />

An analysis of officially registered CDM projects (08.1-408)<br />

Sutter C, Parreno J C<br />

Technology in climate policy and climate models - Introduction (08.1-409)<br />

Thalmann P<br />

Perceptions and evaluations of biosphere reserves by local residents in Switzerland and Ukraine<br />

(08.1-410)<br />

Wallner A, Bauer N, Hunziker M<br />

<strong>The</strong> concept of sustainable development - consequences for social theory. Research desiderata and a<br />

proposal for a research strategy in social geography (08.1-411)<br />

Zierhofer W<br />

4 Mitigation and Adaptation Technologies<br />

<strong>The</strong>rmo-economic optimization of a solid oxide fuel cell, gas turbine hybrid system (08.1-412)<br />

Autissier N, Palazzi F, Marechal F, van Herle J, Favrat D<br />

Effect of pressure and fuel-air unmixedness on NOx emissions from industrial gas turbine burners<br />

(08.1-413)<br />

Biagioli F, Güthe F<br />

Consumption and efficiency of a passenger car with a hydrogen/oxygen PEFC based hybrid electric<br />

drivetrain (08.1-414)<br />

Büchi F N, Paganelli G, Dietrich P, Laurent D, Tsukada A, Varenne P, Delfino A, Koetz R, Freunberger S A, Magne P<br />

A, Walser D, Olsommer D<br />

Flame-synthesized LaCoO3-supported Pd 2. Catalytic behavior in the reduction of NO by H-2 under<br />

lean conditions (08.1-415)<br />

Chiarello G L, Ferri D, Grunwaldt J D, Forni L, Baiker A<br />

Flame-synthesized LaCoO3-supported Pd 1. Structure, thermal stability and reducibility (08.1-416)<br />

Chiarello G L, Grunwaldt J D, Ferri D, Krumeich R, Oliva C, Forni L, Baiker A<br />

Increase of passenger car engine efficiency with low engine-out emissions using hydrogen-natural<br />

gas mixtures: A thermodynamic analysis (08.1-417)<br />

Dimopoulos P, Rechsteiner C, Soltic P, Laemmle C, Boulouchos K<br />

Multi-regional long-term electricity supply scenarios with fusion (08.1-418)<br />

Gnansounou E, Bednyagin D<br />

Carbothermal reduction of alumina: <strong>The</strong>rmochemical equilibrium calculations and experimental<br />

investigation (08.1-419)<br />

Halmann M, Frei A, Steinfeld A<br />

Secondarv effects of catalytic diesel particulate filters: Copper- induced formation of PCDD/Fs<br />

(08.1-420)<br />

Heeb N V, Zennegg M, Gujer E, Honegger P, Zeyer K, Gfeller U, Wichser A, Kohler M, Schmid P, Emmenegger L, Ulrich<br />

A, Wenger D, Petermann J L, Czerwinski J, Mosimann T, Kasper M, Mayer A<br />

194


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

Towards multi-source multi-product energy systems (08.1-421)<br />

Hemmes K, Zachariah Wolff J L, Geidl M, Andersson G<br />

An energy management method for the food industry (08.1-422)<br />

Müller D C A, Marechal F M A, Wolewinski T, Roux P J<br />

H 2O-splitting thermochemical cycle based on ZnO/Zn-redox: Quenching the effluents from the ZnO<br />

dissociation (08.1-423)<br />

Müller R, Steinfeld A<br />

Towards an improved architectural quality of building integrated solar thermal systems (BIST)<br />

(08.1-424)<br />

Munari Probst M C , Roecker C<br />

Biofuels must deliver on their promise of sustainability (08.1-425)<br />

Opal C<br />

A methodology for thermo-economic modeling and optimization of solid oxide fuel cell systems<br />

(08.1-426)<br />

Palazzi F, Autissier N, Marechal F M A, Favrat D<br />

Dynamics of a solar thermochemical reactor for steam-reforming of methane (08.1-427)<br />

Petrasch J, Steinfeld A<br />

Development steps for parabolic trough solar power technologies with maximum impact on cost<br />

reduction (08.1-428)<br />

Pitz P R, Dersch J, Milow B, Tellez F, Ferriere A, Langnickel U, Steinfeld A, Karni J, Zarza E, Popel O<br />

Optimum battery size for fuel cell hybrid electric vehicle - Part I (08.1-429)<br />

Sundstrom O, Stefanopoulou A<br />

Optimum Battery Size for Fuel Cell Hybrid Electric Vehicle With Transient Loading Consideration—<br />

Part II (08.1-430)<br />

Sundstrom O, Stefanopoulou A<br />

5 General Topics<br />

What is a green solvent? A comprehensive framework for the environmental assessment of solvents<br />

(08.1-431)<br />

Capello C, Fischer U, Hungerbühler K<br />

Effect of solar water disinfection (SODIS) on model microorganisms under improved and field SODIS<br />

conditions (08.1-432)<br />

Dejung S, Fuentes I, Almanza G, Jarro R, Navarro L, Arias G, Urquieta E, Torrico A, Fenandez W, Iriarte M, Birrer<br />

C, Stahel W A, Wegelin M<br />

Cumulative energy extraction from the natural environment (CEENE): a comprehensive life cycle<br />

impact assessment method for resource accounting (08.1-433)<br />

Dewulf J, Bosch M E, de Meester B, van der Vorst G, van Langenhove H, Hellweg S, Huijbregts M A J<br />

<strong>The</strong> environmental relevance of capital goods in life cycle assessments of products and services<br />

(08.1-434)<br />

Frischknecht R, Althaus H J, Bauer C, Doka G, Heck T, Jungbluth N, Kellenberger D, Nemecek T<br />

35<br />

200


36 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Short List of all <strong>Abstracts</strong><br />

New concepts of Be-10 AMS at low energies (08.1-435)<br />

Grajcar M, Döbeli M, Kubik P W, Synal H A, Wacker L, Suter M<br />

Terrestrial ecotoxicity and effect factors of metals in life cycle assessment (LCA) (08.1-436)<br />

Haye S, Slaveykova V I, Payet J<br />

Challenges for forestry and forest research - How to promote effective cooperation between science<br />

and practice? (08.1-437)<br />

Jäger J, Pluess A, Klank C, Ghazoul J<br />

Environmental impacts of conventional and sustainable investment funds compared using inputoutput<br />

life-cycle assessment (08.1-438)<br />

Köllner T, Suh S, Weber O, Moser C, Scholz R W<br />

Problem-oriented environmental research: <strong>The</strong> view of geography and landscape ecology on science<br />

and application (08.1-439)<br />

Leser H<br />

Linking models of land use, resources, and economy to simulate the development of mountain<br />

regions (ALPSCAPE) (08.1-440)<br />

Lundstroem C, Kytzia S, Walz A, Gret Regamey A, Bebi P<br />

Occurrence, behavior and effects of nanoparticles in the environment (08.1-441)<br />

Nowack B, Bucheli T D<br />

Life cycle assessment in the telecommunication industry: A review (08.1-442)<br />

Scharnhorst W<br />

Agricultural decline, landscape change, and outmigration: Debating the sustainability of three scenarios<br />

for a <strong>Swiss</strong> mountain region (08.1-443)<br />

Soliva R<br />

Advances in particle identification in AMS at low energies (08.1-444)<br />

Suter M, Döbeli M, Grajcar M, Müller A, Stocker M, Sun G, Synal H A, Wacker L<br />

MICADAS: A new compact radiocarbon AMS system (08.1-445)<br />

Synal H A, Stocker M, Suter M<br />

Restoring dense vegetation can slow mountain erosion to near natural benchmark levels (08.1-446)<br />

Vanacker V, von Blanckenburg F, Govers G, Molina A, Poesen J, Deckers J, Kubik P W<br />

Wooden building products in comparative LCA (08.1-447)<br />

Werner F, Richter K


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 37<br />

1.1 Atmosphere<br />

08.1-1<br />

Identification of the mass spectral signature of<br />

organic aerosols from wood burning emissions<br />

Alfarra M R, Prevot A S H, Szidatt S, Sandradewi J,<br />

Weimer S, Lanz V A, Schreiber D, Mohr M,<br />

Baltensperger U<br />

Switzerland<br />

Urban Studies , Meteorology & Atmospheric Sciences<br />

Throughout the winter months, the village of Roveredo,<br />

Switzerland, frequently experiences strong<br />

temperature inversions that contribute to elevated<br />

levels of particulate matter. Wood is used as<br />

fuel for 75% of the domestic heating installations<br />

in Roveredo, which makes it a suitable location to<br />

study wood burning emissions in the atmosphere<br />

in winter. An Aerodyne quadrupole aerosol mass<br />

spectrometer (Q-AMS) was used to characterize<br />

the composition of the submicrometer, non- refractory<br />

aerosol particles at this location during<br />

two field campaigns in March and December 2005.<br />

Wood burning was found to be a major source of<br />

aerosols at this location in winter. Organics dominated<br />

the composition of the aerosols from this<br />

source, contributing up to 85% of the total AMS<br />

measured mass during the afternoon and evening<br />

hours. Carbonaceous particle analysis showed<br />

that organic carbon composed up to 86% of the<br />

total carbon mass collected at evening times. Results<br />

from C-14 isotope determination revealed<br />

that up to 94% of the organic mass came from<br />

nonfossil sources, which can be attributed mostly<br />

to wood burning. <strong>The</strong> unique combination of offline<br />

C-14 isotope analysis and on-line aerosol mass<br />

spectrometry was used to identify periods during<br />

which organic mass was mainly from wood burning<br />

emissions and allowed for the identification<br />

of the AMS spectral signature of this source in the<br />

atmosphere. <strong>The</strong> identified ambient signature of<br />

wood burning was found to be very similar to the<br />

mass spectral signature obtained during the burning<br />

of chestnut wood samples in a small stove and<br />

also to the spectrum of levoglucosan. Particles<br />

from wood burning appeared to be composed of<br />

highly oxygenated organic compounds, and mass<br />

fragments 60, 73, and 137 have been suggested<br />

as marker fragments for wood burning aerosols.<br />

Mass fragment 44, which is used as a marker for<br />

oxygenated organic aerosols (OOA), contributed<br />

about 5% to the total organic signal from primary<br />

wood burning sources, <strong>The</strong> ratio of the organic<br />

mass emitted from wood burning to m/z 60 in<br />

Roveredo is 36. This ratio may be used to provide<br />

an estimate of the organic aerosol mass emitted<br />

from wood burning in other locations.<br />

Environmental Science Technology, 2007, V41,<br />

N16, AUG 15, pp 5770-5777.<br />

08.1-2<br />

A new atmospheric aerosol phase equilibrium<br />

model (UHAERO): organic systems<br />

Amundson N R, Caboussat A, He J W, Martynenko<br />

A V, Landry C, Tong C, Seinfeld J H<br />

USA, Switzerland<br />

Meteorology & Atmospheric Sciences , Modelling<br />

In atmospheric aerosols, water and volatile inorganic<br />

and organic species are distributed between<br />

the gas and aerosol phases in accordance with<br />

thermodynamic equilibrium. Within an atmospheric<br />

particle, liquid and solid phases can exist<br />

at equilibrium. Models exist for computation of<br />

phase equilibria for inorganic/water mixtures typical<br />

of atmospheric aerosols; when organic species<br />

are present, the phase equilibrium problem is<br />

complicated by organic /water interactions as well<br />

as the potentially large number of organic species.<br />

We present here an extension of the UHAERO inorganic<br />

thermodynamic model (Amundson et al.,<br />

2006c) to organic/water systems. Phase diagrams<br />

for a number of model organic/water systems<br />

characteristic of both primary and secondary<br />

organic aerosols are computed. Also calculated<br />

are inorganic/organic/water phase diagrams that<br />

show the effect of organics on inorganic deliquescence<br />

behavior. <strong>The</strong> effect of the choice of activity<br />

coefficient model for organics on the computed<br />

phase equilibria is explored.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N17, pp 4675-4698.<br />

08.1-3<br />

Equilibrium sorption of gaseous organic chemicals<br />

to fiber filters used for aerosol studies<br />

Arp H P H, Schwarzenbach R P, Goss K U<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , Engineering<br />

Fiber filters commonly used to collect aerosols<br />

for various analyses also collect gaseous organic<br />

chemicals during sampling. <strong>The</strong>se sorbed chemicals<br />

can lead to serious artifacts, particularly<br />

when analyzing aerosols for organic compounds<br />

and organic carbonaceous material. To date, this<br />

sorption process has only been looked at for a few<br />

types of filters and compound classes. This work<br />

presents a comprehensive study of this sorption<br />

process for various, widely used fiber filters and a<br />

broad variety of compound classes. Furthermore,<br />

important factors have been investigated, including<br />

relative humidity, temperature, baking and<br />

exposure to ambient air during sampling. From<br />

these data, poly-parameter linear-free energy relationships<br />

were derived that allow for estimations<br />

of sorption constants of gaseous organic<br />

compounds on different filter types. Based on the<br />

results, recommendations are provided to help


38<br />

predict, minimize and ensure reproducibility of<br />

artifacts caused by gaseous organic compounds<br />

sorbing to fiber filters..<br />

Atmospheric Environment, 2007, V41, N37, DEC,<br />

pp 8241-8252.<br />

08.1-4<br />

Interference of organic signals in highly time<br />

resolved nitrate measurements by low mass<br />

resolution aerosol mass spectrometry<br />

Bae M S, Schwab F J, Zhang Q, Hogrefe O,<br />

Demerjian K L, Weimer A, Rhoads K, Orsini D,<br />

Venkatachari P, Hopke P K<br />

USA, Switzerland<br />

Meteorology & Atmospheric Sciences ,<br />

Urban Studies<br />

Highly time resolved measurements of nitrate in<br />

ambient aerosols were conducted by an Aerodyne<br />

Quadrupole Aerosol Mass Spectrometer (Q-AMS<br />

or simply AMS) and a particle-into-liquid sampler<br />

(PILS) coupled to ion chromatography from field<br />

intensives at two sites: an urban site in New York<br />

City (Queens College; QC) for wintertime (22 January<br />

to 5 February 2004) and a rural site in southwestern<br />

New York state (Pinnacle State Park; PSP)<br />

for summertime (18 July to 6 August 2004). In this<br />

study, we report that in rural atmospheres the<br />

inorganic nitrate signal from Q-AMS may contain<br />

significant interferences from organic signals.<br />

Analysis of the QC data indicates a good agreement<br />

between the PILS-nitrate and AMS-nitrate<br />

measurements (R-2 = 0.94; linear regression slope<br />

= 1.05). In addition, the m/z 30 and m/z 46 (two<br />

dominant ion fragments in nitrate mass spectrum)<br />

signals tightly correlate at QC (R-2 = 0.98)<br />

and have an average ratio similar to that determined<br />

in the laboratory for NH 4NO 3 (m/z 30/m/z<br />

46 = 2.4). In contrast, at the PSP site the correlation<br />

between PILS- and AMS- nitrate was poor<br />

(R-2 = 0.34), the AMS reported nitrate values were<br />

substantially higher, and the m/z 30 to m/z 46 ratios<br />

were generally much larger than 2.4. <strong>The</strong>se<br />

observations, together with evaluations by aerosol<br />

phase ion balance, indicate that the AMS m/z<br />

30 signals at PSP have been strongly influenced<br />

by organic compounds that also produce signals<br />

at m/z 30, e. g., organic nitrates (NO+), oxygenated<br />

organics (CH 2O+), hydrocarbon-like organics<br />

(C2H6+), and nitrogen- containing organic compounds<br />

(CH 4N+).<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND22, NOV 24 ARTN: D22305.<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

08.1-5<br />

Small-scale cloud processes and climate<br />

Baker M B, Peter T<br />

USA, Switzerland<br />

Meteorology & Atmospheric Sciences<br />

Clouds constitute the largest single source of<br />

uncertainty in climate prediction. A better understanding<br />

of small- scale cloud processes could<br />

shed light on the role of clouds in the climate system.<br />

Nature, 2008, V451, N7176, JAN 17, pp 299-300.<br />

08.1-6<br />

Chemical analysis of atmospheric aerosols<br />

Baltensperger U, Prevot A S H<br />

Switzerland<br />

Meteorology & Atmospheric Sciences ,<br />

Urban Studies<br />

Analytical and Bioanalytical Chemistry, 2008, V390,<br />

N1, JAN, pp 277-280.<br />

08.1-7<br />

Entering into the “greenhouse century”:<br />

Recent record temperatures in Switzerland are<br />

comparable to the upper temperature quantiles<br />

in a greenhouse climate<br />

Beniston M<br />

Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

This paper investigates the recent spate of recordbreaking<br />

warm seasons that have affected Switzerland<br />

in less than a decade and compares the<br />

seasonal statistics to those simulated for a ‘’greenhouse-gas’’<br />

climate by the end of the 21st century.<br />

<strong>The</strong> peaks of minimum and maximum temperatures<br />

observed during some the record seasons<br />

enter well into the 25%-75% temperature quantile<br />

range for the scenario climate simulated by a<br />

set of regional climate models. <strong>The</strong> anomalously<br />

warm seasons allow a ‘’preview’’ of conditions<br />

that may occur with greater frequency in the future.<br />

<strong>The</strong> use of current data as a form of proxy<br />

for the future enables an assessment of the possible<br />

impacts on the natural and socio-economic<br />

environments, and can help in considering possible<br />

adaptation strategies to reduce some of the<br />

associated risks of climatic change.<br />

Geophysical Research Letters, 2007, V34, N16,<br />

AUG 30 ARTN: L16710.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 39<br />

08.1-8<br />

Civil Aircraft for the regular investigation of<br />

the atmosphere based on an instrumented<br />

container: <strong>The</strong> new CARIBIC system<br />

Brenninkmeijer C A M, Crutzen P, Boumard F, Dauer<br />

T, Dix B, Ebinghaus R, Filippi D, Fischer H, Franke<br />

H, Friess U, Heintzenberg J, Helleis F, Hermann M,<br />

Kock H H, Koeppel C, Lelieveld J, Leuenberger M,<br />

Martinsson B G, Miemczyk S, Moret H P, Nguyen<br />

H N, Nyfeler P, Oram D, Osullivan D, Penkett S,<br />

Platt U, Pupek M, Ramonet M, Randa B, Reichelt<br />

M, Rhee T S, Rohwer J, Rosenfeld K, Scharffe D,<br />

Schlager H, Schumann U, Slemr F, Sprung D, Stock<br />

P, Thaler R, Valentino F, van Velthoven P, Waibel<br />

A, Wandel A, Waschitschek K, Wiedensohler A,<br />

Xueref Remy I, Zahn A, Zech U, Ziereis H<br />

Germany, France, Switzerland, Sweden, England,<br />

Netherlands<br />

Meteorology & Atmospheric Sciences ,<br />

Instruments & Instrumentation<br />

An airfreight container with automated instruments<br />

for measurement of atmospheric gases and<br />

trace compounds was operated on a monthly basis<br />

onboard a Boeing 767-300 ER of LTU International<br />

Airways during long- distance flights from 1997<br />

to 2002 (CARIBIC, Civil Aircraft for Regular Investigation<br />

of the Atmosphere Based on an Instrument<br />

Container, http://www.caribic-atmospheric.<br />

com). Subsequently a more advanced system has<br />

been developed, using a larger capacity container<br />

with additional equipment and an improved inlet<br />

system. CARIBIC phase #2 was implemented on<br />

a new long-range aircraft type Airbus A340-600<br />

of the Lufthansa German Airlines (Star Alliance)<br />

in December 2004, creating a powerful flying<br />

observatory. <strong>The</strong> instrument package comprises<br />

detectors for the measurement of O-3, total and<br />

gaseous H 2O, NO and NOy, CO, CO 2, O-2, Hg, and<br />

number concentrations of sub- micrometer particles<br />

(>4 nm, >12 nm, and >18 nm diameter). Furthermore,<br />

an optical particle counter (OPC) and<br />

a proton transfer mass spectrometer (PTR-MS) are<br />

incorporated. Aerosol samples are collected for<br />

analysis of elemental composition and particle<br />

morphology after flight. Air samples are taken<br />

in glass containers for laboratory analyses of hydrocarbons,<br />

halocarbons and greenhouse gases<br />

(including isotopic composition of CO 2) in several<br />

laboratories. Absorption tubes collect oxygenated<br />

volatile organic compounds. Three differential optical<br />

absorption spectrometers (DOAS) with their<br />

telescopes mounted in the inlet system measure<br />

atmospheric trace gases such as BrO, HONO, and<br />

NO 2. A video camera mounted in the inlet provides<br />

information about clouds along the flight<br />

track. <strong>The</strong> flying observatory, its equipment and<br />

examples of measurement results are reported.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N18, pp 4953-4976.<br />

08.1-9<br />

Fires and climate linked in nineteenth century<br />

Brönnimann S<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , History ,<br />

Multidisciplinary Sciences<br />

Nature, 2007, V448, N7157, AUG 30, p 992.<br />

08.1-10<br />

Reconstructing the quasi-biennial oscillation<br />

back to the early 1900s<br />

Brönnimann S, Annis J L, Vogler C, Jones P D<br />

Switzerland, England<br />

Meteorology & Atmospheric Sciences<br />

<strong>The</strong> quasi-biennial oscillation (QBO) is important<br />

for understanding the dynamical and chemical<br />

variability of the global stratosphere. Currently<br />

available wind data from the equatorial stratosphere<br />

extend back to 1953. Here we present reconstructions<br />

of the QBO extending back to 1900<br />

that can be used to constrain climate model simulations.<br />

<strong>The</strong> reconstructions are based on historical<br />

pilot balloon data as well as hourly sea-level<br />

pressure (SLP) data from Jakarta, Indonesia. <strong>The</strong><br />

latter were used to extract the signal of the solar<br />

semi-diurnal tide in the middle atmosphere,<br />

which is modulated by the QBO. <strong>The</strong> reconstructions<br />

are in good agreement with the QBO signal<br />

extracted from historical total ozone data extending<br />

back to 1924. Further analyses suggest that<br />

the maximum phases of the QBO are captured<br />

relatively well after about 1910.<br />

Geophysical Research Letters, 2007, V34, N22,<br />

NOV 20 ARTN: L22805.<br />

08.1-11<br />

Temporal and spatial temperature variability<br />

and change over Spain during 1850-2005<br />

Brunet M, Jones P D, Sigro J, Saladie O, Aguilar E,<br />

Moberg A, Della Marta P M, Lister D, Walther A,<br />

Lopez D<br />

Spain, England, Sweden, Switzerland, Australia<br />

Meteorology & Atmospheric Sciences<br />

(1) We analyze temporal and spatial patterns of<br />

temperature change over Spain during the period<br />

1850 - 2005, using daily maximum (T-max) , minimum<br />

(T-min), and mean (T-mean) temperatures<br />

from the 22 longest and most reliable Spanish records.<br />

Over mainland Spain, a significant (at 0.01<br />

level) warming of 0.10 degrees C/decade is found<br />

for the annual average of T-mean. Autumn and<br />

winter contributed slightly more than spring and


40<br />

summer to the annual warming over the 1850 -<br />

2005 period. <strong>The</strong> overall warming is also associated<br />

with higher rates of change for T-max than<br />

T-min (0.11 degrees versus 0.08 degrees C /decade<br />

for 1850 - 2005). This asymmetric diurnal warming<br />

increased in the twentieth century (0.17 degrees<br />

versus 0.09 degrees C/decade during 1901<br />

- 2005). Nevertheless, at many (few) individual stations,<br />

the difference between T-max and T-min is<br />

not statistically significant over 1850 - 2005 (1901<br />

- 2005). Principal Component Analysis has been<br />

carried out to identify spatial modes of Spanish<br />

long-term temperature variability (1901 - 2005).<br />

Three principal spatial patterns are found, Northern<br />

Spain, Southeastern and Eastern Spain, and<br />

Southwestern Spain. All three patterns show<br />

similar significant warming trends. <strong>The</strong> overall<br />

warming has been more associated with reductions<br />

in cold extremes, as opposed to increases in<br />

warm extremes. Estimated trends in the number<br />

of moderately extreme cold days (T-max < 10th<br />

percentile) and moderately extreme cold nights<br />

(T-min < 10th percentile) show significant reductions<br />

of 0.74 and 0.54 days/decade, respectively,<br />

over 1850 - 2005. Moderately extreme warm days<br />

and nights (T-max and T-min > 90th percentile) increased<br />

significantly but at lower rates of 0.53 and<br />

0.49 days /decade.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND12, JUN 30 ARTN: D12117.<br />

08.1-12<br />

A concept for a satellite mission to measure<br />

cloud ice water path, ice particle size, and<br />

cloud altitude<br />

Bühler S A, Jimenez C, Evans K F, Eriksson P, Rydberg<br />

B, Heymsfield A J, Stubenrauch C J, Lohmann<br />

U, Emde C, John V O, Sreerekha T R, Davis C P<br />

Sweden, USA, France, Switzerland, Germany, England,<br />

Scotland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

A passive satellite radiometer operating at submillimetre<br />

wavelengths can measure cloud ice<br />

water path (IWP), ice particle size, and cloud altitude.<br />

<strong>The</strong> paper first discusses the scientific background<br />

for such measurements. Formal scientific<br />

mission requirements are derived, based on this<br />

background and earlier assessments. <strong>The</strong> paper<br />

then presents a comprehensive prototype instrument<br />

and mission concept, and demonstrates<br />

that it meets the requirements. <strong>The</strong> instrument is<br />

a conically scanning 12-channel radiometer with<br />

channels between 183 and 664 GHz, proposed to<br />

fly in tandem with one of the Metop satellites. It<br />

can measure IWP with a relative accuracy of approximately<br />

20% and a detection threshold of ap-<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

proximately 2 g m (-2). <strong>The</strong> median mass equivalent<br />

sphere diameter of the ice particles can be<br />

measured with an accuracy of approximately 30<br />

µm, and the median IWP cloud altitude can be<br />

measured with an accuracy of approximately 300<br />

m. All the above accuracies are median absolute<br />

error values; root mean square error values are approximately<br />

twice as high, due to rare outliers.<br />

Quarterly Journal of the Royal Meteorological Society,<br />

2007, V133, OCT, S2, pp 109-128.<br />

08.1-13<br />

Concentration profiles of particles settling in<br />

the neutral and stratified atmospheric boundary<br />

layer<br />

Chamecki M, van Hout R, Meneveau C,<br />

Parlange M B<br />

USA, Israel, Switzerland<br />

Meteorology & Atmospheric Sciences , Plant<br />

Sciences , Forestry<br />

An expression for the vertical equilibrium concentration<br />

profile of heavy particles, including the effects<br />

of canopy on the eddy diffusivity as well as<br />

corrections for atmospheric stability, is proposed.<br />

This expression is validated against measurements<br />

of vertical concentration profiles of corn<br />

pollen above a corn field. <strong>The</strong> fitted theoretical<br />

profiles show that particle settling is correctly<br />

accounted for. <strong>The</strong> sensitivity to variations in the<br />

turbulent Schmidt number, settling velocity and<br />

stability corrections are explicitly characterized.<br />

<strong>The</strong> importance of independent measurements of<br />

the surface flux of pollen in future experiments<br />

is noted.<br />

Boundary Layer Meteorology, 2007, V125, N1,<br />

OCT, pp 25-38.<br />

08.1-14<br />

<strong>The</strong> influence of small aerosol particles on the<br />

properties of water and ice clouds<br />

Choularton T, Bower K N, Weingartner E, Crawford<br />

I, Coe H, Gallagher M W, Flynn M, Crosier J, Connolly<br />

P, Targino A, Alfarra M R, Baltensperger U,<br />

Sjogren S, Verheggen B, Cozic J, Gysel M<br />

England, Switzerland<br />

Meteorology & Atmospheric Sciences<br />

In this paper, results are presented of the in. uence<br />

of small organic- and soot- containing particles on<br />

the formation of water and ice clouds. <strong>The</strong>re is<br />

strong evidence that these particles have grown<br />

from nano particle seeds produced by the combustion<br />

of oil products. Two series ofield experiments<br />

are selected to represent the observations made.<br />

<strong>The</strong>. first is the CLoud Aerosol Characterisation<br />

Experiment (CLACE) series of experiments performed<br />

at a high Alpine site (Jungfraujoch), where


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 41<br />

cloud was in contact with the ground and the<br />

measuring station. Both water and ice clouds were<br />

examined at different times of the year. <strong>The</strong> second<br />

series of experiments is the CLOud Processing<br />

of regional Air Pollution advecting over land and<br />

sea (CLOPAP) series, where ageing pollution aerosol<br />

from UK cities was observed, from an airborne<br />

platform, to interact with warm stratocumulus<br />

cloud in a cloud- capped atmospheric boundary<br />

layer. Combining the results it is shown that aged<br />

pollution aerosol consists of an internal mixture<br />

of organics, sulfate, nitrate and ammonium, the<br />

organic component is dominated by highly oxidized<br />

secondary material. <strong>The</strong> relative contributions<br />

and absolute loadings of the components<br />

vary with location and season. However, these<br />

aerosols act as Cloud Condensation Nuclei (CCN)<br />

and much of the organic material, along with the<br />

other species, is incorporated into cloud droplets.<br />

In ice and mixed phase cloud, it is observed that<br />

very sharp transitions (extending over just a few<br />

metres) are present between highly glaciated regions<br />

and regions consisting of supercooled water.<br />

This is a unique. finding; however, aircraft<br />

observations in cumulus suggest that this kind of<br />

structure may be found in these cloud types too. It<br />

is suggested that this sharp transition is caused by<br />

ice nucleation initiated by oxidised organic aerosol<br />

coated with sulfate in more polluted regions<br />

of cloud, sometimes enhanced by secondary ice<br />

particle production in these regions.<br />

Faraday Discussions, 2008, V137, pp 205-222.<br />

08.1-15<br />

Limits on climate sensitivity derived from recent<br />

satellite and surface observations<br />

Chylek P, Lohmann U, Dubey M, Mishchenko M,<br />

Kahn R, Ohmura A<br />

USA, Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

An analysis of satellite and surface measurements<br />

of aerosol optical depth suggests that global average<br />

of aerosol optical depth has been recently<br />

decreasing at the rate of around 0.0014/a. This<br />

decrease is nonuniform with the fastest decrease<br />

observed over the United States and Europe. <strong>The</strong><br />

observed rate of decreasing aerosol optical depth<br />

produces the top of the atmosphere radiative forcing<br />

that is comparable to forcing due to the current<br />

rate of increasing atmospheric concentration<br />

of carbon dioxide and other greenhouse gases.<br />

Consequently, both increasing atmospheric concentration<br />

of greenhouse gases and decreasing<br />

loading of atmospheric aerosols are major contributors<br />

to the top-of-atmosphere radiative forc-<br />

ing. We find that the climate sensitivity is reduced<br />

by at least a factor of 2 when direct and indirect<br />

effects of decreasing aerosols are included, compared<br />

to the case where the radiative forcing is<br />

ascribed only to increases in atmospheric concentrations<br />

of carbon dioxide. We find the empirical<br />

climate sensitivity to be between 0.29 and 0.48 K/<br />

Wm(-2) when aerosol direct and indirect radiative<br />

forcing is included.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND24, DEC 13 ARTN: D24S04.<br />

08.1-16<br />

Long-term trend analysis of aerosol variables<br />

at the high-alpine site Jungfraujoch<br />

Collaud Coen M, Weingartner E, Nyeki S, Cozic J,<br />

Henning S, Verheggen B, Gehrig R, Baltensperger U<br />

Switzerland<br />

Meteorology & Atmospheric Sciences<br />

This study reports the first long-term trend analysis<br />

of aerosol optical measurements at the highalpine<br />

site Jungfraujoch, which started 10.5 years<br />

ago. Since the aerosol variables are approximately<br />

lognormally distributed, the seasonal Kendall test<br />

and Sen’s slope estimator were applied as nonparametric<br />

methods to detect the long- term trends for<br />

each month. <strong>The</strong> yearly trend was estimated by a<br />

least-mean-square fit, and the number of years<br />

necessary to detect this trend was calculated. <strong>The</strong><br />

most significant trend is the increase (4-7% yr(-1))<br />

in light-scattering coefficients during the September<br />

to December period. <strong>The</strong> light absorption and<br />

backscattering coefficients and the aerosol number<br />

concentration also show a positive trend during<br />

this time of the year. <strong>The</strong> hemispheric backscattering<br />

fraction and the scattering exponent<br />

calculated with the smaller wavelengths (450 and<br />

550 nm), which relate to the small aerosol size<br />

fraction, decrease except during the summer,<br />

whereas the scattering exponent calculated with<br />

the larger wavelengths (550 and 700 nm) remains<br />

constant. Generally, the summer months at the<br />

Jungfraujoch, which are strongly influenced by<br />

planetary boundary layer air masses, do not show<br />

any long-term trend. <strong>The</strong> trends determined by<br />

least-mean-square fits of the scattering and backscattering<br />

coefficients, the hemispheric backscattering<br />

fractions, and the scattering exponent are<br />

significant, and the number of years necessary<br />

to detect them is shorter than 10 years. For these<br />

variables, the trends and the slopes estimated by<br />

the seasonal Kendall test are therefore confirmed<br />

by the least-mean- square fit results.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND13, JUL 13 ARTN: D13213.


42<br />

08.1-17<br />

Atmospheric blocking: space-time links to the<br />

NAO and PNA<br />

Croci Maspoli M, Schwierz C, Davies H C<br />

Switzerland<br />

Meteorology & Atmospheric Sciences ,<br />

Oceanography<br />

In the Northern hemisphere, regions characterized<br />

by an enhanced frequency of atmospheric<br />

blocking overlap significantly with those associated<br />

with the major extra-tropical patterns of largescale<br />

climate variability-namely the North Atlantic<br />

Oscillation (NAO) and the Pacific North American<br />

(PNA) pattern. <strong>The</strong>re is likewise an overlap in the<br />

temporal band-width of blocks and these-climate<br />

patterns. Here the nature of the linkage between<br />

blocks and the climate patterns is explored by using<br />

the ERA-40 re-analysis data set to examine (1)<br />

their temporal and spatial correlation and (2) the<br />

interrelationship between blocks and the NAO/<br />

PNA. It is shown that a strong anti-correlation exists<br />

between blocking occurrence and the phase<br />

of the NAO (PNA) in the North Atlantic (western<br />

North Pacific), and that there are distinctive interbasin<br />

differences with a clear geographical (over<br />

North Atlantic) and quantitative (over North Pacific)<br />

separation of typical blocking genesis/lysis<br />

regions during the opposing phases of the climate<br />

patterns. An Empirical Orthogonal Function (EOF)<br />

analysis points to a significant influence of blocking<br />

upon the NAO pattern (identifiable as the<br />

leading EOF in the Euro- Atlantic), and a temporal<br />

analysis indicates that long-lasting blocks are associated<br />

with the development of negative NAO/<br />

PNA index values throughout their life-time. In<br />

addition an indication of a cause-and effect relationship<br />

is set-out for the North Atlantic linkage.<br />

Climate Dynamics, 2007, V29, N7-8, DEC, pp<br />

713-725.<br />

08.1-18<br />

FinROSE - middle atmospheric chemistry transport<br />

model<br />

Damski J, Thlix L, Backman L, Taalas P, Kulmala M<br />

Finland, Switzerland<br />

Meteorology & Atmospheric Sciences , Modelling<br />

In this paper we describe the development and<br />

performance of a three- dimensional global middle<br />

atmospheric chemistry transport model Fin<br />

ROSE. <strong>The</strong> FinROSE chemistry transport model<br />

includes a numerical scheme for stratospheric<br />

chemistry with parameterizations for heterogeneous<br />

processing on polar stratospheric clouds<br />

(PSC) and on liquid binary aerosols together with<br />

a parameterisation of large nitric acid trihydrate<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

particles (i.e. NAT-rocks) and PSC sedimentation.<br />

<strong>The</strong> total number of trace species in the model is<br />

34 and the total number of gas-phase reactions,<br />

photodissociation processes and heterogeneous<br />

reactions is about 150. <strong>The</strong> model is forced by external<br />

wind and temperature fields. <strong>The</strong> simulations<br />

are normally performed in a 5 degrees x 10<br />

degrees (lat. x long.) grid from the surface up to<br />

around 0.1 hPa, with a vertical resolution of ca.<br />

1.5 km in the stratosphere. Long-term simulations<br />

(40 to 50 years) have been done using winds and<br />

temperatures from ECMWF ERA40 analyses. <strong>The</strong><br />

performance of the model in describing the stratospheric<br />

composition and chemistry is shown and<br />

evaluated in this paper. In general, the FinROSE<br />

results show a good comparison with measured<br />

total ozone. Also the timing, the depth and the<br />

deepening of the Antarctic ozone hole, and the<br />

responsible processes are captured well in the<br />

model simulations.<br />

Boreal Environment Research, 2007, V12, N5, OCT<br />

24, pp 535-550.<br />

08.1-19<br />

Doubled length of western European summer<br />

heat waves since 1880<br />

Della Marta P M, Haylock M R, Luterbacher J,<br />

Wanner H<br />

Switzerland, Australia, England<br />

Meteorology & Atmospheric Sciences<br />

(1) We analyzed a new data set of 54 high-quality<br />

homogenized daily maximum temperature series<br />

from western Europe (Austria, Belgium, Croatia,<br />

Czech Republic, Denmark, Finland, France, Germany,<br />

Ireland, Netherlands, Portugal, Spain, Sweden,<br />

Switzerland, United Kingdom) to define more<br />

accurately the change in extreme warm Daily<br />

Summer Maximum Temperature (DSMT). Results<br />

from the daily temperature homogeneity analysis<br />

suggest that many instrumental measurements in<br />

the late 19th and early 20th centuries were warm-<br />

biased. Correcting for these biases, over the period<br />

1880 to 2005 the length of summer heat waves over<br />

western Europe has doubled and the frequency of<br />

hot days has almost tripled. <strong>The</strong> DSMT Probability<br />

Density Function (PDF) shows significant changes<br />

in the mean (+ 1.6 +/- 0.4 degrees C) and variance<br />

(+ 6 +/- 2%). <strong>The</strong>se conclusions help further the evidence<br />

that western Europe’s climate has become<br />

more extreme than previously thought and that<br />

the hypothesized increase in variance of future<br />

summer temperature has indeed been a reality<br />

over the last 126 years.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND15, AUG 3 ARTN: D15103.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 43<br />

08.1-20<br />

Summer heat waves over western Europe<br />

1880-2003, their relationship to large-scale<br />

forcings and predictability<br />

Della Marta P M, Luterbacher J, von Weissenfluh H,<br />

Xoplaki E, Brunet M, Wanner H<br />

Switzerland, Australia, Spain<br />

Meteorology & Atmospheric Sciences<br />

We investigate the large-scale forcing and teleconnections<br />

between atmospheric circulation<br />

(sea level pressure, SLP), sea surface temperatures<br />

(SSTs), precipitation and heat wave events over<br />

western Europe using a new dataset of 54 daily<br />

maximum temperature time series. Forty four of<br />

these time series have been homogenised at the<br />

daily timescale to ensure that the presence of<br />

inhomogeneities has been minimised. <strong>The</strong> daily<br />

data have been used to create a seasonal index of<br />

the number of heat waves. Using canonical correlation<br />

analysis (CCA), heat waves over western<br />

Europe are shown to be related to anomalous high<br />

pressure over Scandinavia and central western Europe.<br />

Other forcing factors such as Atlantic SSTs<br />

and European precipitation, the later as a proxy<br />

for soil moisture, a known factor in strengthening<br />

land-atmosphere feedback processes, are also<br />

important. <strong>The</strong> strength of the relationship between<br />

summer SLP anomalies and heat waves is<br />

improved (from 35%) to account for around 46%<br />

of its variability when summer Atlantic and Mediterranean<br />

SSTs and summer European precipitation<br />

anomalies are included as predictors. This<br />

indicates that these predictors are not completely<br />

collinear rather that they each have some contribution<br />

to accounting for summer heat wave variability.<br />

However, the simplicity and scale of the<br />

statistical analysis masks this complex interaction<br />

between variables. <strong>The</strong>re is some useful predictive<br />

skill of summer heat waves using multiple lagged<br />

predictors. A CCA using preceding winter North<br />

Atlantic SSTs and preceding January to May Mediterranean<br />

total precipitation results in significant<br />

hindcast (1972-2003) Spearman rank correlation<br />

skill scores up to 0.55 with an average skill score<br />

over the domain equal to 0.28 +/- 0.28. In agreement<br />

with previous studies focused on mean<br />

summer temperature, there appears to be some<br />

predictability of heat wave events on the decadal<br />

scale from the Atlantic Multidecadal Oscillation<br />

(AMO), although the long-term global mean temperature<br />

is also well related to western European<br />

heat waves. Combining these results with the observed<br />

positive trends in summer continental European<br />

SLP, North Atlantic SSTs and indications of<br />

a decline in European summer precipitation then<br />

possibly these long-term changes are also related<br />

to increased heat wave occurrence and it is important<br />

that the physical processes controlling these<br />

changes be more fully understood.<br />

Climate Dynamics, 2007, V29, N2-3, AUG, pp<br />

251-275.<br />

08.1-21<br />

Effects of convective ice lofting on H 2O and<br />

HDO in the tropical tropopause layer<br />

Dessler A E, Hanisco T F, Füglistaler S<br />

USA, Switzerland, England<br />

Meteorology & Atmospheric Sciences , Modelling<br />

We have added convective ice lofting to a Lagrangian<br />

trajectory model of tropical tropopause layer<br />

(TTL) water vapor (H 2O) and its stable isotopologue,<br />

HDO. <strong>The</strong> Lagrangian model has been previously<br />

shown to accurately simulate H 2O in the TTL and<br />

lower stratosphere. We show here that the model<br />

does a poor job reproducing the observed HDO<br />

depletion (delta D) in the TTL. When convective<br />

ice lofting to altitudes below the cold point (the<br />

point where air experiences its lowest H 2O saturation<br />

mixing ratio) is added to the model, there is<br />

little change in H 2O in the lower stratosphere, but<br />

a large change in delta D throughout the TTL that<br />

brings the model into better agreement with measurements.<br />

Thus convective ice lofting has the capacity<br />

to improve the model’s delta D simulation<br />

while not significantly degrading the agreement<br />

between simulated and measured H 2O. Convective<br />

ice lofting to altitudes above the cold point,<br />

on the other hand, has a large effect on lower<br />

stratospheric H 2O, suggesting that changes in<br />

convection reaching these altitudes could drive<br />

changes in lower stratospheric H 2O. This suggests<br />

a mechanism by which lower stratospheric H 2O<br />

trends may be at least partially decoupled from<br />

tropopause temperature trends. Such a disconnection<br />

was suggested by previous observations of<br />

simultaneously increasing stratospheric H 2O and<br />

a cooling tropical tropopause.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND18, SEP 26 ARTN: D18309.<br />

08.1-22<br />

Some factors in the design of a regional<br />

prediction model: an examination based upon<br />

two MAP events<br />

Didone M, Lüthi D, Davies H C<br />

Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

Consideration is given to the impact of both<br />

synoptic-scale flow features and different model<br />

configurations upon the performance of an<br />

Alpine-encompassing regional NWP model. <strong>The</strong><br />

so-called regional LM forecast model is used to


44<br />

simulate two events selected from the Mesoscale<br />

Alpine Programme (MAP), and simulations are<br />

undertaken with: different domain sizes (at 7 km<br />

resolution); lateral boundary data supplied from<br />

two data sets (the ECMWF’s operational and MAP<br />

Reanalysis fields); and an embedded domain (at 2<br />

km resolution). Quantitative evidence is provided<br />

showing (a) the specification of the incident and<br />

evolving synoptic-scale flow can exert a major<br />

impact upon the quality of the resulting simulations;<br />

(b) the simulation of the low-level meso-a<br />

scale features of the flow is helped considerably<br />

by the refined MAP Reanalysis data set; and (c) the<br />

simulated meso-beta scale precipitation distribution<br />

displays some skill but, at least for one of the<br />

two cases, major deficiencies are not offset by the<br />

use of Reanalysis data.<br />

Meteorologische Zeitschrift, 2007, V16, N3, pp<br />

261-273.<br />

08.1-23<br />

Föhn in the Rhine Valley during MAP: A review<br />

of its multiscale dynamics in complex valley<br />

geometry<br />

Drobinski P, Steinacker R, Richner H, Baumann<br />

Stanzer K, Beffrey G, Benech B, Berger H, Chimani<br />

B, Dabas A, Dorninger M, Dürr B, Flamant<br />

C, Frioud M, Furger M, Gröhn I, Gubser S, Gutermann<br />

T, Häberli C, Häller Scharnhorst E, Ratheiser<br />

G, Ruffieux D, Seiz G, Spatzierer M, Tschannett S,<br />

Vogt S, Werner R, Zängl G<br />

France, Austria, Switzerland, Germany<br />

Meteorology & Atmospheric Sciences<br />

This paper summarizes the findings of seven years<br />

of research on fohn conducted within the project<br />

‘Fohn in the Rhine Valley during MAP’ (FORM) of<br />

the Mesoscale Alpine Programme (MAP). It starts<br />

with a brief historical review of fohn research in<br />

the Alps, reaching back to the middle of the 19th<br />

century. Afterwards, it provides an overview of the<br />

experimental and numerical challenges identified<br />

before the MAP field experiment and summarizes<br />

the key findings made during MAP in observation,<br />

simulation and theory. We specifically address<br />

the role of the upstream and cross-Alpine flow<br />

structure on fohn at a local scale and the processes<br />

driving fohn propagation in the Rhine Valley.<br />

<strong>The</strong> crucial importance of interactions between<br />

the fohn and cold-air pools frequently filling the<br />

lower Rhine Valley is highlighted. In addition, the<br />

dynamics of a low-level flow splitting occurring<br />

at a valley bifurcation between the Rhine Valley<br />

and the Seez Valley are examined. <strong>The</strong> advances<br />

in numerical modelling and forecasting of fohn<br />

events in the Rhine Valley are also underlined.<br />

Finally, we discuss the main differences between<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

fohn dynamics in the Rhine Valley area and in the<br />

Wipp/Inn Valley region and point out some open<br />

research questions needing further investigation.<br />

Quarterly Journal of the Royal Meteorological Society,<br />

2007, V133, N625, B, APR, pp 897-916.<br />

08.1-24<br />

Multimodel projections of stratospheric ozone<br />

in the 21st century<br />

Eyring V, Waugh D W, Bodeker G E, Cordero E, Akiyoshi<br />

H, Austin J, Beagley S R, Boville B A, Braesicke<br />

P, Brühl C, Butchart N, Chipperfield M P, Dameris<br />

M, Deckert R, Deushi M, Frith S M, Garcia R R,<br />

Gettelman A, Giorgetta M A, Kinnison D E, Mancini<br />

E, Manzini E, Marsh D R, Matthes S, Nagashima<br />

T, Newman P A, Nielsen J E, Pawson S, Pitari G,<br />

Plummer D A, Rozanov E, Schraner M, Scinocca J<br />

F, Semeniuk K, Shepherd T G, Shibata K, Steil B,<br />

Stolarski R S, Tian W, Yoshiki M<br />

Germany, USA, New Zealand, Japan, Canada, England,<br />

Italy, Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

Simulations from eleven coupled chemistry-climate<br />

models (CCMs) employing nearly identical<br />

forcings have been used to project the evolution of<br />

stratospheric ozone throughout the 21st century.<br />

<strong>The</strong> model-to-model agreement in projected temperature<br />

trends is good, and all CCMs predict continued,<br />

global mean cooling of the stratosphere<br />

over the next 5 decades, increasing from around<br />

0.25 K/decade at 50 h Pa to around 1 K/decade at<br />

1 hPa under the Intergovernmental Panel on Climate<br />

<strong>Change</strong> (IPCC) Special Report on Emissions<br />

Scenarios (SRES) A1B scenario. In general, the<br />

simulated ozone evolution is mainly determined<br />

by decreases in halogen concentrations and continued<br />

cooling of the global stratosphere due to<br />

increases in greenhouse gases (GHGs). Column<br />

ozone is projected to increase as stratospheric<br />

halogen concentrations return to 1980s levels. Because<br />

of ozone increases in the middle and upper<br />

stratosphere due to GHG-induced cooling, total<br />

ozone averaged over midlatitudes, outside the polar<br />

regions, and globally, is projected to increase<br />

to 1980 values between 2035 and 2050 and before<br />

lowerstratospheric halogen amounts decrease to<br />

1980 values. In the polar regions the CCMs simulate<br />

small temperature trends in the first and<br />

second half of the 21st century in midwinter. Differences<br />

in stratospheric inorganic chlorine (Cl-y)<br />

among the CCMs are key to diagnosing the intermodel<br />

differences in simulated ozone recovery, in<br />

particular in the Antarctic. It is found that there<br />

are substantial quantitative differences in the<br />

simulated Cly, with the October mean Antarctic<br />

Cly peak value varying from less than 2 ppb to


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 45<br />

over 3.5 ppb in the CCMs, and the date at which<br />

the Cly returns to 1980 values varying from before<br />

2030 to after 2050. <strong>The</strong>re is a similar variation in<br />

the timing of recovery of Antarctic springtime column<br />

ozone back to 1980 values. As most models<br />

underestimate peak Cly near 2000, ozone recovery<br />

in the Antarctic could occur even later, between<br />

2060 and 2070. In the Arctic the column ozone increase<br />

in spring does not follow halogen decreases<br />

as closely as in the Antarctic, reaching 1980 values<br />

before Arctic halogen amounts decrease to<br />

1980 values and before the Antarctic. None of the<br />

CCMs predict future large decreases in the Arctic<br />

column ozone. By 2100, total column ozone is projected<br />

to be substantially above 1980 values in all<br />

regions except in the tropics.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND16, AUG 21 ARTN: D16303.<br />

08.1-25<br />

Middle atmosphere water vapour and dynamical<br />

features in aircraft measurements and<br />

ECMWF analyses<br />

Feist D G, Geer A J, Müller S, Kämpfer N<br />

Switzerland, England, Germany<br />

Meteorology & Atmospheric Sciences<br />

<strong>The</strong> European Centre for Medium-Range Weather<br />

Forecasts (ECMWF) provides global analyses of atmospheric<br />

humidity from the ground to the lower mesosphere.<br />

Unlike in the troposphere, in the stratosphere<br />

no humidity observations are assimilated.<br />

Humidity analyses here are essentially the results of<br />

a free-running model constrained by the ECMWF’s<br />

analysed wind fields. So far only the broad-scale<br />

features of the resulting stratospheric water vapour<br />

distribution have been validated. This study provides<br />

the first in-depth comparison of stratospheric<br />

humidity from ECMWF with observations from an<br />

airborne microwave radiometer that has measured<br />

the distribution of stratospheric water vapour over<br />

an altitude range of roughly 15-60 km on several<br />

flight campaigns since 1998. <strong>The</strong> aircraft measurements<br />

provide a horizontal resolution that cannot<br />

be achieved by current satellite instruments. This<br />

study examines dynamical features in the moisture<br />

fields such as filamentation and the vortex edge,<br />

finding that features in the ERA-40 humidity analyses<br />

often do correspond to real atmospheric events<br />

that are seen in the aircraft measurements. However,<br />

the comparisons also show that in general the<br />

ECMWF model produces an unrealistically moist<br />

mesosphere. As a result it cannot replicate the descent<br />

of relatively dry mesospheric air into the polar<br />

vortex in winter and spring.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N20, pp 5291-5307.<br />

08.1-26<br />

An improved low-flow thermodenuder<br />

Fierz M, Vernooij M G C, Burtscher H<br />

Switzerland<br />

Meteorology & Atmospheric Sciences<br />

<strong>The</strong>rmodenuders are used to remove the volatile<br />

fraction of an aerosol. All designs until now<br />

have a cooled adsorption section where the volatile<br />

material is trapped, but theoretical considerations<br />

suggest that the adsorption section should<br />

be heated. <strong>The</strong>refore, we built a thermodenuder<br />

with a heated adsorption section. We tested its<br />

performance with respect to particle penetration<br />

and its ability to remove DEHS coated onto NaCl<br />

nuclei. <strong>The</strong> measured losses are lower than in previously<br />

published designs and the DEHS removal<br />

appears to be satisfactory. Additionally, the new<br />

thermodenuder is practical for field use thanks to<br />

its small size. It should therefore be a good alternative<br />

to previous designs.<br />

Journal of Aerosol Science, 2007, V38, N11, NOV,<br />

pp 1163-1168.<br />

08.1-27<br />

Dynamics of orographically triggered banded<br />

convection in sheared moist orographic flows<br />

Fuhrer O, Schär C<br />

Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

Shallow orographic convection embedded in an<br />

unstable cap cloud can organize into convective<br />

bands. Previous research has highlighted the<br />

important role of small-amplitude topographic<br />

variations in triggering and organizing banded<br />

convection. Here, the underlying dynamical<br />

mechanisms are systematically investigated by<br />

conducting three-dimensional simulations of<br />

moist flows past a two-dimensional mountain<br />

ridge using a cloud-resolving numerical model.<br />

Most simulations address a sheared environment<br />

to account for the observed wind profiles. Results<br />

confirm that small-amplitude topographic variations<br />

can enhance the development of embedded<br />

convection and anchor quasi-stationary convective<br />

bands to a fixed location in space. <strong>The</strong> resulting<br />

precipitation patterns exhibit tremendous<br />

spatial variability, since regions receiving heavy<br />

rainfall can be only kilometers away from regions<br />

receiving little or no rain. In addition, the presence<br />

of banded convection has important repercussions<br />

on the area-mean precipitation amounts.<br />

For the experimental setup here, the gravity wave<br />

response to small-amplitude topographic variations<br />

close to the upstream edge of the cap cloud<br />

(which is forced by the larger-scale topography)<br />

is found to be the dominant triggering mecha-


46<br />

nism. Small-scale variations in the underlying<br />

topography are found to force the location and<br />

spacing of convective bands over a wide range of<br />

scales. Further, a self- sufficient mode of unsteady<br />

banded convection is investigated that does not<br />

dependent on external perturbations and is able<br />

to propagate against the mean flow. Finally, the<br />

sensitivity of model simulations of banded convection<br />

with respect to horizontal computational<br />

resolution is investigated. Consistent with predictions<br />

from a linear stability analysis, convective<br />

bands of increasingly smaller scales are favored<br />

as the horizontal resolution is increased. However,<br />

small-amplitude topographic roughness is<br />

found to trigger banded convection and to control<br />

the spacing and location of the resulting bands.<br />

<strong>The</strong>reby, the robustness of numerical simulations<br />

with respect to an increase in horizontal resolution<br />

is increased in the presence of topographic<br />

variations.<br />

Journal of the Atmospheric Sciences, 2007, V64,<br />

N10, OCT, pp 3542-3561.<br />

08.1-28<br />

A satellite- and model-based assessment of<br />

the 2003 Russian fires: Impact on the Arctic<br />

region<br />

Generoso S, Bey I, Attie J L, Breon F M<br />

Switzerland, France<br />

Modelling , Meteorology & Atmospheric Sciences<br />

(1) In this paper, we address the issues of the representation<br />

of boreal fires in a global chemistry and<br />

transport model (GEOS-Chem) as well as their contribution<br />

to the Arctic aerosol optical thickness<br />

and black carbon (BC) deposition, with a focus on<br />

the 2003 Russian fires. We use satellite observations<br />

from the MOPITT, POLDER and MODIS sensors<br />

to evaluate the model performances in simulating<br />

the fire pollution export over the North<br />

Pacific. Our results show that aerosol and carbon<br />

monoxide (CO) outflow is best reproduced in our<br />

model when fire emissions are (1) increased to 72<br />

Tg for CO, 0.5 Tg C for BC, and 5.3 Tg C for organic<br />

carbon over the entire fire season; (2) prescribed<br />

on a daily basis; and (3) injected up to 4.5 km in<br />

July and August. <strong>The</strong> use of daily, rather than<br />

monthly, biomass burning emission inventories<br />

improves significantly the representation of the<br />

aerosol outflow, but has little impact on CO. <strong>The</strong><br />

injection of fire emissions above the boundary<br />

layer influences both the CO and aerosol columns<br />

but only during the late fire season. <strong>The</strong> model improvements<br />

with respect to the standard configuration<br />

induce an increase of a factor up to 2 on<br />

the aerosol optical thickness and the mass of BC<br />

deposited in the Northern Hemisphere. Accord-<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

ing to our improved simulation, the 2003 Russian<br />

fires contributed to 16-33% of the aerosol optical<br />

thickness and to 40-56% of the mass of BC deposited,<br />

north of 75 degrees N in spring and summer.<br />

<strong>The</strong>y contribute to the aerosol optical thickness<br />

by more than 30% during the days of Arctic haze<br />

events in spring and summer.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND15, AUG 2 ARTN: D15302.<br />

08.1-29<br />

GEM/POPs: a global 3-D dynamic model for<br />

semi-volatile persistent organic pollutants -<br />

Part 1: Model description and evaluations of<br />

air concentrations<br />

Gong S L, Huang P, Zhao T L, Sahsuvar L, Barrie L<br />

A, Kaminski J W, Li Y F, Niu T<br />

Canada, Switzerland, Peoples R China<br />

Modelling , Meteorology & Atmospheric Sciences<br />

GEM/POPs was developed to simulate the transport,<br />

deposition and partitioning of semi-volatile<br />

persistent organic pollutants (POPs) in the atmosphere<br />

within the framework of Canadian weather<br />

forecasting model GEM. In addition to the general<br />

processes such as anthropogenic emissions, atmosphere/water<br />

and atmosphere/soil exchanges,<br />

GEM/POPs incorporates a dynamic aerosol module<br />

to provide the aerosol surface areas for the<br />

semi-volatile POPs to partition between gaseous<br />

and particle phases and a mechanism for particlebound<br />

POPs to be removed. Simulation results<br />

of three PCBs (28, 153 and 180) for the year 2000<br />

indicate that the model captured the main features<br />

of global atmospheric PCBs when compared<br />

with observations from EMEP, IADN and Alert stations.<br />

<strong>The</strong> annual averaged concentrations and<br />

the fractionation of the three PCBs as a function<br />

of latitudes agreed reasonably well with observations.<br />

<strong>The</strong> impacts of atmospheric aerosols on the<br />

transports and partitioning of the three PCBs are<br />

reasonably simulated. <strong>The</strong> ratio of particulate to<br />

gaseous PCBs in the atmospheric column ranges<br />

from less than 0.1 for PCB28 to as high as 100 for<br />

PCB180, increasing from the warm lower latitudes<br />

to the cold high latitudes. Application of GEM/<br />

POPs in a study of the global transports and budgets<br />

of various PCBs accompanies this paper.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N15, pp 4001-4013.<br />

08.1-30<br />

A global model study of ozone enhancement<br />

during the August 2003 heat wave in Europe<br />

Guerova G, Jones N<br />

Australia, Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 47<br />

<strong>The</strong> European summer of 2003 was characterised<br />

by intense heat, prolonged isolation and suppressed<br />

ventilation of the boundary layer which,<br />

combined with large anthropogenic emissions<br />

and strong fires, resulted in a build up of an unprecedentedly<br />

high and long-lasting photochemical<br />

smog over large parts of the continent. In this<br />

work, a global chemistry and transport model<br />

GEOS-Chern is compared with surface O-3 concentrations<br />

observed in 2003 in order to examine<br />

the extent to which the model is capable of reproducing<br />

such an extreme event. <strong>The</strong> GEOS-Chem<br />

reproduces the temporal variation of O-3 at the<br />

Jungfraujoch mountain site, Switzerland, including<br />

the enhanced concentrations associated with<br />

the August 2003 heat wave (r = 0.84). <strong>The</strong> spatial<br />

distribution of the enhanced surface O-3 over<br />

Spain, France, Germany and Italy is also captured<br />

to some extent (r = 0.63), although the largest concentrations<br />

appear to be located over the Italian<br />

Peninsula in the model rather than over Central<br />

Europe as suggested by the surface O-3 observations.<br />

In general, the observed differences between<br />

the European averaged O-3 concentrations<br />

in the summer of 2003 to those in 2004 are larger<br />

in the observations than in the model, as the<br />

model reproduces relatively well the enhanced<br />

levels in 2003 but overestimates those observed in<br />

2004. Preliminary contributions of various sources<br />

to the O-3 surface concentrations over Europe<br />

during the heat wave indicate that anthropogenic<br />

emissions from Europe contribute the most to the<br />

O-3 build up near the surface (40 to 50%, i.e. 30<br />

ppb). <strong>The</strong> contribution from anthropogenic emissions<br />

from the other major source regions of the<br />

northern hemisphere, in particular North America,<br />

tends to be smaller than those of other years.<br />

<strong>The</strong> model indicates that the large fires that occurred<br />

in that year contributed up to 5% (3 ppb) to<br />

surface O-3 in close proximity to the fire regions<br />

and less elsewhere in Europe. Biogenic volatile<br />

organic compounds (VOCs) emitted by grass and<br />

forest areas contributed up to 10% (5-6 ppb) of surface<br />

O-3 over France, Germany and northern Italy,<br />

which represents a contribution that is twice as<br />

large than that found in 2004. <strong>The</strong>se results in<br />

terms of contributions from various sources, particularly<br />

biogenic emissions, should be seen as<br />

preliminary, as the response of vegetation to such<br />

extreme events may not be well represented in<br />

the model.<br />

Environmental Chemistry, 2007, V4, N5, pp<br />

285-292.<br />

08.1-31<br />

Velocity and temperature derivatives in high-<br />

Reynolds-number turbulent flows in the atmospheric<br />

surface layer. Part 1. Facilities, methods<br />

and some general results<br />

Gulitski G, Kholmyansky M, Kinzelbach W, Lüthi B,<br />

Tsinober A, Yorish S<br />

Israel, Switzerland<br />

Meteorology & Atmospheric Sciences , Oceanography<br />

, Geochemistry & Geophysics<br />

This is a report on a field experiment in an atmospheric<br />

surface layer at heights between 0.8 and<br />

10m with the Taylor micro-scale Reynolds number<br />

in the range Re-lambda = 1.6 - 6.6 x 10(3). Explicit<br />

information is obtained on the full set of velocity<br />

and temperature derivatives both spatial and<br />

temporal, i.e. no use of Taylor hypothesis is made.<br />

<strong>The</strong> report consists of three parts. Part I is devoted<br />

to the description of facilities, methods and<br />

some general results. Certain results are similar<br />

to those reported before and give us confidence in<br />

both old and new data, since this is the first repetition<br />

of this kind of experiment at better data<br />

quality. Other results were not obtained before,<br />

the typical example being the so- called tear-drop<br />

R - Q plot and several others. Part 2 concerns accelerations<br />

and related matters. Part 3 is devoted to<br />

issues concerning temperature, with the emphasis<br />

on joint statistics of temperature and velocity<br />

derivatives. <strong>The</strong> results obtained in this work are<br />

similar to those obtained in experiments in laboratory<br />

turbulent grid flow and in direct numerical<br />

simulations of Navier- Stokes equations at much<br />

smaller Reynolds numbers Re-lambda similar to<br />

10(2), and this similarity is not only qualitative,<br />

but to a large extent quantitative. This is true of<br />

such basic processes as enstrophy and strain production,<br />

geometrical statistics, the role of concentrated<br />

vorticity and strain, reduction of nonlinearity<br />

and non- local effects. <strong>The</strong> present experiments<br />

went far beyond the previous ones in two main<br />

respects. (i) All the data were obtained without<br />

invoking the Taylor hypothesis, and therefore a<br />

variety of results on fluid particle accelerations<br />

became possible. (ii) Simultaneous measurements<br />

of temperature and its gradients with the emphasis<br />

on joint statistics of temperature and velocity<br />

derivatives. <strong>The</strong>se are reported in Parts 2 and 3.<br />

Journal of Fluid Mechanics, 2007, V589, OCT 25,<br />

pp 57-81.


48<br />

08.1-32<br />

Velocity and temperature derivatives in high-<br />

Reynolds-number turbulent flows in the atmospheric<br />

surface layer. Part 2. Accelerations and<br />

related matters<br />

Gulitski G, Kholmyansky M, Kinzelbach W, Lüthi B,<br />

Tsinober A, Yorish S<br />

Israel, Switzerland<br />

Oceanography , Meteorology & Atmospheric<br />

Sciences , Geochemistry & Geophysics<br />

We report the first results of an experiment, in<br />

which explicit information on all velocity derivatives<br />

(the nine spatial derivatives, partial derivative<br />

u(i)/partial derivative x(j), and the three temporal<br />

derivatives, partial derivative u(i)/partial derivative<br />

t) along with the three components of velocity<br />

fluctuations at a Reynolds number as high as Relambda<br />

similar to 10 (4) is obtained. No use of the<br />

Taylor hypothesis was made, and this allowed us<br />

to obtain a variety of results concerning acceleration<br />

and its different Eulerian components along<br />

with vorticity, strain and other small-scale quantities.<br />

<strong>The</strong> field experiments were performed at five<br />

heights between 0.8 and 10 in above the ground.<br />

<strong>The</strong> report consists of three parts. Part 1 is devoted<br />

to the description of facilities, methods and some<br />

general results. Part 2 concerns accelerations and<br />

related matters. Part 3 is devoted to the issues concerning<br />

temperature with the emphasis on joint<br />

statistics of temperature and velocity derivatives.<br />

Journal of Fluid Mechanics, 2007, V589, OCT 25,<br />

pp 83-102.<br />

08.1-33<br />

Velocity and temperature derivatives in<br />

high-Reynolds-number turbulent flows in the<br />

atmospheric surface layer. Part 3. Temperature<br />

and joint statistics of temperature and velocity<br />

derivatives<br />

Gulitski G, Kholmyansky M, Kinzelbach W, Lüthi B,<br />

Tsinober A, Yorish S<br />

Israel, Switzerland<br />

Meteorology & Atmospheric Sciences , Oceanography<br />

, Geochemistry & Geophysics<br />

This is part 3 of our work describing experiments<br />

in which explicit information was obtained on<br />

all the derivatives, i.e. spatial derivatives, partial<br />

derivative/partial derivative x(j), and temporal<br />

derivatives, partial derivative/partial derivative<br />

t, of velocity and temperature fields (and all the<br />

components of velocity fluctuations and temperature)<br />

at the Reynolds number Re-lambda similar<br />

to 10(4). This part is devoted to the issues concerning<br />

temperature with the emphasis on joint statistics<br />

of temperature and velocity derivatives, based<br />

on preliminary results from a jet facility and the<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

main results from a field experiment. Apart from<br />

a number of conventional results, these contain a<br />

variety of results concerning production of temperature<br />

gradients, such as role of vorticity and<br />

strain, eigen- contributions, geometrical statistics<br />

such as alignments of the temperature gradient<br />

and the eigenframe of the rate-of-strain tensor,<br />

tilting of the temperature gradient, comparison<br />

of the true production of the temperature gradient<br />

with its surrogate. Among the specific results<br />

of importance is the essential difference in the behaviour<br />

of the production of temperature gradients<br />

in regions dominated by vorticity and strain.<br />

Namely, the production of temperature gradients<br />

is much more intensive in regions dominated by<br />

strain, whereas production of temperature gradients<br />

is practically independent of the magnitude<br />

of vorticity. In contrast, vorticity and strain are<br />

contributing equally to the tilting of the vector of<br />

temperature gradients. <strong>The</strong> production of temperature<br />

gradients is mainly due to the fluctuative<br />

strain, the terms associated with mean fields are<br />

unimportant. It was checked directly (by looking<br />

at corresponding eigen-contributions and alignments),<br />

that the production of the temperature<br />

gradients is due to predominant compressing of<br />

fluid elements rather than stretching, which is<br />

true of other processes in turbulent flows, e.g. turbulent<br />

energy production in shear flows. Though<br />

the production of the temperature gradient and<br />

its surrogate possess similar univariate PDFs<br />

(which indicates the tendency to isotropy in small<br />

scales by this particular criterion), their joint PDF<br />

is not close to a bisector. This means that the true<br />

production of the temperature gradient is far<br />

from being fully represented by its surrogate. <strong>The</strong><br />

main technical achievement is demonstrating the<br />

possibility of obtaining experimentally Joint statistics<br />

of velocity and temperature gradients.<br />

Journal of Fluid Mechanics, 2007, V589, OCT 25,<br />

pp 103-123.<br />

08.1-34<br />

Comparison and synergy of stratospheric<br />

ozone measurements by satellite limb sounders<br />

and the ground-based microwave radiometer<br />

SOMORA<br />

Hocke K, Kämpfer N, Ruffieux D, Froidevaux L, Parrish<br />

A, Boyd I, von Clarmann T, Steck T, Timofeyev Y<br />

M, Polyakov A V, Kyrola E<br />

Switzerland, USA, Germany, Russia, Finland<br />

Meteorology & Atmospheric Sciences<br />

Stratospheric O-3 profiles obtained by the satellite<br />

limb sounders Aura/MLS, ENVISAT/ MIPAS,<br />

ENVISAT/ GOMOS, SAGE-II, SAGE-III, UARS /HALOE<br />

are compared to coincident O-3 profiles of the


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 49<br />

ground-based microwave radiometer SOMORA in<br />

Switzerland. Data from the various measurement<br />

techniques are within 10% at altitudes below 45<br />

km. At altitudes 45-60 km, the relative O-3 differences<br />

are within a range of 50%. Larger deviations<br />

at upper altitudes are attributed to larger relative<br />

measurement errors caused by lower O-3 concentrations.<br />

<strong>The</strong> spatiotemporal characteristics of the<br />

O-3 differences (satellite ground station) are investigated<br />

by analyzing about 2300 coincident profile<br />

pairs of Aura/MLS (retrieval version 1.5) and SO-<br />

MORA. <strong>The</strong> probability density function of the O-3<br />

differences is represented by a Gaussian normal<br />

distribution. <strong>The</strong> dependence of the O-3 differences<br />

on the horizontal distance between the sounding<br />

volumes of Aura/MLS and SOMORA is derived.<br />

While the mean bias (Aura/MLS - SOMORA) is constant<br />

with increasing horizontal distance (up to<br />

800 km), the standard deviation of the O-3 differences<br />

increases from around 8 to 11% in the midstratosphere.<br />

Geographical maps yield azimuthal<br />

dependences and horizontal gradients of the O-3<br />

difference field around the SOMORA ground station.<br />

Coherent oscillations of O-3 are present in<br />

the time series of Aura/MLS and SOMORA (e. g.,<br />

due to traveling planetary waves). Ground-and<br />

space-based measurements often complement<br />

one another. We discuss the double differencing<br />

technique which allows both the cross-validation<br />

of two satellites by means of a ground station and<br />

the cross-validation of distant ground stations<br />

by means of one satellite. Temporal atmospheric<br />

noise in the geographical ozone map over Payerne<br />

is significantly reduced by combination of the<br />

data from SOMORA and Aura/MLS. <strong>The</strong>se analyses<br />

illustrate the synergy of ground-based and spacebased<br />

measurements.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N15, pp 4117-4131.<br />

08.1-35<br />

Atmospheric predictability at synoptic versus<br />

cloud-resolving scales<br />

Hohenegger C, Schär C<br />

Switzerland<br />

Meteorology & Atmospheric Sciences<br />

<strong>The</strong> limited atmospheric predictability has been<br />

addressed by the development of ensemble prediction<br />

systems (EPS) that are now routinely applied<br />

for medium-range synoptic-scale numerical<br />

weather prediction (NWP). With the increase of<br />

computational power, interest is growing in the<br />

design of high-resolution (cloud resolving) NWP<br />

models and their associated short-range EPS.<br />

This development raises a series of fundamental<br />

questions, espe cially concerning the type of er-<br />

ror growth and the validity of the tangent-linear<br />

approximation. To address these issues, a comparison<br />

between perturbed medium-range (10<br />

day) synoptic-scale integrations (taken from the<br />

operational ECMWF EPS with a horizontal resolution<br />

of about 80 km) and short-range (1 day) highresolution<br />

simulations (based on the Lokal Modell<br />

of the Consortium for Small-Scale Modeling with<br />

a grid spacing of 2.2 km) is conducted. <strong>The</strong> differences<br />

between the two systems are interpreted in<br />

a nondimensional sense and illustrated with the<br />

help of the Lorenz attractor. Typical asymptotic<br />

perturbation-doubling times of cloud-resolving<br />

and synoptic-scale simulations amount to about<br />

4 and 40 h, respectively, and are primarily related<br />

to convective and baro- clinic instability. Thus,<br />

in terms of growth rates, integrating a 1-day :1<br />

Cloud- re solving forecast may be seen as equivalent<br />

to performing a 10-day synoptic-scale simulation.<br />

However, analysis of the prevailing linearity<br />

reveals that the two systems are fundamentally<br />

different in the following sense: the tangentlinear<br />

approximation breaks down at 1. 5 h for<br />

cloud resolving against 54 h for synoptic-scale<br />

forecasts. In terms of nonlinearity, a 10-day synoptic-scale<br />

integration thus corresponds to a very<br />

short cloud-resolving simulation of merely; about<br />

7 h. <strong>The</strong> higher degree of nonlinearity raises questions<br />

concerning the direct application of standard<br />

synoptic-scale forecasting methodologies<br />

(e.g., optimal perturbations, 4D variational data<br />

assimilation, or targeted observations) to 1-day<br />

cloud-resolving forecasting.<br />

Bulletin of the American Meteorological Society,<br />

2007, V88, N11, NOV, pp 1783-+.<br />

08.1-36<br />

Predictability and error growth dynamics in<br />

cloud-resolving models<br />

Hohenegger C, Schär C<br />

Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

While the benefits of ensemble techniques over<br />

deterministic numerical weather predictions<br />

(NWP) are now widely recognized, the prospects<br />

of ensemble prediction systems (EPS) at high computational<br />

resolution are still largely unclear.<br />

Difficulties arise due to the poor knowledge of<br />

the mechanisms promoting rapid perturbation<br />

growth and propagation, as well as the role of<br />

nonlinearities. In this study, the dynamics associated<br />

with the growth and propagation of initial<br />

uncertainties is investigated by means of real-case<br />

high- resolution (cloud resolving) NWP integrations.<br />

<strong>The</strong> considered case is taken from the Mesoscale<br />

Alpine Programme intensive observing


50<br />

period 3 (MAP IOP3) and involves convection of<br />

intermediate intensity. To assess the underlying<br />

mechanisms and the degree of linearity upon the<br />

predictability of the flow, vastly different initial<br />

perturbation methodologies are compared, while<br />

all simulations use identical lateral boundary<br />

conditions to mimic a perfectly predictable synoptic-scale<br />

flow. Comparison of the perturbation<br />

methodologies indicates that the ensuing patterns<br />

of ensemble spread converge within 11 h,<br />

irrespective of the initial perturbations employed.<br />

All methodologies pinpoint the same meso-betascale<br />

regions of the flow as suffering from predictability<br />

limitations. This result reveals the important<br />

role of nonlinearities. Analysis also shows<br />

that hot spots of error growth can quickly (1-2 h<br />

after initialization) develop far away from the initial<br />

perturbations. This rapid radiation of the initial<br />

uncertainties throughout the computational<br />

domain is due to both sound and gravity waves,<br />

followed by the triggering and/or growth of perturbations<br />

over regions of convective instability.<br />

<strong>The</strong> growth of the uncertainties is then limited by<br />

saturation effects, which in turn are controlled by<br />

the larger-scale atmospheric environment. From<br />

a practical point of view, it is suggested that the<br />

combined effects of rapid propagation, sizeable<br />

amplification, and inherent nonlinearities may<br />

pose severe difficulties for the design of EPS or<br />

data assimilation techniques related to high-resolution<br />

quantitative precipitation forecasting.<br />

Journal of the Atmospheric Sciences, 2007, V64,<br />

N12, DEC, pp 4467-4478.<br />

08.1-37<br />

Upper-tropospheric flow features and the<br />

Alps: An overview<br />

Hoinka K P, Davies H C<br />

Germany, Switzerland<br />

Meteorology & Atmospheric Sciences<br />

One focus of the Mesoscale Alpine Programme<br />

(MAP) was the study of upper-tropospheric potential<br />

vorticity (PV) anomalies that take the form of<br />

narrow meridionally elongated troughs termed<br />

‘PV streamers’. A systematic effort was undertaken<br />

within the MAP framework to: establish a streamer<br />

climatology, develop appropriate instrumentation<br />

and undertake a measurement programme<br />

to better ascertain their structure, study both<br />

their intrinsic dynamics and their modification<br />

by the Alps, and perform model experiments to<br />

examine their significance for numerical weather<br />

prediction. Here an overview is given of the progress<br />

made toward achieving these objectives. In<br />

particular it is shown that PV streamers translating<br />

toward the Alpine region are dynamically<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

distinctive and constitute an identifiable precursor<br />

of and contribute seminally to heavy precipitation<br />

events on the south side of the Alps and<br />

possess rich mesoscale sub-structures that can be<br />

examined with novel water vapour absorption<br />

lidar instrumentation. It is also shown that the<br />

accurate representation of a streamer might well<br />

be a critical prerequisite for accurate quantitative<br />

prediction of mesoscale precipitation.<br />

Quarterly Journal of the Royal Meteorological Society,<br />

2007, V133, N625, B, APR, pp 847-865.<br />

08.1-38<br />

GEM/POPs: a global 3-D dynamic model for<br />

semi-volatile persistent organic pollutants -<br />

Part 2: <strong>Global</strong> transports and budgets of PCBs<br />

Huang P, Gong S L, Zhao T L, Neary L, Barrie L A<br />

Canada, Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

<strong>Global</strong> transports and budgets of three PCBs were<br />

investigated with a 3-D dynamic model for semivolatile<br />

persistent organic pollutants - GEM/POPs.<br />

Dominant pathways were identified for PCB transports<br />

in the atmosphere with a transport flux peaking<br />

below 8 km for gaseous and 14 km for particulate<br />

PCB28, and peaking below 4 km for gaseous<br />

and 6 km for particulate PCB180. <strong>The</strong> inter-continental<br />

transports of PCBs in the Northern Hemisphere<br />

(NH) are dominated in the zonal direction<br />

with their route changes regulated seasonally by<br />

the variation of westerly jet. <strong>The</strong> transport pathways<br />

from Europe and North Atlantic contributed<br />

the most PCBs to the Arctic. Inter-hemispheric<br />

transports of PCBs originated from the regions of<br />

Europe, Asia and North America in three different<br />

flow-paths, accompanying with easterly jet, Asian<br />

monsoon winds and trade winds. PCBs from the<br />

Southern Hemisphere (SH) could also be exported<br />

into the NH. According to the PCB emissions of<br />

year 2000, Europe, North America and Asia are the<br />

three largest sources of the three PCBs, contributing<br />

to the global background concentrations in<br />

the atmosphere, soil and water. <strong>Global</strong>ly, PCB28 in<br />

soil and water has become a comparable source to<br />

the anthropogenic emissions while heavier PCBs<br />

such as PCB153 and 180 are still transporting into<br />

soil and water. For all three congeners, particulate<br />

PCBs are concentrated in the higher levels than<br />

gaseous PCBs. More than half of the particulate<br />

PCB28 could reach up to the stratosphere, while<br />

most of the heavier counter-parts (PCB153 and<br />

PCB180) are stored in the troposphere including<br />

boundary layer with more than 99% gaseous<br />

PCB180 below 6 km.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N15, pp 4015-4025.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 51<br />

08.1-39<br />

Validation of Aura Microwave Limb Sounder<br />

Ozone by ozonesonde and lidar measurements<br />

Jiang Y B, Froidevaux L, Lambert A, Livesey N J,<br />

Read W G, Waters J W, Bojkov B, Leblanc T, Mcdermid<br />

I S, Godin Beekmann S, Filipiak M J, Harwood<br />

R S, Fuller R A, Daffer W H, Drouin B J, Cofield R<br />

E, Cuddy D T, Jarnot R F, Knosp B W, Perun V S,<br />

Schwartz M J, Snyder W V, Stek P C, Thurstans R<br />

P, Wagner P A, Allaart M, Andersen S B, Bodeker<br />

G E, Calpini B, Claude H, Coetzee G, Davies J, de<br />

Backer H, Dier H, Fujiwara M, Johnson B, Kelder H,<br />

Leme N P, Koenig Langlo G, Kyro E, Laneve G, Fook<br />

L S, Merrill J, Morris G, Newchurch M, Oltmans S J,<br />

Parrondos M C, Posny F, Schmidlin F, Skrivankova P,<br />

Stubi R, Tarasick D, Thompson A, Thouret V, Viatte<br />

P, Vomel H, von der Gathen P, Yela M, Zablocki G<br />

USA, France, Scotland, Netherlands, Denmark,<br />

New Zealand, Switzerland, Germany, South Africa,<br />

Canada, Belgium, Japan, Brazil, Finland, Italy, Malaysia,<br />

Spain, Czech Republic, Poland<br />

Meteorology & Atmospheric Sciences , Modelling<br />

(1) We present validation studies of MLS version<br />

2.2 upper tropospheric and stratospheric ozone<br />

profiles using ozonesonde and lidar data as well<br />

as climatological data. Ozone measurements<br />

from over 60 ozonesonde stations worldwide and<br />

three lidar stations are compared with coincident<br />

MLS data. <strong>The</strong> MLS ozone stratospheric data between<br />

150 and 3 hPa agree well with ozonesonde<br />

measurements, within 8% for the global average.<br />

MLS values at 215 hPa are biased high compared<br />

to ozonesondes by similar to 20% at middle to<br />

high latitude, although there is a lot of variability<br />

in this altitude region. Comparisons between<br />

MLS and ground-based lidar measurements from<br />

Mauna Loa, Hawaii, from the Table Mountain<br />

Facility, California, and from the Observatoire<br />

de Haute-Provence, France, give very good agreement,<br />

within similar to 5%, for the stratospheric<br />

values. <strong>The</strong> comparisons between MLS and the<br />

Table Mountain Facility tropospheric ozone lidar<br />

show that MLS data are biased high by similar to<br />

30% at 215 hPa, consistent with that indicated by<br />

the ozonesonde data. We obtain better global average<br />

agreement between MLS and ozonesonde partial<br />

column values down to 215 hPa, although the<br />

average MLS values at low to middle latitudes are<br />

higher than the ozonesonde values by up to a few<br />

percent. MLS v2.2 ozone data agree better than<br />

the MLS v1.5 data with ozonesonde and lidar measurements.<br />

MLS tropical data show the wave one<br />

longitudinal pattern in the upper troposphere,<br />

with similarities to the average distribution from<br />

ozonesondes. High upper tropospheric ozone val-<br />

ues are also observed by MLS in the tropical Pacific<br />

from June to November.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND24, DEC 15 ARTN: D24S34.<br />

08.1-40<br />

<strong>The</strong> impact of reducing the maximum speed<br />

limit on motorways in Switzerland to 80 km<br />

h(-1) on emissions and peak ozone<br />

Keller J, Andreani Aksoyoglu S, Tinguely M, Flemming<br />

J, Heldstab J, Keller M, Zbinden R,<br />

Prevot A S H<br />

Switzerland, England<br />

Urban Studies , Meteorology & Atmospheric<br />

Sciences , Modelling<br />

Hot and dry conditions in summer 2003 led to<br />

ozone levels that substantially exceeded the <strong>Swiss</strong><br />

ambient air quality standard. We investigated how<br />

emissions and ozone levels would have changed<br />

in this period if the maximum speed limit on<br />

<strong>Swiss</strong> motorways were decreased from 120 to 80<br />

km h(-1). <strong>The</strong> air quality model package MM5 /<br />

CAMx was applied to two nested domains, both<br />

including Switzerland. Anthropogenic emissions<br />

were based on various European and <strong>Swiss</strong> data<br />

sources. <strong>The</strong> simulations for the reference case<br />

were based on current driving behaviour. In the<br />

reduction case, nitrogen oxides (NOx) emissions<br />

from road traffic were lower by about 4% with<br />

respect to the current total NOx release. Emissions<br />

of volatile organic compounds (VOC) were<br />

not significantly affected. <strong>The</strong> peak ozone levels<br />

decreased by less than 1%.<br />

Environmental Modelling Software, 2008, V23, N3,<br />

MAR, pp 322-332.<br />

08.1-41<br />

<strong>The</strong> evolution of ERA-40 surface temperatures<br />

and total ozone compared to observed <strong>Swiss</strong><br />

time series<br />

Kunz H, Scherrer S C, Liniger M A, Appenzeller C<br />

Switzerland, USA<br />

Meteorology & Atmospheric Sciences<br />

<strong>The</strong> aim of this paper is to compare long term<br />

changes derived from ERA-40 reanalysis with the<br />

corresponding changes found in carefully homogenized<br />

observational data. Focus is given on two<br />

climate key parameter, daily surface temperature<br />

(T2) and total ozone in the Alpine region for the<br />

period 1961-2000. Overall the two temperature<br />

data sets agree well. <strong>The</strong> reanalysed temperature<br />

trend (0.3 degrees C /decade) is similar to the trend<br />

in raw data but underestimates the trend derived<br />

from homogenized data by 0.1 degrees C/decade.<br />

Differences between ERA-40 and the observations<br />

decrease with time. <strong>The</strong> bias is reduced from +/- 2


52<br />

degrees in the 1960s to +/- 1 degrees in the 1990s.<br />

Differences show a distinct annual cycle. On average<br />

ERA-40 overestimates T2 in summer by 1.0<br />

degrees C and underestimates it by 0.4 degrees<br />

C in winter. A simple downscaling procedure is<br />

applied to compare the temperature values of<br />

single <strong>Swiss</strong> station series with ERA-40 data. <strong>The</strong><br />

technique makes use of a topographic lapse rate<br />

derived from observations. It is shown that the<br />

lapse rate has a distinct seasonal cycle in the Alpine<br />

region. <strong>The</strong> use of this seasonal varying lapse<br />

rate reduces considerably the seasonal bias found<br />

between ERA-40 and the observed series. In contrast<br />

to the temperature data the two ozone data<br />

sets show strong differences between time periods<br />

satellite data has been assimilated or not. In the<br />

episodes where ozone measurements from satellites<br />

are used, basically after 1979, the total ozone<br />

values agree well with ERA-40. <strong>The</strong> reanalysis data<br />

slightly overestimates the observations by 10 DU<br />

(Dobson Units). Before 1973 the error is a little bit<br />

larger with 12 DU, but the lack of satellite data<br />

assimilation in ERA-40 results in an enhanced seasonal<br />

bias with maximum errors in winter (about<br />

20 DU) . <strong>The</strong> strongest differences are found in the<br />

1970s, when radiance from satellite data was assimilated,<br />

but ozone was not. <strong>The</strong>re is a mean bias<br />

of 38 DU with maximum errors in winter of about<br />

70 DU.<br />

Meteorologische Zeitschrift, 2007, V16, N2, pp<br />

171-181.<br />

08.1-42<br />

<strong>Global</strong> model simulations of the impact of<br />

ocean-going ships on aerosols, clouds, and the<br />

radiation budget<br />

Lauer A, Eyring V, Hendricks J, Joeckel P, Lohmann U<br />

Germany, Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

International shipping contributes significantly<br />

to the fuel consumption of all transport related<br />

activities. Specific emissions of pollutants such<br />

as sulfur dioxide (SO 2) per kg of fuel emitted are<br />

higher than for road transport or aviation. Besides<br />

gaseous pollutants, ships also emit various<br />

types of particulate matter. <strong>The</strong> aerosol impacts<br />

the Earth’s radiation budget directly by scattering<br />

and absorbing the solar and thermal radiation<br />

and indirectly by changing cloud properties. Here<br />

we use ECHAM5/MESSy1-MADE, a global climate<br />

model with detailed aerosol and cloud microphysics<br />

to study the climate impacts of international<br />

shipping. <strong>The</strong> simulations show that emissions<br />

from ships significantly increase the cloud droplet<br />

number concentration of low marine water clouds<br />

by up to 5% to 30% depending on the ship emis-<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

sion inventory and the geographic region. Whereas<br />

the cloud liquid water content remains nearly<br />

unchanged in these simulations, effective radii of<br />

cloud droplets decrease, leading to cloud optical<br />

thickness increase of up to 5 - 10%. <strong>The</strong> sensitivity<br />

of the results is estimated by using three different<br />

emission inventories for present-day conditions.<br />

<strong>The</strong> sensitivity analysis reveals that shipping contributes<br />

to 2.3% to 3.6% of the total sulfate burden<br />

and 0.4% to 1.4% to the total black carbon burden<br />

in the year 2000 on the global mean. In addition<br />

to changes in aerosol chemical composition, shipping<br />

increases the aerosol number concentration,<br />

e. g. up to 25% in the size range of the accumulation<br />

mode (typically > 0.1 µm) over the Atlantic.<br />

<strong>The</strong> total aerosol optical thickness over the Indian<br />

Ocean, the Gulf of Mexico and the Northeastern<br />

Pacific increases by up to 8 - 10% depending on<br />

the emission inventory. <strong>Change</strong>s in aerosol optical<br />

thickness caused by shipping induced modification<br />

of aerosol particle number concentration<br />

and chemical composition lead to a change in the<br />

shortwave radiation budget at the top of the atmosphere<br />

(ToA) under clear-sky condition of about -<br />

0.014 W/m(2) to - 0.038 W/m(2) for a global annual<br />

average. <strong>The</strong> corresponding all-sky direct aerosol<br />

forcing ranges between - 0.011 W/m(2) and - 0.013<br />

W/m(2). <strong>The</strong> indirect aerosol effect of ships on climate<br />

is found to be far larger than previously estimated.<br />

An indirect radiative effect of - 0.19 W/m<br />

(2) to - 0.60 W/m(2) (a change in the atmospheric<br />

shortwave radiative flux at ToA) is calculated here,<br />

contributing 17% to 39% of the total indirect effect<br />

of anthropogenic aerosols. This contribution<br />

is high because ship emissions are released in regions<br />

with frequent low marine clouds in an otherwise<br />

clean environment. In addition, the potential<br />

impact of particulate matter on the radiation<br />

budget is larger over the dark ocean surface than<br />

over polluted regions over land.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N19, pp 5061-5079.<br />

08.1-43<br />

Measurements of OVOCs and NMHCs in a<br />

swiss highway tunnel for estimation of road<br />

transport emissions<br />

Legreid G, Reimann S, Steinbacher M, Stähelin J,<br />

Young D, Stemmler K<br />

Switzerland, England<br />

Meteorology & Atmospheric Sciences<br />

Eighteen oxygenated volatile organic compounds<br />

(OVOCs) and eight nonmethane hydrocarbons<br />

(NMHCs) were measured continuously during a<br />

two-week campaign in 2004 in the Gubrist highway<br />

tunnel (Switzerland) . <strong>The</strong> study aimed to es-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 53<br />

timate selected OVOC and NMHC emissions of the<br />

current vehicle fleet under highway conditions.<br />

For the measured OVOCs the highest EFs were<br />

found for ethanol (9.7 mg/km), isopropanol (3.2<br />

mg/km), and acetaldehyde (2.5 mg/km), followed<br />

by acetone, benzaldehyde, and acrolein. Formaldehyde,<br />

the most abundant OVOC measured in<br />

other studies, was not measured by the method applied.<br />

Relative emissions of the measured OVOCs<br />

were estimated to contribute approximately 6 and<br />

4% to the total road traffic VOC emissions from<br />

Switzerland and Europe, respectively. Results are<br />

compared with those from previous studies from<br />

the same tunnel performed in 1993 and 2002, and<br />

from campaigns in other tunnels. A continuous<br />

reduction in the emission factors (EFs) was determined<br />

for all measured compounds from 1993 until<br />

2004. <strong>The</strong> relative contributions of light-duty<br />

vehicles (LDV) and heavy-duty vehicles (HDV) to the<br />

total emissions indicated that OVOCs were mainly<br />

produced by the HDVs, whereas LDVs dominated<br />

the production of the NMHCs.<br />

Environmental Science Technology, 2007, V41,<br />

N20, OCT 15, pp 7060-7066.<br />

08.1-44<br />

A photochemical modeling study of ozone and<br />

formaldehyde generation and budget in the<br />

Po basin<br />

Liu L, Andreani Aksoyoglu S, Keller J, Ordonez C,<br />

Junkermann W, Hak C, Braathen G O, Reimann S,<br />

Astorga Llorens C, Schultz M, Prevot A S H, Isaksen I S A<br />

Norway, Switzerland, France, Germany, Sweden,<br />

Italy<br />

Modelling , Meteorology & Atmospheric Sciences<br />

In this work, a photochemical dispersion model,<br />

CAMx (Comprehensive Air quality Model with<br />

eXtensions) was used to simulate a high ozone<br />

episode observed in the Po basin during the 2003<br />

FORMAT (Formaldehyde as a Tracer of Oxidation<br />

in the Troposphere) campaign. <strong>The</strong> study focuses<br />

on formaldehyde and ozone, and a budget analysis<br />

was set up for interpreting the importance<br />

of different processes, namely emission, chemistry,<br />

transport and deposition, for three different<br />

areas (urban, downwind, suburban) around the<br />

Milan metropolitan region. In addition, a sensitivity<br />

study was carried out based on 11 different<br />

VOC emission scenarios. <strong>The</strong> results of the budget<br />

study show that the strongest O-3 production<br />

rate (4 ppbv/hour) occurs in the downwind area<br />

of the city of Milan, and that accumulated O 3 is<br />

transported back to Milan city during nighttime.<br />

More than 80% of the HCHO concentration over<br />

the Milan metropolitan region is secondary, i.<br />

e., photochemically produced from other VOCs.<br />

<strong>The</strong> sensitivity study shows that the emissions<br />

of isoprene are not, on average, a controlling factor<br />

for the peak concentrations of O 3 and HCHO<br />

over the model domain because of very few oak<br />

trees in this region. Although the paraffinic (PAR)<br />

emissions are fairly large, a 20% reduction of PAR<br />

yields only 1.7% of HCHO reduction and 2.7% reduction<br />

of the O 3 peak. <strong>The</strong> largest reduction of<br />

O 3 levels can be obtained by reduced xylene (XYL)<br />

emissions. A 20% reduction of the total anthropogenic<br />

VOC emissions leads to 15.5% (20.3 ppbv)<br />

reduction of O 3 peak levels over the Milan metropolitan<br />

region.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND22, NOV 20 ARTN: D22303.<br />

08.1-45<br />

Cloud microphysics and aerosol indirect effects<br />

in the global climate model ECHAM5-HAM<br />

Lohmann U, Stier P, Hoose C, Ferrachat S, Kloster S,<br />

Röckner E, Zhang J<br />

Switzerland, USA, Italy, Germany, Canada<br />

Meteorology & Atmospheric Sciences , Modelling<br />

<strong>The</strong> double-moment cloud microphysics scheme<br />

from ECHAM4 that predicts both the mass mixing<br />

ratios and number concentrations of cloud<br />

droplets and ice crystals has been coupled to<br />

the size-resolved aerosol scheme ECHAM5-HAM.<br />

ECHAM5-HAM predicts the aerosol mass, number<br />

concentrations and mixing state. <strong>The</strong> simulated<br />

liquid, ice and total water content and the cloud<br />

droplet and ice crystal number concentrations as<br />

a function of temperature in stratiform mixedphase<br />

clouds between 0 and -35 degrees C agree<br />

much better with aircraft observations in the<br />

ECHAM5 simulations. ECHAM5 performs better<br />

because more realistic aerosol concentrations are<br />

available for cloud droplet nucleation and because<br />

the Bergeron-Findeisen process is parameterized<br />

as being more efficient. <strong>The</strong> total anthropogenic<br />

aerosol effect includes the direct, semi- direct<br />

and indirect effects and is defined as the difference<br />

in the top-of-the-atmosphere net radiation<br />

between present-day and pre- industrial times.<br />

It amounts to & minus; 1.9 W m(-2) in ECHAM5,<br />

when a relative humidity dependent cloud cover<br />

scheme and aerosol emissions representative for<br />

the years 1750 and 2000 from the AeroCom emission<br />

inventory are used. <strong>The</strong> contribution of the<br />

cloud albedo effect amounts to -0.7 W m(-2). <strong>The</strong><br />

total anthropogenic aerosol effect is larger when<br />

either a statistical cloud cover scheme or a different<br />

aerosol emission inventory are employed because<br />

the cloud lifetime effect increases.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N13, pp 3425-3446.


54<br />

08.1-46<br />

A thermophoretic precipitator for the representative<br />

collection of atmospheric ultrafine<br />

particles for microscopic analysis<br />

Lorenzo R, Kägi R, Gehrig R, Scherrer L, Grobety B,<br />

Burtscher H<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , Instruments<br />

& Instrumentation<br />

In this article, the potential of a thermophoretic<br />

sampling device to derive quantitative particle<br />

size distributions and number concentrations of<br />

aerosols based on microscopic single particle analysis<br />

is explored. For that purpose a plate-to-plate<br />

thermophoretic precipitator to collect ultrafine<br />

atmospheric particles for TEM (transmission electron<br />

microscopy) analysis has been calibrated and<br />

characterized. <strong>The</strong> representativeness of the samples<br />

has been verified in a series of experiments.<br />

Results show that, for particles with diameters of<br />

15 nm to 300 nm, the precipitator’s collection efficiency<br />

is independent of size, shape, and composition<br />

of the particles. Hence, its samples accurately<br />

represent the original aerosol. A numerical model<br />

of thermophoretic deposition within the device<br />

has been developed and tailored to the specifications<br />

of the precipitator. <strong>The</strong> model has been used<br />

to derive the particle number density and size<br />

distribution of several calibration aerosols using<br />

the TEM analysis of the samples taken with the<br />

thermophoretic precipitator as input parameters.<br />

<strong>The</strong> results agree very well with the on-line measurements<br />

of the calibration aerosols. This work<br />

demonstrates that our thermophoretic sampling<br />

device can be used to derive quantitative particle<br />

size distributions and number concentrations of<br />

ultrafine particles based on microscopic single<br />

particle analysis.<br />

Aerosol Science and Technology, 2007, V41, N10,<br />

pp 934-943.<br />

08.1-47<br />

Evidence for a modest undercount bias in<br />

early historical Atlantic tropical cyclone counts<br />

Mann M E, Sabbatelli T A, Neu U<br />

USA, Switzerland<br />

Oceanography , Meteorology & Atmospheric<br />

Sciences<br />

We obtain new insights into the reliability of<br />

long-term historical Atlantic tropical cyclone<br />

(‘TC’) counts through the use of a statistical<br />

model that relates variations in annual Atlantic<br />

TC counts to climate state variables. We find<br />

that the existence of a substantial undercount<br />

bias in late 19th through mid 20th century TC<br />

counts is inconsistent with the statistical rela-<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

tionship between TC counts and climate.<br />

Geophysical Research Letters, 2007, V34, N22,<br />

NOV 24 ARTN: L22707.<br />

08.1-48<br />

Efficiency of immersion mode ice nucleation<br />

on surrogates of mineral dust<br />

Marcolli C, Gedamke S, Peter T, Zobrist B<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , Instruments<br />

& Instrumentation<br />

A differential scanning calorimeter (DSC) was<br />

used to explore heterogeneous ice nucleation of<br />

emulsified aqueous suspensions of two Arizona<br />

test dust (ATD) samples with particle diameters of<br />

nominally 0 - 3 and 0 - 7 µm, respectively. Aqueous<br />

suspensions with ATD concentrations of 0.01<br />

- 20 wt% have been investigated. <strong>The</strong> DSC thermograms<br />

exhibit a homogeneous and a heterogeneous<br />

freezing peak whose intensity ratios vary<br />

with the ATD concentration in the aqueous suspensions.<br />

Homogeneous freezing temperatures<br />

are in good agreement with recent measurements<br />

by other techniques. Depending on ATD concentration,<br />

heterogeneous ice nucleation occurred<br />

at temperatures as high as 256K or down to the<br />

onset of homogeneous ice nucleation (237 K). For<br />

ATD-induced ice formation Classical Nucleation<br />

<strong>The</strong>ory (CNT) offers a suitable framework to parameterize<br />

nucleation rates as a function of temperature,<br />

experimentally determined ATD size,<br />

and emulsion droplet volume distributions. <strong>The</strong><br />

latter two quantities serve to estimate the total<br />

heterogeneous surface area present in a droplet,<br />

whereas the suitability of an individual heterogeneous<br />

site to trigger nucleation is described<br />

by the compatibility function (or contact angle)<br />

in CNT. <strong>The</strong> intensity ratio of homogeneous to<br />

heterogeneous freezing peaks is in good agreement<br />

with the assumption that the ATD particles<br />

are randomly distributed amongst the emulsion<br />

droplets. <strong>The</strong> observed dependence of the heterogeneous<br />

freezing temperatures on ATD concentrations<br />

cannot be described by assuming a constant<br />

contact angle for all ATD particles, but requires<br />

the ice nucleation efficiency of ATD particles to be<br />

(log) normally distributed amongst the particles.<br />

Best quantitative agreement is reached when explicitly<br />

assuming that high-compatibility sites are<br />

rare and that therefore larger particles have on<br />

average more and better active sites than smaller<br />

ones. This analysis suggests that a particle has to<br />

have a diameter of at least 0.1 µm to exhibit on<br />

average one active site.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N19, pp 5081-5091.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 55<br />

08.1-49<br />

Aerosol scattering as a function of altitude in<br />

a coastal environment<br />

Marshall J, Lohmann U, Leaitch W R, Lehr P,<br />

Hayden K<br />

Canada, Switzerland<br />

Meteorology & Atmospheric Sciences<br />

(1) An optical closure study was carried out on<br />

the basis of measurements taken during five research<br />

flights in October 2003 over the waters surrounding<br />

Nova Scotia. Measurements of aerosol<br />

size spectra were made using a variety of instruments,<br />

and the size- segregated chemical signature<br />

was determined with an Aerodyne Aerosol<br />

Mass Spectrometer. <strong>The</strong> aerosol scattering and<br />

backscattering coefficients were determined<br />

with an integrating nephelometer at three visible<br />

wavelengths. At a wavelength of 550 nm and<br />

at altitudes less than 1000 m, the mean total scattering<br />

coefficient of the dry in-cabin aerosol is 26<br />

Mm(-1), with a standard deviation of 10 Mm(-1) ,<br />

while the mean backscattering coefficient is 1.7<br />

Mm(-1) with a standard deviation of 0.8 Mm(-1).<br />

On the basis of data from instruments within<br />

the cabin, closure between the directly measured<br />

and calculated total scattering coefficients is attained<br />

for more than 70% of cases, but is not attained<br />

for the backscattering coefficients. Coarse<br />

particles are found to account for roughly half<br />

of the total scattering and 70% of the backscattering<br />

for altitudes up to similar to 1000 m. <strong>The</strong><br />

scattering contribution from coarse particles is<br />

found to account for approximately 65% of the<br />

total scattering and 88% of the backscattering<br />

when calculated on the basis of measurements<br />

taken outside of the aircraft, which are not subject<br />

to inlet losses for larger particles.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND14, JUL 21 ARTN: D14203.<br />

08.1-50<br />

Breaking waves at the tropopause in the wintertime<br />

Northern Hemisphere: Climatological<br />

analyses of the orientation and the theoretical<br />

LC1/2 classification<br />

Martius O, Schwierz C, Davies H C<br />

Switzerland<br />

Meteorology & Atmospheric Sciences<br />

Breaking waves on the tropopause are viewed as<br />

potential vorticity (PV) streamers on middle-world<br />

isentropic levels. A Northern Hemisphere winter<br />

climatology of the streamers’ spatial distribution<br />

and meridional orientation is derived from<br />

the 40-yr ECMWF Re- Analysis (ERA-40) dataset,<br />

and used to assess the nature and frequency of<br />

occurrence of breaking synoptic-scale waves. <strong>The</strong><br />

streamers are grouped into two classes related to<br />

the so-called cyclonic (LC2) and anticyclonic (LC1)<br />

patterns, and the ambient wind strength and wind<br />

shear is also noted. It is shown that the occurrence<br />

of cyclonic and anticyclonic PV streamers exhibits<br />

a distinct spatial variability in the horizontal and<br />

the vertical. <strong>The</strong> majority of cyclonic PV streamers<br />

are found on lower isentropic levels that intersect<br />

the tropopause at more poleward latitudes,<br />

whereas anticyclonic streamers predominate at<br />

higher elevations in the subtropics. An analysis of<br />

the streamer patterns for the two phases of the<br />

North Atlantic Oscillation (NAO) reveals significant<br />

differences in the location and frequency of<br />

both cyclonic and anticyclonic streamers in the<br />

Euro-Atlantic region on the 310-K isentropic level.<br />

Likewise, for the two phases of the ENSO and the<br />

Pacific-North American (PNA) pattern, there are<br />

marked differences in the frequency pattern of<br />

cyclonic streamers. An examination of the tropopause-level<br />

hemispheric flow pattern at the time<br />

of and prior to a streamer’s formation indicates<br />

a linkage to the presence or absence of double jet<br />

structures.<br />

Journal of the Atmospheric Sciences, 2007, V64,<br />

N7, JUL, pp 2576-2592.<br />

08.1-51<br />

Comparison between backscatter lidar and<br />

radiosonde measurements of the diurnal and<br />

nocturnal stratification in the lower troposphere<br />

Martucci G, Matthey R, Mitev V, Richner H<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , Instruments<br />

& Instrumentation<br />

A collection of boundary layer heights has been<br />

derived from measurements performed by a<br />

ground-based backscatter lidar in Neuch tel, Switzerland<br />

(47.000 N, 6.967 E, 485 m ASL). A dataset<br />

of 98 cases have been collected during 2 yr. From<br />

these data, 61 are noon and 37 are midnight cases.<br />

<strong>The</strong> following two different schemes were used to<br />

retrieve the mixed layer depth and the height of<br />

the residual layer from the measurements: the<br />

gradient and variance methods. <strong>The</strong> obtained values<br />

were compared with those derived from the<br />

potential temperature profiles as computed from<br />

radiosonde data. For nocturnal cases, the height<br />

of the first aerosol layer above the residual layer<br />

was also compared to the corresponding potential<br />

temperature value. Correlation coefficients<br />

between lidar and radiosonde in both convective<br />

and stable conditions are between 0.88 and 0.97.<br />

Journal of Atmospheric and Oceanic Technology,<br />

2007, V24, N7, JUL, pp 1231-1244.


56<br />

08.1-52<br />

Counterflow virtual impact or based collection<br />

of small ice particles in mixed-phase clouds<br />

for the physico-chemical characterization of<br />

tropospheric ice nuclei : Sampler description<br />

and first case study<br />

Mertes S, Verheggen B, Walter S, Connolly P, Ebert<br />

M, Schneider J, Bower K N, Cozic J, Weinbruch S,<br />

Baltensperger U, Weingartner E<br />

Germany, Switzerland, England<br />

Meteorology & Atmospheric Sciences<br />

A ground-based sampling system named Ice-CVI<br />

is introduced that is able to extract small ice<br />

particles with sizes between 5 and 20 µm out of<br />

mixed-phase clouds. <strong>The</strong> instrument is based on<br />

a counterflow virtual impactor (CVI) removing interstitial<br />

particles and is supplemented by additional<br />

modules that pre-segregate other constituents<br />

of mixed-phase clouds. Ice particles of 20 µm<br />

and smaller are expected to grow only by water<br />

vapor diffusion and there is a negligible probability<br />

that they scavenge aerosol particles by impaction<br />

and riming. Thus, their residuals which are<br />

released by the Ice-CVI can be interpreted as the<br />

original ice nuclei (IN). In a first field test within<br />

the Cloud and Aerosol Characterization Experiment<br />

(CLACE-3) at the high alpine research station<br />

Jungfraujoch, the collection behavior of the<br />

single components and the complete system was<br />

evaluated under atmospheric sampling conditions.<br />

By comparing parameters measured by the<br />

Ice-CVI with corresponding results obtained from<br />

other inlets or with in-situ instrumentation it is<br />

verified that the small ice particles are representatively<br />

collected whereas all other mixed phase<br />

cloud constituents are effectively suppressed. In<br />

a case study it is observed that supermicrometer<br />

particles preferentially serve as IN although in absolute<br />

terms the IN concentration is dominated by<br />

sub- micrometer particles. Mineral dust (Si), nonvolatile<br />

organic matter and black carbon could be<br />

identified as IN components by means of different<br />

chemical analyses. <strong>The</strong> latter suggests an anthropogenic<br />

influence on the heterogeneous ice nucleation<br />

in supercooled, tropospheric clouds.<br />

Aerosol Science and Technology, 2007, V41, N9, pp<br />

848-864.<br />

08.1-53<br />

A one-dimensional ensemble forecast and assimilation<br />

system for fog prediction<br />

Müller M D, Schmutz C, Parlow E<br />

Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

A probabilistic fog forecast system was designed<br />

based on two high resolution numerical 1-D mod-<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

els called COBEL and PAFOG. <strong>The</strong> 1-D models are<br />

coupled to several 3-D numerical weather prediction<br />

models and thus are able to consider the effects<br />

of advection. To deal with the large uncertainty<br />

inherent to fog forecasts, a whole ensemble<br />

of 1-D runs is computed using the two different<br />

numerical models and a set of different initial<br />

conditions in combination with distinct boundary<br />

conditions. Initial conditions are obtained<br />

from variational data assimilation, which optimally<br />

combines observations with a first guess<br />

taken from operational 3-D models. <strong>The</strong> design<br />

of the ensemble scheme computes members that<br />

should fairly well represent the uncertainty of<br />

the current meteorological regime. Verification<br />

for an entire fog season reveals the importance of<br />

advection in complex terrain. <strong>The</strong> skill of 1-D fog<br />

forecasts is significantly improved if advection is<br />

considered. Thus the probabilistic forecast system<br />

has the potential to support the forecaster and<br />

therefore to provide more accurate fog forecasts.<br />

Pure and Applied Geophysics, 2007, V164, N6-7,<br />

JUN, pp 1241-1264.<br />

08.1-54<br />

Ozone air pollution effects on tree-ring<br />

growth, delta C-13, visible foliar injury and<br />

leaf gas exchange in three ozone-sensitive<br />

woody plant species<br />

Novak K, Cherubini P, Saurer M, Fuhrer J, Skelly J<br />

M, Kräuchi N, Schaub M<br />

Switzerland, USA<br />

Meteorology & Atmospheric Sciences , Plant<br />

Sciences , Forestry<br />

We assessed the effects of ambient tropospheric<br />

ozone on annual tree- ring growth, delta C-13 in<br />

the rings, leaf gas exchange and visible injury<br />

in three ozone-sensitive woody plant species in<br />

southern Switzerland. Seedlings of Populus nigra<br />

L., Viburnum lantana L. and Fraxinus excelsior L.<br />

were exposed to charcoal-filtered air (CF) and nonfiltered<br />

air (NF) in open-top chambers, and to ambient<br />

air (AA) in open plots during the 2001 and<br />

2002 growing seasons. Ambient ozone exposures<br />

in the region were sufficient to cause visible foliar<br />

injury, early leaf senescence and premature leaf<br />

loss in all species. Ozone had significant negative<br />

effects on net photosynthesis and stomatal conductance<br />

in all species in 2002 and in V. lantana<br />

and F. excelsior in 2001. Water-use efficiency decreased<br />

and intercellular CO 2 concentrations increased<br />

in all species in response to ozone in 2002<br />

only. <strong>The</strong> width and delta C-13 of the 2001 and<br />

2002 growth rings were measured for all species<br />

at the end of the 2002 growing season. Compared<br />

with CF seedlings, mean ring width in the AA and


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 57<br />

NF P. nigra seedlings was reduced by 52 and 46%,<br />

respectively, in 2002, whereas in V lantana and F.<br />

excelsior ring width showed no significant reductions<br />

in either year. Although delta C-13 was usually<br />

more negative in CF seedlings than in AA and<br />

NF seedlings, with the exception of F. excelsior in<br />

2001, ozone effects on delta C-13 were significant<br />

only for V lantana and P nigra in 2001. Among<br />

species, P. nigra exhibited the greatest response to<br />

ozone for the measured parameters as well as the<br />

most severe foliar injury and was the only species<br />

to show a significant reduction in ring width in response<br />

to ozone exposure, despite significant negative<br />

ozone effects on leaf gas exchange and the<br />

development of visible foliar injury in V lantana<br />

and F. excelsior. Thus, significant ozone-induced<br />

effects at the leaf level did not correspond to reduced<br />

tree-ring growth or increased delta C-13 in<br />

all species, indicating that the timing of ozone exposure<br />

and severity of leaf-level responses may be<br />

important in determining the sensitivity of tree<br />

productivity to ozone exposure.<br />

Tree Physiology, 2007, V27, N7, JUL, pp 941-949.<br />

08.1-55<br />

Perturbation of the European free troposphere<br />

aerosol by North American forest fire plumes<br />

during the ICARTT-ITOP experiment in summer<br />

2004<br />

Petzold A, Weinzierl B, Huntrieser H, Stohl A, Real<br />

E, Cozic J, Fiebig M, Hendricks J, Lauer A, Law K,<br />

Roiger A, Schlager H, Weingartner E<br />

Germany, Norway, France, Switzerland<br />

Meteorology & Atmospheric Sciences , Modelling ,<br />

Forestry , Plant Sciences<br />

During the ICARTT-ITOP Experiment in summer<br />

2004 plumes from large wildfires in North America<br />

were transported to Central Europe at 3 - 8 km<br />

altitude above sea level (a.s.l.). <strong>The</strong>se plumes were<br />

studied with the DLR (Deutsches Zentrum fuer<br />

Luft- und Raumfahrt) research aircraft Falcon<br />

which was equipped with an extensive set of in<br />

situ aerosol and trace gas instruments. Analyses<br />

by the Lagrangian dispersion model FLEXPART<br />

provided source regions, transport times and<br />

horizontal extent of the fire plumes. Results from<br />

the general circulation model ECHAM/MADE and<br />

data from previous aerosol studies over Central<br />

Europe provided reference vertical profiles of<br />

black carbon (BC) mass concentrations for year<br />

2000 conditions with forest fire activities below<br />

the long-term average. Smoke plume observations<br />

yielded a BC mass fraction of total aerosol mass<br />

with respect to PM 2.5 of 2 - 8%. <strong>The</strong> ratio of BC<br />

mass to excess CO was 3 - 7.5 mg BC (g CO)(-1). Even<br />

after up to 10 days of atmospheric transport, both<br />

characteristic properties were of the same order<br />

as for fresh emissions. This suggests an efficient<br />

lifting of BC from forest fires to higher altitudes<br />

with only minor scavenging removal of particulate<br />

matter. Maximum aerosol absorption coefficient<br />

values were 7 - 8Mm (-1) which is about two<br />

orders of magnitude above the average European<br />

free tropospheric background value. Forest fire<br />

aerosol size distributions were characterised by a<br />

strong internally mixed accumulation mode centred<br />

at modal diameters of 0.25 - 0.30 µm with an<br />

average distribution width of 1.30. Nucleation and<br />

small Aitken mode particles were almost completely<br />

depleted.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N19, pp 5105-5127.<br />

08.1-56<br />

Long-term variability of daily North Atlantic-<br />

European pressure patterns since 1850 classified<br />

by simulated annealing clustering<br />

Philipp A, Della Marta P M, Jacobeit J, Fereday D R,<br />

Jones P D, Moberg A, Wanner H<br />

Germany, Switzerland, England, Sweden<br />

Meteorology & Atmospheric Sciences<br />

Reconstructed daily mean sea level pressure patterns<br />

of the North Atlantic - European region are<br />

classified for the period 1850 to 2003 to explore<br />

long- term changes of the atmospheric circulation<br />

and its impact on long- term temperature variability<br />

in the central European region. Commonly<br />

used k- means clustering algorithms resulted in<br />

classifications of low quality because of methodological<br />

deficiencies leading to local optima by<br />

chance for complex datasets. In contrast, a newly<br />

implemented clustering scheme combining the<br />

concepts of simulated annealing and diversified<br />

randomization (SANDRA) is able to reduce substantially<br />

the influence of chance in the cluster<br />

assignment, leading to partitions that are noticeably<br />

nearer to the global optimum and more stable.<br />

<strong>The</strong> differences between conventional cluster<br />

analysis and the SANDRA scheme are significant<br />

for subsequent analyses of single clusters - in particular,<br />

for trend analysis. Conventional indices<br />

used to determine the appropriate number of<br />

clusters failed to provide clear guidance, indicating<br />

that no distinct separation between clusters of<br />

circulation types exists in the dataset. <strong>The</strong>refore,<br />

the number of clusters is determined by an external<br />

indicator, the so- called dominance criteria for<br />

t- mode principal component analysis. Nevertheless,<br />

the resulting partitions are stable for certain<br />

numbers of clusters and provide meaningful and<br />

reproducible clusters. <strong>The</strong> resulting types of pressure<br />

patterns reveal pronounced long- term vari-


58<br />

ability and various significant trends of the time<br />

series of seasonal cluster frequency. Tentative estimations<br />

of central European temperature changes<br />

based solely on seasonal cluster frequencies can<br />

explain between 33.9% (summer) and 59.0% (winter)<br />

of temperature variance on the seasonal time<br />

scale. However, the signs of long- term changes<br />

in temperature are correctly reproduced even on<br />

multidecadal - centennial time scales. Moreover,<br />

linear warming trends are reproduced, implying<br />

from one- third up to one- half of the observed<br />

temperature increase between 1851/ 52 and 2003<br />

(except for summer, but with significant trends<br />

for spring and autumn), indicating that changes<br />

in daily circulation patterns contribute to the observed<br />

overall long- term warming in the central<br />

European region.<br />

Journal of Climate, 2007, V20, N16, AUG 17, pp<br />

4065-4095.<br />

08.1-57<br />

Remote sensing of aerosol optical depth over<br />

central Europe from MSG- SEVIRI data and accuracy<br />

assessment with ground-based AERO-<br />

NET measurements<br />

Popp C, Hauser A, Foppa N, Wunderle S<br />

Switzerland, Germany<br />

Remote Sensing , Meteorology & Atmospheric<br />

Sciences<br />

In this study, the remote sensing of aerosol optical<br />

depth (tau(a)) from the geostationary Meteosat<br />

Second Generation (MSG) Spinning Enhanced Visible<br />

and Infrared Imager (SEVIRI) is demonstrated.<br />

<strong>The</strong> proposed method is based on the analysis of<br />

a time series of SEVIRI’s 0.6 µm channel images.<br />

Top-of-atmosphere reflectance is precorrected for<br />

the effect of atmospheric gases and a background<br />

aerosol amount. Subsequently, surface reflectance<br />

for each pixel is estimated by determining its lowest<br />

precorrected reflectance within the observed<br />

time period for each satellite observation time of<br />

the day. <strong>The</strong> resulting diurnal surface reflectance<br />

curve in combination with the radiative transfer<br />

code SMAC are finally used to derive ta. This approach<br />

is applied to SEVIRI subscenes of central<br />

Europe (40.8 - 51.3 degrees N, 0.3 degrees W - 19.9<br />

degrees E) from August 2004, daily acquired between<br />

0612 and 1712 UTC in intervals of 15 min.<br />

SEVIRI tau(a) are related to Aerosol Robotic Network<br />

(AERONET) Sun photometer measurements<br />

from nine sites. About 3200 instantaneous SEVIRI<br />

and Sun photometer tau(a) are compared. An<br />

overall correlation of 0.9 and a root mean square<br />

error of 0.08 are obtained. Further, the spatial distribution<br />

of SEVIRI tau(a) maps for August 2004<br />

represent expectable features like higher concen-<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

trations in industrialized regions or lower loading<br />

in higher altitudes. It is concluded that the<br />

described method is able to provide an estimate of<br />

tau(a) from MSG-SEVIRI data. Such aerosol maps<br />

of high temporal frequency could be of interest to<br />

atmospheric related sciences, e. g., to track aerosol<br />

particle transport.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND24, NOV 9 ARTN: D24S11.<br />

08.1-58<br />

Hydrological aspects of the Mesoscale Alpine<br />

Programme: Findings from field experiments<br />

and simulations<br />

Ranzi R, Zappa M, Bacchi B<br />

Italy, Switzerland<br />

Modelling , Hydrology , Meteorology & Atmospheric<br />

Sciences<br />

<strong>The</strong> Mesoscale Alpine Programme (MAP) was a<br />

unique initiative to improve the understanding<br />

of processes involved in orographically influenced<br />

precipitation events and in the related emergence<br />

and mitigation of floods in the Alps. This study<br />

presents a summary of the results from investigations<br />

of hydrological relevance in areas to<br />

the south (Lago Maggiore watershed) and north<br />

(Ammer watershed) of the Alps. A special focus<br />

is given to the 1999 Special Observing Period<br />

(SOP) experiment. MAP has been an important<br />

dialogue platform between the hydrological and<br />

meteorological communities. A common goal<br />

has been the verification and the assessment of<br />

errors and sources of uncertainty of new coupled<br />

techniques for flood forecasting in mountainous<br />

environments. <strong>The</strong> ensemble multi-model<br />

error in the hydrometeorological forecast, two<br />

days in advance, was 30% of the observed peaks<br />

and 15% of the observed runoff volumes, on average.<br />

To provide some insight on the relative importance<br />

and priority of observation strategies<br />

of hydrological factors such as soil moisture and<br />

reservoir volume in contributing to the flood intensity,<br />

the MAP project ‘Hydrology’ focused also<br />

on the role and magnitude of water storage in reservoirs.<br />

<strong>The</strong> presented analyses indicate that for<br />

the investigated basins and flood events, the storage<br />

reservoirs may retain, on average, up to 10%<br />

of the event runoff volume and are key elements<br />

contributing to the mitigation of peak runoff.<br />

<strong>The</strong> observed variability of soil moisture is large<br />

and therefore it has been confirmed that severe<br />

difficulties remain in instrumental monitoring of<br />

soil moisture in mountainous environments. <strong>The</strong><br />

sensitivity of floods to soil moisture in the physiogeographic<br />

context analysed here seems, however,<br />

to be minor, due to the shallow soil layer covering


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 59<br />

the underlying rocks and the relatively high permeability<br />

of soils which reduce the ‘hydrological<br />

memory’ of the soil cover in the mountain basins<br />

investigated.<br />

Quarterly Journal of the Royal Meteorological Society,<br />

2007, V133, N625, B, APR, pp 867-880.<br />

08.1-59<br />

Ice nucleation of ammonia gas exposed montmorillonite<br />

mineral dust particles<br />

Salam A, Lohmann U, Lesins G<br />

Canada, Bangladesh, Switzerland<br />

Meteorology & Atmospheric Sciences<br />

<strong>The</strong> ice nucleation characteristics of montmorillonite<br />

mineral dust aerosols with and without<br />

exposure to ammonia gas were measured at different<br />

atmospheric temperatures and relative humidities<br />

with a continuous flow diffusion chamber.<br />

<strong>The</strong> montmorillonite particles were exposed<br />

to pure (100%) and diluted ammonia gas (25 ppm)<br />

at room temperature in a stainless steel chamber.<br />

<strong>The</strong>re was no significant change in the mineral<br />

dust particle size distribution due to the ammonia<br />

gas exposure. 100% pure ammonia gas exposure<br />

enhanced the ice nucleating fraction of montmorillonite<br />

mineral dust particles 3 to 8 times at<br />

90% relative humidity with respect to water (RHw)<br />

and 5 to 8 times at 100% RHw for 120 min exposure<br />

time compared to unexposed montmorillonite<br />

within our experimental conditions. <strong>The</strong><br />

percentages of active ice nuclei were 2 to 8 times<br />

higher at 90% RHw and 2 to 7 times higher at 100%<br />

RHw in 25 ppm ammonia exposed montmorillonite<br />

compared to unexposed montmorillonite. All<br />

montmorillonite particles are more efficient as ice<br />

nuclei with increasing relative humidities and decreasing<br />

temperatures. <strong>The</strong> activation temperature<br />

of montmorillonite exposed to 100% pure ammonia<br />

was 15 degrees C higher than for unexposed<br />

montmorillonite particles at 90% RHw. In the 25<br />

ppm ammonia exposed montmorillonite experiments,<br />

the activation temperature was 10 degrees<br />

C warmer than unexposed montmorillonite at 90%<br />

RHw. Degassing does not reverse the ice nucleating<br />

ability of ammonia exposed montmorillonite<br />

mineral dust particles suggesting that the ammonia<br />

is chemically bound to the montmorillonite<br />

particle. This is the first experimental evidence<br />

that ammonia gas exposed montmorillonite mineral<br />

dust particles can enhance its activation as ice<br />

nuclei and that the activation can occur at temperatures<br />

warmer than -degrees C where natural<br />

atmospheric ice nuclei are very scarce.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N14, pp 3923-3931.<br />

08.1-60<br />

A trajectory-based estimate of the tropospheric<br />

ozone column using the residual method<br />

Schoeberl M R, Ziemke J R, Bojkov B, Livesey N J,<br />

Duncan B, Strahan S, Froidevaux L, Kulawik S, Bhartia<br />

P K, Chandra S, Levelt P F, Witte J C, Thompson A<br />

M, Cuevas E, Redondas A, Tarasick D W, Davies J,<br />

Bodeker G E, Hansen G, Johnson B J, Oltmans S J,<br />

Voemel H, Allaart M, Kelder H, Newchurch M, Godin<br />

Beekmann S, Ancellet G, Claude H, Andersen S B,<br />

Kyroe E, Parrondos M C, Yela M, Zablocki G, Moore<br />

D, Dier H, von der Gathen P, Viatte P, Stuebi R, Calpini<br />

B, Skrivankova P, Dorokhov V, de Backer H, Schmidlin<br />

F J, Coetzee G, Fujiwara M, Thouret V, Posny F, Morris<br />

G, Merrill J, Leong C P, König Langlo G, Joseph E<br />

USA, Netherlands, Spain, Canada, New Zealand,<br />

Norway, France, Denmark, Finland, Poland, England,<br />

Germany, Switzerland, Czech Republic, Russia,<br />

Belgium, South Africa, Japan, Malaysia<br />

Meteorology & Atmospheric Sciences , Modelling<br />

We estimate the tropospheric column ozone using<br />

a forward trajectory model to increase the<br />

horizontal resolution of the Aura Microwave<br />

Limb Sounder (MLS) derived stratospheric column<br />

ozone. Subtracting the MLS stratospheric column<br />

from Ozone Monitoring Instrument total column<br />

measurements gives the trajectory enhanced tropospheric<br />

ozone residual (TTOR). Because of different<br />

tropopause definitions, we validate the basic<br />

residual technique by computing the 200-hPato-<br />

surface column and comparing it to the same<br />

product from ozonesondes and Tropospheric<br />

Emission Spectrometer measurements. Comparisons<br />

show good agreement in the tropics and reasonable<br />

agreement at middle latitudes, but there<br />

is a persistent low bias in the TTOR that may be<br />

due to a slight high bias in MLS stratospheric column.<br />

With the improved stratospheric column<br />

resolution, we note a strong correlation of extratropical<br />

tropospheric ozone column anomalies<br />

with probable troposphere-stratosphere exchange<br />

events or folds. <strong>The</strong> folds can be identified by their<br />

colocation with strong horizontal tropopause gradients.<br />

TTOR anomalies due to folds may be mistaken<br />

for pollution events since folds often occur<br />

in the Atlantic and Pacific pollution corridors.<br />

We also compare the 200-hPa-to-surface column<br />

with <strong>Global</strong> Modeling Initiative chemical model<br />

estimates of the same quantity. While the tropical<br />

comparisons are good, we note that chemical<br />

model variations in 200hPa-to-surface column at<br />

middle latitudes are much smaller than seen in<br />

the TTOR.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND24, DEC 19 ARTN: D24S49.


60<br />

08.1-61<br />

<strong>The</strong> impact of NOx, CO and VOC emissions on<br />

the air quality of Zürich airport<br />

Schürmann G, Schäfer K, Jahn C, Hoffman H,<br />

Bauerfeind M, Fleuti E, Rappenglück B<br />

Germany, Switzerland, USA<br />

Meteorology & Atmospheric Sciences<br />

Atmospheric Environment, 2007, V41, N26, AUG,<br />

pp 5553-5554.<br />

08.1-62<br />

Dewpoint and humidity measurements and<br />

trends at the summit of Mount Washington,<br />

New Hampshire, 1935-2004<br />

Seidel T M, Grant A N, Pszenny A A P, Allman D J<br />

USA, Switzerland<br />

Meteorology & Atmospheric Sciences<br />

Meteorological conditions have been recorded at<br />

the summit of Mount Washington, New Hampshire,<br />

(44 degrees 16 ‘ N, 71 degrees 18 ‘ W, 1914<br />

m ASL) since November 1932. Use of consistent<br />

instrumentation allows analysis of humidity<br />

measurements as calculated from error- checked<br />

dry bulb temperature, wet bulb temperature, and<br />

pressure during the period 1935-2004. This paper<br />

presents seasonally and annually averaged dewpoint<br />

temperature, mixing ratio, and relative humidity<br />

means and trends, including clear-air and<br />

fog subsets and, beginning in 1939, day and night<br />

subsets. <strong>The</strong> majority of linear trends are negative<br />

over the full study period, although these decreases<br />

are not constant, with relatively large (small)<br />

values in the mid-1950s (late 1970s). Annual mean<br />

dewpoint (water vapor mixing ratio) over the 70-yr<br />

period has decreased by 0.06 degrees C decade(-1)<br />

(0.01 g kg(-1) decade(-1)). During this period the annual<br />

frequency of fog increased by 0.5% decade(-1).<br />

Dewpoint and mixing ratio trends, both generally<br />

decreasing, differ by season; they are smallest in<br />

spring and greatest in fall. Relative humidity has<br />

decreased most in winter. <strong>The</strong> clear-air subset<br />

shows significant decreases in both dewpoint and<br />

mixing ratio for all seasons except spring.<br />

Journal of Climate, 2007, V20, N22, NOV 15, pp<br />

5629-5641.<br />

08.1-63<br />

Assessment of the performance of ECCozonesondes<br />

under quasi-flight conditions<br />

in the environmental simulation chamber:<br />

Insights from the Juelich Ozone Sonde Intercomparison<br />

Experiment (JOSIE)<br />

Smit H G J, Straeter W, Johnson B J, Oltmans S J,<br />

Davies J, Tarasick D W, Hoegger B, Stubi R, Schmidlin<br />

F J, Northam T, Thompson A M, Witte J C, Boyd<br />

I, Posny F<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

Germany, USA, Switzerland, Reunion<br />

Meteorology & Atmospheric Sciences , Modelling<br />

(1) Since 1996, quality assurance experiments<br />

of electrochemical concentration cell (ECC)<br />

ozonesondes of two different model types (SPC-6A<br />

and ENSCI-Z) have been conducted in the environmental<br />

simulation facility at the Research Centre<br />

Juelich within the framework of the Juelich Ozone<br />

Sonde Intercomparison Experiment (JOSIE). <strong>The</strong><br />

experiments have shown that the performance<br />

characteristics of the two ECC-sonde types can be<br />

significantly different, even when operated under<br />

the same conditions. Particularly above 20 km<br />

the ENSCI-Z sonde tends to measure 5-10% more<br />

ozone than the SPC-6A sonde. Below 20 km the differences<br />

are 5% or less, but appear to show some<br />

differences with year of manufacture. <strong>The</strong>re is a<br />

significant difference in the ozone readings when<br />

sondes of the same type are operated with different<br />

cathode sensing solutions. Testing the most<br />

commonly used sensing solutions showed that for<br />

each ECC- manufacturer type the use of 1.0% KI<br />

and full buffer gives 5% larger ozone values compared<br />

with the use of 0.5% KI and half buffer, and<br />

as much as 10% larger values compared with 2.0%<br />

KI and no buffer. For ozone sounding stations<br />

performing long term measurements this means<br />

that changing the sensing solution type or ECCsonde<br />

type can easily introduce a change of +/- 5%<br />

or more in their records, affecting determination<br />

of ozone trends. Standardization of operating procedures<br />

for ECC-sondes yields a precision better<br />

than +/-(3-5)% and an accuracy of about +/-(5-10)%<br />

up to 30 km altitude.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND19, OCT 11 ARTN: D19306.<br />

08.1-64<br />

Modelling heavy metal fluxes from traffic into<br />

the environment<br />

Steiner M, Boller M, Schulz T, Pronk W<br />

Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

A new method is presented which allows emissions<br />

of traffic into the environment to be described<br />

as a function of road distance. <strong>The</strong> method<br />

distinguishes different types of emissions (runoff,<br />

spray and drift), which are determined by measurements<br />

and mass balances of a specified road<br />

section. <strong>The</strong> measurement of two-dimensional<br />

pollutant concentrations in the road shoulder is<br />

an important part of the method. In a case study<br />

performed at Burgdorf, Switzerland, the method<br />

was applied to the determination of the spatial<br />

distribution of heavy metal emissions. <strong>The</strong> results<br />

show that between 36 and 65% of the heavy met-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 61<br />

als Cd, Cr, Cu, Ph and Zn are present in runoff and<br />

spray and between 35 and 64% are dispersed diffusely<br />

in the environment (defined as drift). <strong>The</strong><br />

runoff infiltrates into the vegetated road shoulder<br />

up to a distance of approx. 1 m from the road.<br />

<strong>The</strong> distribution of spray shows a maximum at<br />

1 m and decreases steadily up to a distance of 5<br />

m. This information can serve as a basis for the<br />

quantitative evaluation of road-runoff treatment<br />

scenarios. Although the results of the Burgdorf<br />

study are case- specific, several general guidelines<br />

for the reduction of traffic- related emissions can<br />

be derived from it.<br />

Journal of Environmental Monitoring, 2007, V9,<br />

N8, AUG, pp 847-854.<br />

08.1-65<br />

Ultrafine (aerosol) particles and their agglomerate<br />

and aggregate - revised international<br />

measuring convention<br />

Steinle P<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , International<br />

Relations<br />

Gefahrstoffe Reinhaltung der Luft, 2007, V67, N6,<br />

JUN, pp 243-245.<br />

08.1-66<br />

Light induced conversion of nitrogen dioxide<br />

into nitrous acid on submicron humic acid<br />

aerosol<br />

Stemmler K, Ndour M, Elshorbany Y, Kleffmann J,<br />

Danna B, George C, Bohn B, Ammann M<br />

Switzerland, France, Germany, Egypt<br />

Urban Studies , Meteorology & Atmospheric<br />

Sciences<br />

<strong>The</strong> interactions of aerosols consisting of humic<br />

acids with gaseous nitrogen dioxide (NO 2) were<br />

investigated under different light conditions in<br />

aerosol flow tube experiments at ambient pressure<br />

and temperature. <strong>The</strong> results show that<br />

NO 2 is converted on the humic acid aerosol into<br />

nitrous acid (HONO), which is released from the<br />

aerosol and can be detected in the gas phase at<br />

the reactor exit. <strong>The</strong> formation of HONO on the<br />

humic acid aerosol is strongly activated by light:<br />

In the dark, the HONO-formation was below the<br />

detection limit, but it was increasing with the<br />

intensity of the irradiation with visible light.<br />

Under simulated atmospheric conditions with<br />

respect to the actinic flux, relative humidity and<br />

NO 2-concentration, reactive uptake coefficients<br />

gamma(rxn) for the NO 2 -> HONO conversion on<br />

the aerosol between gamma(rxn) < 10(-7) (in the<br />

dark) and gamma(rxn)=6x 10(-6) were observed.<br />

<strong>The</strong> observed uptake coefficients decreased with<br />

increasing NO 2-concentration in the range from<br />

2.7 to 280 ppb and were dependent on the relative<br />

humidity (RH) with slightly reduced values at low<br />

humidity (< 20% RH) and high humidity (> 60%<br />

RH). <strong>The</strong> measured uptake coefficients for the NO 2<br />

-> HONO conversion are too low to explain the<br />

HONO-formation rates observed near the ground<br />

in rural and urban environments by the conversion<br />

of NO 2 -> HONO on organic aerosol surfaces,<br />

even if one would assume that all aerosols consist<br />

of humic acid only. It is concluded that the processes<br />

leading to HONO formation on the Earth<br />

surface will have a much larger impact on the<br />

HONO-formation in the lowermost layer of the<br />

troposphere than humic materials potentially occurring<br />

in airborne particles.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N16, pp 4237-4248.<br />

08.1-67<br />

Impact of scale and aggregation on the terrestrial<br />

water exchange: Integrating land surface<br />

models and Rhone catchment observations<br />

Stöckli R, Vidale P L, Boone A, Schär C<br />

Switzerland, USA, England, France<br />

Modelling , Meteorology & Atmospheric Sciences ,<br />

Hydrology<br />

Land surface models (LSMs) used in climate modeling<br />

include detailed above- ground biophysics<br />

but usually lack a good representation of runoff.<br />

Both processes are closely linked through soil<br />

moisture. Soil moisture however has a high spatial<br />

variability that is unresolved at climate model<br />

grid scales. Physically based vertical and horizontal<br />

aggregation methods exist to account for this<br />

scaling problem. Effects of scaling and aggregation<br />

have been evaluated in this study by performing<br />

catchment- scale LSM simulations for the Rh<br />

ne catchment. It is found that evapotranspiration<br />

is not sensitive to soil moisture over the Rhone<br />

but it largely controls total runoff as a residual of<br />

the terrestrial water balance. Runoff magnitude is<br />

better simulated when the vertical soil moisture<br />

fluxes are resolved at a finer vertical resolution.<br />

<strong>The</strong> use of subgrid-scale topography significantly<br />

improves both the timing of runoff on the daily<br />

time scale (response to rainfall events) and the<br />

magnitude of summer baseflow (from seasonal<br />

groundwater recharge). Explicitly accounting for<br />

soil moisture as a subgrid- scale process in LSMs<br />

allows one to better resolve the seasonal course<br />

of the terrestrial water storage and makes runoff<br />

insensitive to the used grid scale. However, scale<br />

dependency of runoff to above-ground hydrology<br />

cannot be ignored: snowmelt runoff from the Alpine<br />

part of the Rh ne is sensitive to the spatial


62<br />

resolution of the snow scheme, and autumnal<br />

runoff from the Mediterranean part of the Rh ne<br />

is sensitive to the spatial resolution of precipitation.<br />

Journal of Hydrometeorology, 2007, V8, N5, OCT,<br />

pp 1002-1015.<br />

08.1-68<br />

Direct assessment of international consistency<br />

of standards for ground-level ozone: strategy<br />

and implementation toward metrological<br />

traceability network in Asia<br />

Tanimoto H, Mukai H, Sawa Y, Matsueda H, Yonemura<br />

S, Wang T, Poon S, Wong A, Lee G, Jung J Y,<br />

Kim K R, Lee M H, Lin N H, Wang J L, Ou Yang C F,<br />

Wu C F, Akimoto H, Pochanart P, Tsuboi K, Doi H,<br />

Zellwegern C, Klausenn J<br />

Japan, Peoples R China, South Korea, Taiwan,<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , International<br />

Relations<br />

An international exercise to directly assess consistency<br />

of standards for ground-level ozone in<br />

East Asia was conducted as part of the East Asian<br />

Regional Experiment 2005 (EAREX 2005) in the<br />

framework of the Atmospheric Brown Clouds<br />

(ABC) project. Ten organizations collaboratively<br />

participated in the intercomparison. Four groups<br />

representing Japan, Korea, Hong Kong, and Taiwan<br />

made comparisons at the Gosan super observatory,<br />

Jeju Island, Korea, in March 2005, with<br />

ozone instruments calibrated to their national<br />

standards, and four Japanese groups made off-site<br />

comparisons with laboratory-level standards. All<br />

comparisons generally indicated good agreement<br />

with the standard reference photometer (SRP) 35,<br />

built by the National Institute of Standards and<br />

Technology (USA) and maintained by the National<br />

Institute for Environmental Studies (Japan). <strong>The</strong><br />

assessment was expanded to measurement networks<br />

contributing to the World Meteorological<br />

Organization’s <strong>Global</strong> Atmospheric Watch (WMO/<br />

GAW) program as part of off-site comparisons,<br />

and excellent agreement was achieved. <strong>The</strong>se efforts<br />

contribute to propagating traceability of the<br />

national metrology standards among the atmospheric<br />

science community, to ensuring comparability<br />

of the existing ozone measurements, and to<br />

establishing an integrated network of air quality<br />

monitoring in Asia.<br />

Journal of Environmental Monitoring, 2007, V9,<br />

N11, pp 1183-1193.<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

08.1-69<br />

<strong>The</strong> influence of a weakening of the Atlantic<br />

meridional overturning circulation on ENSO<br />

Timmermann A, Okumura Y, An S I, Clement A,<br />

Dong B, Guilyardi E, Hu A, Jungclaus J H, Renold<br />

M, Stocker T F, Stouffer R J, Sutton R, Xie S P, Yin J<br />

USA, South Korea, England, France, Germany,<br />

Switzerland<br />

Oceanography , Meteorology & Atmospheric Sciences<br />

, Modelling<br />

<strong>The</strong> influences of a substantial weakening of<br />

the Atlantic meridional overturning circulation<br />

(AMOC) on the tropical Pacific climate mean state,<br />

the annual cycle, and ENSO variability are studied<br />

using five different coupled general circulation<br />

models (CGCMs). In the CGCMs, a substantial<br />

weakening of the AMOC is induced by adding<br />

freshwater flux forcing in the northern North<br />

Atlantic. In response, the well- known surface<br />

temperature dipole in the low- latitude Atlantic<br />

is established, which reorganizes the large- scale<br />

tropical atmospheric circulation by increasing<br />

the northeasterly trade winds. This leads to a<br />

southward shift of the intertropical convergence<br />

zone (ITCZ) in the tropical Atlantic and also the<br />

eastern tropical Pacific. Because of evaporative<br />

fluxes, mixing, and changes in Ekman divergence,<br />

a meridional temperature anomaly is generated<br />

in the northeastern tropical Pacific, which leads<br />

to the development of a meridionally symmetric<br />

thermal background state. In four out of five CGC-<br />

Ms this leads to a substantial weakening of the<br />

annual cycle in the eastern equatorial Pacific and<br />

a subsequent intensification of ENSO variability<br />

due to nonlinear interactions. In one of the CGCM<br />

simulations, an ENSO intensification occurs as<br />

a result of a zonal mean thermocline shoaling.<br />

Analysis suggests that the atmospheric circulation<br />

changes forced by tropical Atlantic SSTs can<br />

easily influence the large- scale atmospheric circulation<br />

and hence tropical eastern Pacific climate.<br />

Furthermore, it is concluded that the existence of<br />

the present- day tropical Pacific cold tongue complex<br />

and the annual cycle in the eastern equatorial<br />

Pacific are partly controlled by the strength of<br />

the AMOC. <strong>The</strong> results may have important implications<br />

for the interpretation of global multidecadal<br />

variability and paleo- proxy data.<br />

Journal of Climate, 2007, V20, N19, OCT, pp<br />

4899-4919.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 63<br />

08.1-70<br />

Aerosols in polar regions: A historical overview<br />

based on optical depth and in situ observations<br />

Tomasi C, Vitale V, Lupi A, Di Carmine C, Campanelli<br />

M, Herber A, Treffeisen R, Stone R S, Andrews<br />

E, Sharma S, Radionov V, von Hoyningen Huene<br />

W, Stebel K, Hansen G H, Myhre C L, Wehrli C,<br />

Aaltonen V, Lihavainen H, Virkkula A, Hillamo R,<br />

Stroem J, Toledano C, Cachorro V E, Ortiz P, de Frutos<br />

A M, Blindheim S, Frioud M, Gausa M, Zielinski<br />

T, Petelski T, Yamanouchi T<br />

Italy, Germany, USA, Canada, Russia, Norway, Switzerland,<br />

Finland, Sweden, Spain, Poland, Japan<br />

Meteorology & Atmospheric Sciences , Modelling<br />

Large sets of filtered actinometer, filtered pyrheliometer<br />

and Sun photometer measurements have<br />

been carried out over the past 30 years by various<br />

groups at different Arctic and Antarctic sites and<br />

for different time periods. <strong>The</strong>y were examined<br />

to estimate ensemble average, long-term trends<br />

of the summer background aerosol optical depth<br />

AOD(500 nm) in the polar regions (omitting the<br />

data influenced by Arctic haze and volcanic eruptions).<br />

<strong>The</strong> trend for the Arctic was estimated to<br />

be between -1.6% and -2.0% per year over 30 years,<br />

depending on location. No significant trend was<br />

observed for Antarctica. <strong>The</strong> time patterns of<br />

AOD(500 nm) and angstrom ngstrom’s parameters<br />

a and beta measured with Sun photometers during<br />

the last 20 years at various Arctic and Antarctic<br />

sites are also presented. <strong>The</strong>y give a measure<br />

of the large variations of these parameters due to<br />

El Chichon, Pinatubo, and Cerro Hudson volcanic<br />

particles, Arctic haze episodes most frequent in<br />

winter and spring, and the transport of Asian dust<br />

and boreal smokes to the Arctic region. Evidence<br />

is also shown of marked differences between the<br />

aerosol optical parameters measured at coastal<br />

and high-altitude sites in Antarctica. In situ optical<br />

and chemical composition parameters of aerosol<br />

particles measured at Arctic and Antarctic<br />

sites are also examined to achieve more complete<br />

information on the multimodal size distribution<br />

shape parameters and their radiative properties.<br />

A characterization of aerosol radiative parameters<br />

is also defined by plotting the daily mean values<br />

of a as a function of AOD(500 nm), separately for<br />

the two polar regions, allowing the identification<br />

of different clusters related to fifteen aerosol<br />

classes, for which the spectral values of complex<br />

refractive index and single scattering albedo were<br />

evaluated.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND16, AUG 21 ARTN: D16205.<br />

08.1-71<br />

Aerosol partitioning between the interstitial<br />

and the condensed phase in mixed-phase<br />

clouds<br />

Verheggen B, Cozic J, Weingartner E, Bower K,<br />

Mertes S, Connolly P, Gallagher M W, Flynn M,<br />

Choularton T, Baltensperger U<br />

Germany, England, Switzerland<br />

Meteorology & Atmospheric Sciences<br />

(1) <strong>The</strong> partitioning of aerosol particles between<br />

the cloud and the interstitial phase (i.e., unactivated<br />

aerosol) has been investigated during several<br />

Cloud and Aerosol Characterization Experiments<br />

(CLACE-3, CLACE-3 1/2 and CLACE-4) conducted in<br />

winter and summer 2004 and winter 2005 at the<br />

high alpine research station Jungfraujoch (3580<br />

m altitude, Switzerland). Ambient air was sampled<br />

using different inlets in order to determine<br />

the activated fraction of aerosol particles, F-N, defined<br />

as the fraction of the total aerosol number<br />

concentration (with particle diameter d(p) > 100<br />

nm) that has been incorporated into cloud particles.<br />

<strong>The</strong> liquid and ice water content of mixedphase<br />

clouds were characterized by analyzing<br />

multiple cloud probes. <strong>The</strong> dependence of the activated<br />

fraction on several environmental factors<br />

is discussed on the basis of more than 900 h of incloud<br />

observations and parameterizations for key<br />

variables are given. FN is found to increase with<br />

increasing liquid water content and to decrease<br />

with increasing particle number concentration in<br />

liquid clouds. FN also decreases with increasing<br />

cloud ice mass fraction and with decreasing temperature<br />

from 0 to -25 degrees C. <strong>The</strong> Wegener-<br />

Bergeron-Findeisen process probably contributed<br />

to this trend, since the presence of ice crystals<br />

causes liquid droplets to evaporate, thus releasing<br />

the formerly activated particles back into the<br />

interstitial phase. Ice nucleation could also have<br />

prevented additional cloud condensation nuclei<br />

from activating. <strong>The</strong> observed activation behavior<br />

has significant implications for our understanding<br />

of the indirect effect of aerosols on climate.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND23, DEC 13 ARTN: D23202.<br />

08.1-72<br />

Alpha-Pinene oxidation in the presence of<br />

seed aerosol: Estimates of nucleation rates,<br />

growth rates, and yield<br />

Verheggen B, Mozurkewich M, Caffrey P, Frick G,<br />

Hoppel W, Sullivan W<br />

Canada, Switzerland, USA<br />

Meteorology & Atmospheric Sciences , Modelling<br />

A recently developed inverse-modeling procedure<br />

has been applied to a case study of particle nucle-


64<br />

ation and growth following alpha-pinene and SO 2<br />

oxidation in a smog chamber. With the use of only<br />

the measured aerosol size distributions as input,<br />

the condensational growth rate is obtained by<br />

regression analysis of the general dynamic equation,<br />

taking into account coagulation and wall<br />

losses. <strong>The</strong> growth rate provides an indirect measure<br />

of the concentration of the condensing species,<br />

offset by their vapor pressures. Assuming a<br />

particle density of 1.0 g cm(-3), an aerosol yield of<br />

7 +/- 1% is obtained for an initial alpha-pinene concentration<br />

of 14 ppbv and a final organic aerosol<br />

mass of 4 µg m(3). Using the estimated vapor concentration,<br />

we show that the time-dependence of<br />

the yield is at least partly due to the time needed<br />

for condensation. Such a kinetic limitation to secondary<br />

organic aerosol formation may have implications<br />

for our understanding of gas-particle<br />

partitioning. <strong>The</strong> measured size distributions are<br />

also used to determine the empirical nucleation<br />

rate; it appears to be enhanced by the presence of<br />

organics.<br />

Environmental Science Technology, 2007, V41,<br />

N17, SEP 1, pp 6046-6051.<br />

08.1-73<br />

Dobson total ozone series of Oxford: Reevaluation<br />

and applications<br />

Vogler C, Brönnimann S, Stähelin J, Griffin R E M<br />

Switzerland, Canada<br />

Meteorology & Atmospheric Sciences , Urban Studies<br />

We have reevaluated the original total ozone measurements<br />

made in Oxford between 1924 and 1957,<br />

with a view to extending backward in time the existing<br />

total ozone series from 1957 to 1975. <strong>The</strong> Oxford<br />

measurements are the oldest Dobson observations<br />

in the world. <strong>The</strong>ir prime importance, when coupled<br />

with the series from Arosa (since 1926) and Tromso<br />

(since 1935), is for increasing basic understanding<br />

of stratospheric ozone and dynamics, while in relation<br />

to studies of the recent ozone depletion they<br />

constitute a baseline of considerable (and unique)<br />

significance and value. However, the reevaluation<br />

was made difficult on account of changes to the instruments<br />

and wavelengths as the early data collection<br />

methods evolved, while unknowns due to the<br />

influence of aerosols and the possible presence of<br />

dioxides of sulphur and nitrogen created additional<br />

problems. Our reevaluation was based on statistical<br />

procedures (comparisons with meteorological upper<br />

air data and ozone series from Arosa) and also<br />

on corrections suggested by Dobson himself. <strong>The</strong><br />

comparisons demonstrate that the data are internally<br />

consistent and of good quality. Nevertheless,<br />

as post-1957 data were not assessed in this study, the<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

series cannot be recommended at present for trend<br />

analysis, though the series can be used for climatological<br />

studies. By supplementing the Oxford data<br />

with other existing series, we present a European total<br />

ozone climatology for 1924-1939, 1950-1965, and<br />

1988-2000 and analyze the data with respect to variables<br />

measuring the strength and the temperature<br />

of the polar vortex.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND20, OCT 26 ARTN: D20116.<br />

08.1-74<br />

Road vehicle emissions of molecular hydrogen<br />

(H-2) from a tunnel study<br />

Vollmer M K, Jürgens N, Steinbacher M, Reimann<br />

S, Weilenmann M, Buchmann B<br />

Switzerland, Germany<br />

Modelling , Meteorology & Atmospheric Sciences<br />

Motor vehicle combustion emissions of molecular<br />

hydrogen (HA carbon monoxide (CO), and carbon<br />

dioxide (CO 2) were measured during a 6-week period<br />

from November 2004 to January 2005 in Gubrist<br />

Tunnel, Switzerland, to determine vehicle emission<br />

factors for these trace gases and the ratios of<br />

the concentration growths Delta H-2/Delta CO and<br />

Delta H-2/Delta CO 2 in the tunnel under real-world<br />

highway driving conditions. For H-2, molar mixing<br />

ratios at the tunnel exit were found to be 7-10ppm<br />

(parts-per-million, 10-6) during rush hours. Mean<br />

emission factors of E-H2=49.7(+/- 16.5)mg km(-1),<br />

E-CO = 1.46(+ /-.54) g km(-1), and E-CO 2, = 266(69)<br />

g km(-1) were calculated. E-H2 was largest during<br />

weekday rush-hour traffic, a consequence of the<br />

more frequent accelerations in congested traffic<br />

when fuel combustion is not optimal. EH, was<br />

smaller for heavy-duty vehicles (HDV) compared to<br />

light-duty vehicles (LDV), a finding which was attributed<br />

to the diesel vs. gasoline engine technology.<br />

<strong>The</strong> mean Delta H-2 /Delta CO molecular ratio<br />

was 0.48 A 0.12. This ratio increased to similar to<br />

0.6 during rush hours, suggesting that H-2 yield is<br />

favored relative to CO under fuel-rich conditions,<br />

presumably a consequence of an increasing contribution<br />

of the water-gas-shift reaction. <strong>The</strong> mean<br />

Delta H-2/Delta CO 2 molecular ratio was 4.4 x 10<br />

(-3) but reduced to 2.5 x 10-3 when the relative HDV<br />

abundance was at maximum. Using three different<br />

approaches, road traffic H 2 emissions were estimated<br />

for 2004 for Switzerland at 5.0-6.6 Gg and<br />

globally at 4.2-8.1 Tg. Despite projections of increasing<br />

traffic, <strong>Swiss</strong> H 2 emissions are not expected to<br />

change significantly in the near future, and global<br />

emissions are likely to decrease due to improved<br />

exhaust gas clean-up technologies.<br />

Atmospheric Environment, 2007, V41, N37, DEC,<br />

pp 8355-8369.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere 65<br />

08.1-75<br />

<strong>The</strong> effect of mountainous topography on<br />

moisture exchange between the “surface” and<br />

the free atmosphere<br />

Weigel A P, Chow F K, Rotach M W<br />

Switzerland, USA<br />

Meteorology & Atmospheric Sciences<br />

Typical numerical weather and climate prediction<br />

models apply parameterizations to describe<br />

the subgrid-scale exchange of moisture, heat and<br />

momentum between the surface and the free<br />

atmosphere. To a large degree, the underlying<br />

assumptions are based on empirical knowledge<br />

obtained from measurements in the atmospheric<br />

boundary layer over flat and homogeneous topography.<br />

It is, however, still unclear what happens if<br />

the topography is complex and steep. Not only is<br />

the applicability of classical turbulence schemes<br />

questionable in principle over such terrain, but<br />

mountains additionally induce vertical fluxes on<br />

the meso-gamma scale. Examples are thermally<br />

or mechanically driven valley winds, which are<br />

neither resolved nor parameterized by climate<br />

models but nevertheless contribute to vertical exchange.<br />

Attempts to quantify these processes and<br />

to evaluate their impact on climate simulations<br />

have so far been scarce. Here, results from a case<br />

study in the Riviera Valley in southern Switzerland<br />

are presented. In previous work, measurements<br />

from the MAP-Riviera field campaign have been<br />

used to evaluate and configure a high-resolution<br />

large-eddy simulation code (ARPS). This model is<br />

here applied with a horizontal grid spacing of 350<br />

m to detect and quantify the relevant exchange<br />

processes between the valley atmosphere (i.e. the<br />

ground “surface” in a coarse model) and the free<br />

atmosphere aloft. As an example, vertical export<br />

of moisture is evaluated for three fair-weather<br />

summer days. <strong>The</strong> simulations show that moisture<br />

exchange with the free atmosphere is indeed<br />

no longer governed by turbulent motions alone.<br />

Other mechanisms become important, such as<br />

mass export due to topographic narrowing or the<br />

interaction of thermally driven cross-valley circulations.<br />

Under certain atmospheric conditions,<br />

these topographical-related mechanisms exceed<br />

the “classical” turbulent contributions a coarse<br />

model would see by several times. <strong>The</strong> study<br />

shows that conventional subgrid-scale parameterizations<br />

can indeed be far off from reality if<br />

applied over complex topography, and that largeeddy<br />

simulations could provide a helpful tool for<br />

their improvement.<br />

Boundary Layer Meteorology, 2007, V125, N2,<br />

NOV, pp 227-244.<br />

08.1-76<br />

Source apportionment of PM2.5 and selected<br />

hazardous air pollutants in Seattle<br />

Wu C F, Larson T V, Wu S Y, Williamson J, Westberg<br />

H H, Liu L J S<br />

Taiwan, USA, Switzerland<br />

Urban Studies , Meteorology & Atmospheric Sciences<br />

, Modelling<br />

<strong>The</strong> potential benefits of combining the speciated<br />

PM2.5 and VOCs data in source apportionment<br />

analysis for identification of additional sources<br />

remain unclear. We analyzed the speciated PM2.5<br />

and VOCs data collected at the Beacon Hill in Seattle,<br />

WA between 2000 and 2004 with the Multilinear<br />

Engine (ME-2) to quantify source contributions<br />

to the mixture of hazardous air pollutants<br />

(HAPs). We used the ‘missing mass’, defined as<br />

the concentration of the measured total particle<br />

mass minus the sum of all analyzed species, as<br />

an additional variable and implemented an auxiliary<br />

equation to constrain the sum of all species<br />

mass fractions to be 100%. Regardless of whether<br />

the above constraint was implemented and/<br />

or the additional VOCs data were included with<br />

the PM2.5 data, the models identified that wood<br />

burning (24%-31%), secondary sulfate (20%-24%)<br />

and secondary nitrate (15%-20%) were the main<br />

contributors to PM2.5. Using only PM2.5 data, the<br />

model distinguished two diesel features with the<br />

100% constraint, but identified only one diesel<br />

feature without the constraint. When both PM2.5<br />

and VOCs data were used, one additional feature<br />

was identified as the major contributor (26%) to<br />

total VOC mass. Adding VOCs data to the speciated<br />

PM2.5 data in source apportionment modeling<br />

resulted in more accurate source contribution<br />

estimates for combustion related sources as evidenced<br />

by the less ‘missing mass’ percentage in<br />

PM2.5. Using the source contribution estimates,<br />

we evaluated the validity of using black carbon<br />

(BC) as a surrogate for diesel exhaust. We found<br />

that BC measured with an aethalometer at 370<br />

nm and 880 nm had reasonable correlations with<br />

the estimated concentrations of diesel particulate<br />

matters (r > 0.7), as well as with the estimated concentrations<br />

of wood burning particles during the<br />

heating seasons (r=0.56-0.66). This indicates that<br />

the BC is not a unique tracer for either source. <strong>The</strong><br />

difference in BC between 370 and 880 nm, however,<br />

correlated well exclusively with the estimated<br />

wood smoke source (r=0.59) and may be used to<br />

separate wood smoke from diesel exhaust. Thus,<br />

when multiple BC related sources exist in the<br />

same monitoring environment, additional data<br />

processing or modeling of the BC measurements


66<br />

is needed before these measurements could be<br />

used to represent the diesel exhaust.<br />

Science of the Total Environment, 2007, V386,<br />

N1-3, NOV 1, pp 42-52.<br />

08.1-77<br />

Gas temperature measurement in thermal radiating<br />

environments using a suction thermocouple<br />

apparatus<br />

Z’graggen A, Friess H, Steinfeld A<br />

Switzerland<br />

Engineering , Instruments & Instrumentation , Meteorology<br />

& Atmospheric Sciences<br />

An experimental methodology is developed for<br />

gas temperature measurements in highly radiating<br />

environments. It consists of a suction thermocouple<br />

apparatus and associated heat transfer<br />

model for determining the gas temperature from<br />

shielded thermocouple readings by radiation,<br />

convection and conduction dimensionless correlations.<br />

<strong>The</strong> apparatus and methodology are calibrated<br />

and applied to measure gas flow temperatures<br />

in a tubular furnace with wall temperatures<br />

up to 1223 K. Results are compared with predictions<br />

by CFD simulations.<br />

Measurement Science Technology, 2007, V18, N11,<br />

NOV, pp 3329-3334.<br />

08.1-78<br />

Air quality modelling over Bogota, Colombia:<br />

Combined techniques to estimate and evaluate<br />

emission inventories<br />

Zarate E, Belalcazar L C, Clappier A, Manzi V, van<br />

den Bergh H<br />

Switzerland, Colombia<br />

Urban Studies , Meteorology & Atmospheric Sciences<br />

, Modelling<br />

Two versions of the Emission Inventory (EI) are<br />

generated for the city of Bogota, Colombia. In the<br />

first version (EI-1), CORINAIR traffic emission factors<br />

(EFs) are used. In the second (EI-2), bulk traffic<br />

EF’s calculated for the city, using in situ measurements<br />

and inverse modelling techniques at street<br />

level, are used. EI-2 traffic emissions are 5, 4 and<br />

3 times bigger than the corresponding values in<br />

EI-1, for CO, PM10 and NMVOCs, respectively. <strong>The</strong><br />

main goal of this study consists in evaluating the<br />

two versions of the El when introduced into a mesoscale<br />

air quality model. <strong>The</strong> AOT (accumulated<br />

exposure over a threshold) index is calculated for<br />

comparison between observed and simulated concentrations<br />

of primary pollutants. Simulated concentrations<br />

using EI-2 are closer to the observed<br />

values. This comparison allows us to extract some<br />

conclusions of the methodology used to calculate<br />

the EFs. Local factors like the driving behavior,<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Atmosphere<br />

the altitude, vehicle technology and an aged fleet<br />

cannot be totally included and corrected in the<br />

standard methodologies, and seem to be more<br />

important than obtaining very detailed and precise<br />

information on the classification of the fleet<br />

or driving speeds. Under financially limited and<br />

fast changing situations, as in the case of many<br />

developing countries, a simple methodology to estimate<br />

bulk traffic Ef’s and to evaluate the Ell, is<br />

of utmost importance. <strong>The</strong> use of combined techniques<br />

such as in situ measurements to estimate<br />

bulk traffic EFs, and further evaluation of the inventories<br />

with numerical models, proved to be a<br />

useful too) for this purpose.<br />

Atmospheric Environment, 2007, V41, N29, SEP, pp<br />

6302-6318.<br />

08.1-79<br />

Ubiquity and dominance of oxygenated species<br />

in organic aerosols in anthropogenicallyinfluenced<br />

Northern Hemisphere midlatitudes<br />

Zhang Q, Jimenez J L, Canagaratna M R, Allan J D,<br />

Coe H, Ulbrich I, Alfarra M R, Takami A, Middlebrook<br />

A M, Sun Y L, Dzepina K, Dunlea E, Docherty<br />

K, Decarlo P F, Salcedo D, Onasch T, Jayne J T,<br />

Miyoshi T, Shimono A, Hatakeyama S, Takegawa<br />

N, Kondo Y, Schneider J, Drewnick F, Borrmann<br />

S, Weimer S, Demerjian K L, Williams P, Bower K,<br />

Bahreini R, Cottrell L, Griffin R J, Rautiainen J, Sun J<br />

Y, Zhang Y M, Worsnop D R<br />

USA, Switzerland, England, Germany, Japan, Finland,<br />

Mexico, Peoples R China<br />

Urban Studies , Meteorology & Atmospheric Sciences<br />

(1) Organic aerosol (OA) data acquired by the Aerosol<br />

Mass Spectrometer (AMS) in 37 field campaigns<br />

were deconvolved into hydrocarbon-like OA (HOA)<br />

and several types of oxygenated OA (OOA) components.<br />

HOA has been linked to primary combustion<br />

emissions (mainly from fossil fuel) and other<br />

primary sources such as meat cooking. OOA is<br />

ubiquitous in various atmospheric environments,<br />

on average accounting for 64%, 83% and 95% of<br />

the total OA in urban, urban downwind, and rural/remote<br />

sites, respectively. A case study analysis<br />

of a rural site shows that the OOA concentration is<br />

much greater than the advected HOA, indicating<br />

that HOA oxidation is not an important source of<br />

OOA, and that OOA increases are mainly due to<br />

SOA. Most global models lack an explicit representation<br />

of SOA which may lead to significant biases<br />

in the magnitude, spatial and temporal distributions<br />

of OA, and in aerosol hygroscopic properties.<br />

Geophysical Research Letters, 2007, V34, N13, JUL<br />

7 ARTN: L13801.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 67<br />

1.2 Terrestrial Ecosystems<br />

08.1-80<br />

<strong>The</strong> <strong>Swiss</strong> agri-environment scheme enhances<br />

pollinator diversity and plant reproductive success<br />

in nearby intensively managed farmland<br />

Albrecht M, Duelli P, Müller C, Kleijn D, Schmid B<br />

Switzerland, Netherlands<br />

Agriculture, Soil Sciences , Forestry , Biodiversity ,<br />

Zoology , Ecology , Plant Sciences<br />

1. Agri-environment schemes attempt to counteract<br />

the loss of biodiversity and associated ecosystem<br />

services such as pollination and natural<br />

pest control in agro-ecosystems. However, only<br />

a few studies have evaluated whether these attempts<br />

are successful. 2. We studied the effects<br />

of managing meadows according to the prescriptions<br />

of ecological compensation areas (ECA), the<br />

most widely adopted agri-environment scheme in<br />

Switzerland, on both pollinator species richness<br />

and abundance, and the reproductive success of<br />

plants in nearby intensively managed meadows<br />

(IM). 3. We established arrays of four pots, each<br />

containing individuals of three insect-pollinated,<br />

non-autogamous ‘phytometer’ species (Raphanus<br />

sativus, Hypochaeris radicata and Campanula<br />

glomerata), in ECA and adjacent IM at increasing<br />

distances from the ECA at 13 sites. 4. Species richness<br />

and abundance of hoverflies, solitary bees<br />

and large-sized pollinators (mainly social bees<br />

and butterflies) were significantly higher in ECA<br />

than in adjacent IM. Species richness and abundance<br />

of small-sized pollinators in IM declined<br />

significantly with increasing distance from ECA,<br />

whereas large-sized pollinators were not significantly<br />

affected by distance. Plant species richness<br />

and flower abundance were the major drivers of<br />

pollinator species richness and abundance; the<br />

area of an ECA had no significant influence. 5.<br />

Individual plants of R. sativus and C. glomerata<br />

produced more and heavier seeds in ECA than in<br />

IM. Furthermore, the number of seeds of these<br />

two phytometer species was positively correlated<br />

with species richness and abundance of bees. No<br />

such effects were observed for individual plants<br />

of H. radicata. <strong>The</strong> number of fruits and seeds per<br />

plant of R. sativus in IM decreased with increasing<br />

distance from ECA. 6. Synthesis and applications.<br />

We conclude that establishing ECA is an effective<br />

method of enhancing both pollinator species<br />

richness and abundance and pollination services<br />

to nearby intensely managed farmland. Our<br />

study emphasizes the importance of connectivity<br />

between ECA in maintaining diverse pollinator<br />

communities and thereby providing pollination<br />

services in agricultural landscapes.<br />

Journal of Applied Ecology, 2007, V44, N4, AUG,<br />

pp 813-822.<br />

08.1-81<br />

Interaction diversity within quantified insect<br />

food webs in restored and adjacent intensively<br />

managed meadows<br />

Albrecht M, Duelli P, Schmid B, Müller C B<br />

Switzerland<br />

Ecology , Biodiversity , Agriculture, Soil Sciences ,<br />

Zoology<br />

1. We studied the community and food-web structure<br />

of trap-nesting insects in restored meadows<br />

and at increasing distances within intensively<br />

managed grassland at 13 sites in Switzerland to<br />

test if declining species diversity correlates with<br />

declining interaction diversity and changes in<br />

food-web structure. 2. We analysed 49 quantitative<br />

food webs consisting of a total of 1382 trophic<br />

interactions involving 39 host/prey insect species<br />

and 14 parasitoid/predator insect species. Species<br />

richness and abundance of three functional<br />

groups, bees and wasps as the lower trophic level<br />

and natural enemies as the higher trophic level,<br />

were significantly higher in restored than in adjacent<br />

intensively managed meadows. Diversity and<br />

abundance of specific trophic interactions also<br />

declined from restored to intensively managed<br />

meadows. 3. <strong>The</strong> proportion of attacked brood<br />

cells and the mortality of bees and wasps due to<br />

natural enemies were significantly higher in restored<br />

than in intensively managed meadows. Bee<br />

abundance and the rate of attacked brood cells of<br />

bees declined with increasing distance from restored<br />

meadows. <strong>The</strong>se findings indicate that interaction<br />

diversity declines more rapidly than species<br />

diversity in our study system. 4. Quantitative<br />

measures of food-web structure (linkage density,<br />

interaction diversity, interaction evenness and<br />

compartment diversity) were higher in restored<br />

than in intensively managed meadows. This was<br />

reflected in a higher mean number of host/prey<br />

species per consumer species (degree of generalism)<br />

in restored than in intensively managed<br />

meadows. 5. <strong>The</strong> higher insect species and interaction<br />

diversity was related to higher plant species<br />

richness in restored than in intensively managed<br />

meadows. In particular, bees and natural enemies<br />

reacted positively to increased plant diversity. 6.<br />

Our findings provide empirical evidence for the<br />

theoretical prediction that decreasing species<br />

richness at lower trophic levels should reduce<br />

species richness at higher trophic levels, and in<br />

addition lead to even stronger reductions in interaction<br />

diversity at these higher levels. Species at<br />

higher trophic levels may thus benefit relatively<br />

more than species at lower trophic levels from<br />

habitat restoration in the grassland ecosystems<br />

studied. We also demonstrate enhanced compart-


68<br />

ment diversity and lower interaction evenness in<br />

restored than in intensively managed meadows,<br />

both of which are theoretically positively associated<br />

with increased ecosystem stability in restored<br />

meadows.<br />

Journal of Animal Ecology, 2007, V76, N5, SEP, pp<br />

1015-1025.<br />

08.1-82<br />

Sustaining agricultural production and food<br />

security in Southern Africa: an improved role<br />

for climate prediction?<br />

Archer E, Mukhala E, Walker S, Dilley M, Masamvu K<br />

South Africa, Botswana, Switzerland<br />

Agriculture, Soil Sciences , Meteorology & Atmospheric<br />

Sciences , Ecology , Social Sciences<br />

Livelihoods and household food security in the<br />

Southern African region can be extremely vulnerable<br />

to the negative effects of climate stress<br />

as shown by the 2002-2004 ‘complex emergency.’<br />

Climate prediction may prove a valuable resource<br />

in mitigating these effects. If climate prediction is<br />

applied successfully, it may be able to help guide<br />

responses in populations at risk to reduce vulnerability<br />

to climate stress. <strong>The</strong> study presented here<br />

seeks to understand what would constitute an improved<br />

role for climate prediction in contributing<br />

to sustaining agricultural production and food<br />

security in Southern Africa. Investigation undertaken<br />

during the 2002/2003 rainy season under regional<br />

conditions of elevated disaster risk shows,<br />

however, that a number of weaknesses and gaps<br />

persistently characterize climate information<br />

systems in the Southern African region, and constrain<br />

such systems’ ability to benefit key sectors,<br />

particularly agriculture. <strong>The</strong> stakeholder identification<br />

of such gaps forms the basis for distilling<br />

concrete recommendations to improve process<br />

and organizational efficiency. Such recommendations,<br />

while developmental, should better enable<br />

institutions and stakeholders involved in climate<br />

prediction to fulfill their potential in supporting<br />

development of successful adaptation strategies<br />

in populations and sectors at risk.<br />

Climatic <strong>Change</strong>, 2007, V83, N3, AUG, pp<br />

287-300.<br />

08.1-83<br />

Importance of ecological compensation areas<br />

for small mammals in intensively farmed areas<br />

Aschwanden J, Holzgang O, Jenni L<br />

Switzerland<br />

Agriculture, Soil Sciences , Ecology , Zoology<br />

Small mammals make up an important link in the<br />

food chain as many predator species feed on them.<br />

<strong>The</strong>re are indications that small mammal popula-<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

tions in Europe are declining due to the intensification<br />

of agriculture. According to national legislation,<br />

farmers in Switzerland have to cultivate at<br />

least 7% of their land as ecological compensation<br />

areas and, thus, some alternative habitats that are<br />

possibly beneficial for small mammals have been<br />

created. In this study, we estimated the diversity<br />

and density of small mammals on two types of<br />

conventional farmland field types (artificial grassland<br />

and autumn-sown wheat) and three types of<br />

ecological compensation areas (wild-flower strips,<br />

herbaceous strips and low-intensity meadows) by<br />

use of capture-recapture in March, May and July<br />

2003. <strong>The</strong> common vole Microtus arvalis was the<br />

most abundant and predominant species in all<br />

habitat types except in herbaceous strips, which<br />

harboured the highest diversity with six species<br />

caught. In March the density of small mammals<br />

was generally very low, but significantly higher<br />

in wild-flower (mainly due to common vole) and<br />

herbaceous strips than in the other habitat types.<br />

In wild-flower and herbaceous strips, densities increased<br />

strongly from March to May and in July.<br />

On autumn-sown wheat fields, a strong increase<br />

occurred only from May to July and was caused<br />

by common vole. On artificial grassland and lowintensity<br />

meadows, densities of small mammals<br />

(mainly common vole) increased only marginally<br />

with low-intensity meadows supporting slightly<br />

higher densities. Thus, habitats that were not<br />

mown each year supported the highest densities<br />

of small mammals. This demonstrates that ecological<br />

compensation areas, such as wild-flower<br />

and herbaceous strips, make up an important refuge<br />

for small mammals. <strong>The</strong>y probably also have<br />

positive effects on populations of many predator<br />

species that depend on small mammals, particularly<br />

if a mosaic with mown surfaces is created.<br />

Wildlife Biology, 2007, V13, N2, JUN, pp 150-158.<br />

08.1-84<br />

Effects of agri-environmental measures, site<br />

and landscape conditions on butterfly diversity<br />

of <strong>Swiss</strong> grassland<br />

Aviron S, Jeanneret P, Schüpbach B, Herzog F<br />

Switzerland<br />

Agriculture, Soil Sciences , Ecology , Biodiversity<br />

Agri-environment schemes (AES) were introduced<br />

in Europe to mitigate the loss of biodiversity in<br />

cultivated landscapes. In Switzerland, farmers<br />

have to convert 7% of the arable land into ecological<br />

compensation areas (ECA) in order to enhance<br />

biodiversity, low-input grassland making up the<br />

major part of ECA. This study investigated during<br />

6 years the effect of ECA grassland on butterfly diversity<br />

at the field and the landscape scales in two


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 69<br />

farming landscape units of the <strong>Swiss</strong> Plateau. Butterfly<br />

diversity was compared between low-input<br />

and conventional grasslands, controlling for potential<br />

influence of local site conditions and landscape<br />

context of grasslands. Low-input management<br />

of ECA grasslands had a significant impact<br />

on butterfly communities, but ECA and conventional<br />

grasslands differed more in the composition<br />

of species assemblages than in the number of<br />

butterfly species. <strong>The</strong> typical butterfly assemblages<br />

on ECA grassland might be linked to the slightly<br />

higher plant species richness due to management<br />

restrictions. However, the effectiveness of ECA<br />

grassland for promoting butterfly diversity varied<br />

according to local site conditions (field slope and<br />

orientation) and to the amount of ECA and seminatural<br />

elements in the surrounding landscape.<br />

Thus, the present study underlines the necessity<br />

to account for such environmental variation at<br />

multiple scales to be able to detect and interpret<br />

effects of AES. Nevertheless, our results suggest<br />

that additional restoration measures should be<br />

adopted. Especially, the ECA scheme should promote<br />

a connected network of ECA grasslands and<br />

semi-natural habitats at the landscape scale.<br />

Agriculture Ecosystems Environment, 2007, V122,<br />

N3, NOV, pp 295-304.<br />

08.1-85<br />

Conservation of butterfly populations in dynamic<br />

landscapes: <strong>The</strong> role of farming practices<br />

and landscape mosaic<br />

Aviron S, Kindlmann P, Burel F<br />

Switzerland, France, Czech Republic<br />

Agriculture, Soil Sciences , Ecology , Biodiversity ,<br />

Modelling , Zoology<br />

In a dynamic landscape the rate of change in landscape<br />

structure can be even more important than<br />

the degree of patch isolation in determining population<br />

survival and abundance. If the changes in<br />

landscape structure occur at an “extremely” high<br />

rate (as in some anthropogenic changes), dispersal<br />

may not be able to keep up with the high rates of<br />

local extinction. Understanding impacts of such<br />

changes is thus crucial for determination of the<br />

driving factors for species survival in agricultural<br />

landscapes and for elaboration of conservation<br />

plans. Here we studied the effects of landscape<br />

dynamics under local farming practices on movements<br />

and population dynamics of a diurnal butterfly<br />

Maniola jurtina L. (Satyridae), specifically<br />

the impacts of regular yearly mowing on butterfly<br />

movements, distribution and abundance<br />

over many years. We used an existing simulation<br />

model, extended it by the effect of the intensity of<br />

disturbance (amount of mown habitat) and tim-<br />

ing of disturbance within the reproductive season<br />

on the butterfly population dynamics, and validated<br />

on our data from a field experiment using<br />

a mark-release method. Increase in the amount of<br />

disturbed habitats in the landscape led to an increasing<br />

isolation of the remnant habitat patches<br />

for butterflies. This resulted in decreasing movements<br />

between habitat patches and ultimately to<br />

population decline, especially in less accessible<br />

patches. In the past, influence of landscape dynamics<br />

on species survival was usually considered at<br />

the long-term scale. our results demonstrate that<br />

the short time scale landscape dynamics induced<br />

by farming practices should not be neglected. <strong>The</strong><br />

novelty of this paper stems in the combination<br />

of inclusion of landscape dynamics, of realistic<br />

dispersal strategies of individuals, and of considering<br />

real landscapes. <strong>The</strong> effect of man-induced<br />

landscape changes on population persistence of a<br />

real species in a real landscape has not been possible<br />

to be studied by any of the previously developed<br />

models.<br />

Ecological Modelling, 2007, V205, N1-2, JUL 10,<br />

pp 135-145.<br />

08.1-86<br />

Nitrogen deposition but not ozone affects<br />

productivity and community composition of<br />

subalpine grassland after 3 yr of treatment<br />

Bassin S, Volk M, Suter M, Buchmann N, Fuhrer J<br />

Switzerland<br />

Biodiversity , Ecology , Meteorology & Atmospheric<br />

Sciences , Plant Sciences<br />

A field experiment was established at 2000 m above<br />

sea level (asl) in the central <strong>Swiss</strong> Alps with the aim<br />

of investigating the effects of elevated ozone (O-3)<br />

and nitrogen deposition (N), and of their combination,<br />

on above-ground productivity and species<br />

composition of subalpine grassland. One hundred<br />

and eighty monoliths were extracted from a<br />

species-rich Geo-Montani-Nardetum pasture and<br />

exposed in a free-air O-3-fumigation system to one<br />

of three concentrations of O-3 (ambient, 1.2 x ambient,<br />

1.6 x ambient) and five concentrations of<br />

additional N. Above-ground biomass, proportion<br />

of functional groups and normalized difference<br />

vegetation index (NDVI) were measured annually.<br />

After 3 yr of treatment, the vegetation responded<br />

to the N input with an increase in above-ground<br />

productivity and altered species composition, but<br />

without changes resulting from elevated O-3. N<br />

input > 10 kg N ha(-1) yr(-1) was sufficient to affect<br />

the composition of functional groups, with<br />

sedges benefiting over-proportionally. No interaction<br />

of O-3 x N was observed, except for NDVI;<br />

positive effects of N addition on canopy greenness


70<br />

were counteracted by accelerated leaf senescence<br />

in the highest O-3 treatment. <strong>The</strong> results suggest<br />

that effects of elevated O-3 on the productivity<br />

and floristic composition of subalpine grassland<br />

may develop slowly, regardless of the sensitive response<br />

to increasing N.<br />

New Phytologist, 2007, V175, N3, pp 523-534.<br />

08.1-87<br />

Volcanic explosive eruptions of the Vesuvio<br />

decrease tree-ring growth but not photosynthetic<br />

rates in the surrounding forests<br />

Battipaglia G, Cherubini P, Saurer M, Siegwolf R T<br />

W, Strumia S, Cotrufo M F<br />

Switzerland, Italy<br />

Plant Sciences , Forestry , Meteorology & Atmospheric<br />

Sciences<br />

Volcanic eruptions impact the global and the<br />

hemispheric climate, but it is still unknown how<br />

and to what degree they force the climate system<br />

and in particular the global carbon cycle. In this<br />

paper, the relationships between individual eruptions<br />

(reconstructed for the past using written records),<br />

tree primary productivity (estimated using<br />

ring widths), photosynthetic rate and stomatal<br />

conductance (assessed by carbon and oxygen isotope<br />

data) are investigated, to understand the impact<br />

of volcanic eruptions on net primary production.<br />

Data from a mixed stand of Fagus sylvatica<br />

L. and Acer pseudoplatanus L. located in the area<br />

of the Vesuvio volcanic complex (Southern Italy)<br />

showed a significant decrease in ring width following<br />

each eruption. Isotope analyses indicate a<br />

change in climatic conditions after such events.<br />

Specifically, the lower oxygen isotope ratio in the<br />

tree-ring cellulose strongly suggests an increase in<br />

relative humidity and a decrease in temperature,<br />

with the latter resulting in a strong limitation<br />

to tree-ring growth. <strong>The</strong> carbon isotope ratio was<br />

only moderately but not significantly reduced in<br />

the years of volcanic eruption, suggesting no major<br />

changes in C fixation rates. This work is a case<br />

study on the effects of volcanic eruptions resulting<br />

in strong climatic changes on the local scale.<br />

This is an opportunity to explore the process and<br />

causal relationships between climatic changes<br />

and the response of the vegetation. Thus, we propose<br />

here a realistic model scenario, from which<br />

we can extrapolate to global scales and improve<br />

our interpretations of results of global studies.<br />

<strong>Global</strong> <strong>Change</strong> Biology, 2007, V13, N6, JUN, pp<br />

1122-1137.<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

08.1-88<br />

Intensified grazing affects endemic plant and<br />

gastropod diversity in alpine grasslands of the<br />

Southern Carpathian mountains (Romania)<br />

Baur B, Cremene C, Groza C, Schileyko A A, Baur<br />

A, Erhardt A<br />

Switzerland, Romania, Russia<br />

Plant Sciences , Biodiversity , Ecology , Zoology<br />

Alpine grasslands in the Southern Carpathian<br />

Mts, Romania, harbour an extraordinarily high<br />

diversity of plants and invertebrates, including<br />

Carpathic endemics. In the past decades, intensive<br />

sheep grazing has caused a dramatic decrease<br />

in biodiversity and even led to eroded soils at<br />

many places in the Carpathians. Because of limited<br />

food resources, sheep are increasingly forced<br />

to graze on steep slopes, which were formerly not<br />

grazed by livestock and are considered as local<br />

biodiversity hotspots. We examined species richness,<br />

abundance and number of endemic vascular<br />

plants and terrestrial gastropods on steep slopes<br />

that were either grazed by sheep or ungrazed by<br />

livestock in two areas of the Southern Carpathians.<br />

On calcareous soils in the Bucegi Mts, a total<br />

of 177 vascular plant and 19 gastropod species<br />

were recorded. Twelve plant species (6.8%) and<br />

three gastropod species (15.8%) were endemic to<br />

the Carpathians. Grazed sites had lower plant and<br />

gastropod species richness than ungrazed sites.<br />

Furthermore, grazed sites harboured fewer gastropod<br />

species endemic to the Carpathians than<br />

ungrazed sites. On acid soils in the Fagaras Mts, a<br />

total of 96 vascular plant and nine gastropod species<br />

were found. In this mountain area, however,<br />

grazed and ungrazed sites did not differ in species<br />

richness, abundance and number of endemic<br />

plant and gastropod species. Our findings confirm<br />

the high biodiversity of grasslands on steep slopes<br />

in the Southern Carpathian Mts and caution<br />

against increasing grazing pressure in these refuges<br />

for relic plants and gastropods as well as for<br />

other invertebrates.<br />

Biologia, 2007, V62, N4, AUG, pp 438-445.<br />

08.1-89<br />

Effect of rock climbing on the calcicolous<br />

lichen community of limestone cliffs in the<br />

northern <strong>Swiss</strong> Jura Mountains<br />

Baur B, Froeberg L, Müller S W<br />

Switzerland, Sweden<br />

Plant Sciences , Ecology<br />

Exposed limestone cliffs in the <strong>Swiss</strong> Jura Mountains<br />

harbour a diverse lichen community with<br />

some rare species. Sport climbing has recently<br />

increased in popularity on these cliffs. We examined<br />

the effect of sport climbing on calcicolous


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 71<br />

lichens by assessing species diversity and cover<br />

of lichens in climbed and unclimbed areas of 10<br />

isolated cliffs in the northern <strong>Swiss</strong> Jura Mountains.<br />

We also investigated possible associations<br />

between lichens and lichen-feeding land snails on<br />

these cliffs. A total of 38 calcicolous lichen species,<br />

three bryophytes and one alga were found on<br />

the rock faces of 10 cliffs. Twenty lichen species<br />

(52.6%) were epilithic, 16(42.1%) endolithic and<br />

two (5.3%) foliose. Overall, the epilithic lichen species<br />

covered 8.3% of the rock surface, endolithic<br />

species 10.2%, and foliose species 0.03%. Climbed<br />

and unclimbed rock areas did not differ in total<br />

number of lichen species, species density (number<br />

of species per 100 cm(2)) or total lichen cover. However,<br />

the frequency of occurrence of epilithic lichens<br />

was lower along climbing routes than in unclimbed<br />

areas. A multi-response permutation test<br />

showed that the lichen community composition<br />

of climbed areas differed from that of unclimbed<br />

areas. <strong>The</strong> dissimilarity of lichen communities<br />

between climbed and unclimbed areas increased<br />

with increasing climbing intensity on the focal<br />

route in climbed areas, but not with the age of the<br />

climbing route. Five of the 11 snail species recorded<br />

on the cliff faces were specialized lichen feeders.<br />

Plots along climbing routes harboured fewer<br />

snail species than plots in unclimbed areas. Total<br />

snail abundance was positively correlated with lichen<br />

species richness, but no correlation between<br />

snail species richness and lichen species richness<br />

was found. Our results indicate that frequent rock<br />

climbing can change the lichen community and<br />

reduce the snail community of limestone cliffs.<br />

A climbing-related reduction of snail abundance<br />

may also alter the lichen-herbivore interaction<br />

and indirectly change competitive interactions<br />

among lichen species.<br />

Nova Hedwigia, 2007, V85, N3-4, NOV, pp<br />

429-444.<br />

08.1-90<br />

Evaluating macrolichens and environmental<br />

variables as predictors of the diversity of epiphytic<br />

microlichens<br />

Bergamini A, Stofer S, Bolliger J, Scheidegger C<br />

Switzerland<br />

Biodiversity , Ecology , Forestry , Plant Sciences<br />

In contrast to the frequently assessed macrolichens,<br />

microlichens are rarely considered in biodiversity<br />

assessments despite their high species<br />

richness. Microlichens require generally a higher<br />

species identification effort than macrolichens.<br />

Thus, microlichens are more expensive to assess.<br />

Here we evaluate if macrolichen richness can be<br />

used as an indicator of total and threatened mi-<br />

crolichen richness. Furthermore, we tested if different<br />

sets of environmental variables (modelled<br />

climatic variables, forest structure, altitude, etc.)<br />

improve the regression models based on macrolichens<br />

only or even replace the macrolichens as<br />

predictors. Multiple linear regressions were used<br />

to model species richness of microlichens, and<br />

Poisson regressions for threatened microlichens.<br />

On 237 forest plots (200 m(2)) distributed randomly<br />

across Switzerland, 77 macrolichens and 219<br />

microlichens occurred. Macrolichen richness was<br />

positively related to the richness of microlichens.d.<br />

= 0-27) and, in combination with threatened macrolichens<br />

as an additional predictor, also to the<br />

number of threatened microlichens (R-dev(2) =<br />

0.14). Environmental variables alone and in different<br />

combinations explained between 0.20 and<br />

0.41 (R-adj.(2)) of the total variation of microlichen<br />

richness, and between 0.09 and 0.29 (R-dev.(2)) of<br />

the total variation of threatened microlichen<br />

richness. All models based on environmental variables<br />

were considerably improved when macrolichens<br />

were included. Furthermore, macrolichen<br />

richness turned out to be the most important variable<br />

in explaining species richness of all, as well<br />

as threatened microlichens. <strong>The</strong> best models for<br />

total microlichen richness reached a R-2 of 0.56.<br />

Threatened microlichens were more difficult to<br />

model with the best model reaching a R-dev.(2) of<br />

0.29. We conclude that in biodiversity assessments<br />

with scarce resources, lichen sampling could be<br />

focused on the better known macrolichens, at<br />

least in many temperate lowland and mountain<br />

forests. In combination with environmental variables,<br />

reliable predictions of microlichen richness<br />

can be expected. If the focus is on threatened microlichens,<br />

however, models were not reliable and<br />

specialized taxonomists are necessary to assess<br />

these species in the field.<br />

Lichenologist, 2007, V39, 5, pp 475-489.<br />

08.1-91<br />

Which species will succesfully track climate<br />

change? <strong>The</strong> influence of intraspecific competition<br />

and density dependent dispersal on<br />

range shifting dynamics<br />

Best A S, Johst K, Münkemüller T, Travis J M J<br />

Germany, Switzerland, Scotland<br />

Modelling , Meteorology & Atmospheric Sciences ,<br />

Ecology , Biodiversity<br />

Understanding the ability of species to shift their<br />

geographic range is of considerable importance<br />

given the current period of rapid climate change.<br />

Furthermore, a greater understanding of the spatial<br />

population dynamics underlying range shifting<br />

is required to complement the advances made


72<br />

in climate niche modelling. A simulation model is<br />

developed which incorporates three key features<br />

that have been largely overlooked in studies of<br />

range shifting dynamics: the form of intraspecific<br />

competition, density dependent dispersal and<br />

the transient dynamics of habitat patches. <strong>The</strong><br />

results show that the exact shape of the response<br />

depends critically on both local and patch dynamics.<br />

Species whose intraspecific competition<br />

is contest based are more vulnerable than those<br />

whose competition is scramble based. Contesters<br />

are especially sensitive when combined with<br />

density dependent dispersal. Species living in<br />

patches whose carrying capacity grows slowly are<br />

also susceptible to rapid shifts of environmental<br />

conditions. A complementary analytic approach<br />

further highlights the importance of intraspecific<br />

competition.<br />

Oikos, 2007, V116, N9, SEP, pp 1531-1539.<br />

08.1-92<br />

Drought induces lagged tree mortality in a<br />

subalpine forest in the Rocky Mountains<br />

Bigler C, Gavin D G, Gunning C, Veblen T T<br />

Switzerland, USA<br />

Plant Sciences , Forestry , Ecology<br />

Extreme climatic events are key factors in initiating<br />

gradual or sudden changes in forest ecosystems<br />

through the promotion of severe, treekilling<br />

disturbances such as fire, blowdown, and<br />

widespread insect outbreaks. In contrast to these<br />

climatically-incited disturbances, little is known<br />

about the more direct effect of drought on tree<br />

mortality, especially in high-elevation forests.<br />

<strong>The</strong>refore projections of drought-induced mortality<br />

under future climatic conditions remain<br />

uncertain. For a subalpine forest landscape in the<br />

Rocky Mountains of northern Colorado (USA), we<br />

quantified lag effects of drought on mortality of<br />

Engelmann spruce Picea engelmannii, subalpine<br />

fir Abies lasiocarpa, and lodgepole pine Pinus contorta.<br />

For the period 1910-2004, we related death<br />

dates of 164 crossdated dead trees to early-season<br />

and late-season droughts. Following early- season<br />

droughts, spruce mortality increased over five<br />

years and fir mortality increased sharply over<br />

11 years. Following late-season droughts, spruce<br />

showed a small increase in mortality within one<br />

year, whereas fir showed a consistent period of<br />

increased mortality over two years. Pine mortality<br />

was not affected by drought. Low pre- drought<br />

radial growth rates predisposed spruce and fir to<br />

drought- related mortality. Spruce and fir trees<br />

that died during a recent drought (2000-2004) had<br />

significantly lower pre-drought growth rates than<br />

live neighbour trees. Overall, we found large inter-<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

specific differences in drought-related mortality<br />

with fir showing the strongest effect followed by<br />

spruce and pine. This direct influence of climatic<br />

variability on differential tree mortality has the<br />

potential for driving large-scale changes in subalpine<br />

forests of the Rocky Mountains.<br />

Oikos, 2007, V116, N12, DEC, pp 1983-1994.<br />

08.1-93<br />

Conservation of high-altitude wetlands: 368<br />

experiences of the WWF network<br />

Biksham G<br />

Switzerland<br />

Biodiversity , Ecology<br />

Mountain Research and Development, 2007, V27,<br />

N4, NOV, pp 368-371.<br />

08.1-94<br />

Restoration of montane fen meadows by<br />

mowing remains possible after 4-35 years of<br />

abandonment<br />

Billeter R, Peintinger M, Diemer M<br />

Switzerland<br />

Ecology , Biodiversity , Agriculture, Soil Sciences ,<br />

Plant Sciences<br />

<strong>The</strong> abandonment of management in <strong>Swiss</strong> fen<br />

meadows has reduced their plant species diversity<br />

and the fitness of some typical fen species. We examined<br />

whether the resumption of mowing can<br />

reverse these effects, and if so, which mechanisms<br />

are responsible for community change; we also<br />

tested whether restoration success depends on the<br />

duration since abandonment. Experimental mowing<br />

was applied to 15 montane fen meadows of<br />

NE Switzerland that had been abandoned for 4-35<br />

years. After two years of mowing, plant species<br />

richness was 11 % higher in mown plots (2 m(2))<br />

than in fallow plots, approaching levels of neighbouring<br />

continuously managed fen meadows. In<br />

particular, experimental mowing significantly increased<br />

the number of fen indicator species (+15<br />

%) as well as herbs and woody species (seedlings<br />

and saplings), while grass, sedge and rush species<br />

richness was not affected. Mowing had little<br />

effect on aboveground biomass, but strongly reduced<br />

litter mass (-50%) and canopy height (-20%).<br />

Seedling densities of two common species showed<br />

opposite responses to mowing: they increased in<br />

Carex davalliana and decreased in Succisa pratensis,<br />

approaching values of continuously mown<br />

fen meadows. Duration since abandonment had<br />

no significant effect on any of the variables. Our<br />

results demonstrate a rapid recovery of montane<br />

fen plant communities irrespective of the duration<br />

since abandonment (up to 35 years). We<br />

conclude that the restoration of pre-fallow plant


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 73<br />

community composition is likely to be successful<br />

if site conditions (hydrology, nutrient status) remain<br />

intact and if common habitat specialists are<br />

still present in the vegetation and/or seed bank.<br />

Botanica Helvetica, 2007, V117, N1, JUN, pp 1-13.<br />

08.1-95<br />

Dynamics in debris-flow activity on a forested<br />

cone - A case study using different dendroecological<br />

approaches<br />

Bollschweiler M, Stoffel M, Schneuwly D M<br />

Switzerland<br />

Forestry , Plant Sciences , Geomorphology<br />

Dendrogeomorpho logical analyses of trees affected<br />

by debris flows have regularly been used to<br />

date past events. However, this method has always<br />

been limited to forested cones where trees registered<br />

the impact of previous events. <strong>The</strong> minimum<br />

age dating of trees growing in the debris<br />

deposits can, in contrast, provide information on<br />

the latest possible moment of past activity. In this<br />

paper, we report on results obtained from a combination<br />

of these two approaches on a forested<br />

cone in the Valais Alps (Switzerland). A detailed<br />

geomorphic map in a scale of 1: 1000 served as a<br />

basis for the sampling strategy. Disturbed Larix<br />

decidua Mill. and Picea abies (L.) Karst. trees growing<br />

in the deposits allowed reconstruction of 49<br />

events between AD 1782 and 2005 as well as the<br />

determination of the spatial extent of events. In<br />

the debris-flow channels where survivor trees are<br />

missing, we selected the oldest post-event trees<br />

and assessed their age by counting their growth<br />

rings. Missing rings due to lack of center as well<br />

as to sampling height were added so as to determine<br />

real tree age. <strong>The</strong> combination of the dendrogeomorphological<br />

event reconstruction with<br />

the assessment of germination dates of successor<br />

trees allowed realistic approximation of the<br />

minimum time elapsed since the last debris-flow<br />

activity in 23 of the 29 channels present on the<br />

current-day cone surface. In general, channels in<br />

the northern part of the cone and those close to<br />

the currently active channel generally show signs<br />

of (sub-) recent activity with one last overbank sedimentation<br />

event in the 1980s, whereas signs of<br />

debris-flow activity are absent from the channels<br />

in the outermost part since the late 19th century.<br />

As a consequence of the deeply incised channel<br />

and the stabilization measures undertaken along<br />

the banks, signs of debris flows are missing in the<br />

tree-ring record for the past two decades.<br />

Catena, 2008, V72, N1, JAN 1, pp 67-78.<br />

08.1-96<br />

Methanol exchange between grassland and<br />

the atmosphere<br />

Brunner A, Ammann C, Neftel A, Spirig C<br />

Switzerland<br />

Agriculture, Soil Sciences , Plant Sciences , Meteorology<br />

& Atmospheric Sciences , Ecology<br />

Concentrations and fluxes of methanol were measured<br />

above two differently managed grassland<br />

fields (intensive and extensive) in central Switzerland<br />

during summer 2004. <strong>The</strong> measurements<br />

were performed with a proton-transfer-reaction<br />

mass-spectrometer and fluxes were determined by<br />

the eddy covariance method. <strong>The</strong> observed methanol<br />

emission showed a distinct diurnal cycle and<br />

was strongly correlated with global radiation and<br />

water vapour flux. Mean and maximum daily<br />

emissions were found to depend on grassland species<br />

composition and, for the intensive field, also<br />

on the growing state. <strong>The</strong> extensive field with a<br />

more complex species composition had higher<br />

emissions than the graminoid-dominated intensive<br />

field, both on an area and on a biomass basis.<br />

A simple parameterisation depending on the water<br />

vapour flux and the leaf area index allowed a<br />

satisfying simulation of the temporal variation of<br />

methanol emissions over the growing phase. Accumulated<br />

carbon losses due to methanol emissions<br />

accounted for 0.024 and 0.048% of net primary<br />

productivity for the intensive and extensive field,<br />

respectively. <strong>The</strong> integral methanol emissions over<br />

the growing periods were more than one order of<br />

magnitude higher than the emissions related to<br />

cut and drying events.<br />

Biogeosciences, 2007, V4, N3, pp 395-410.<br />

08.1-97<br />

A standardized procedure for surveillance and<br />

monitoring European habitats and provision<br />

of spatial data<br />

Bunce R G H, Metzger M J, Jongman R H G, Brandt<br />

J, de Blust G, Elena Rossello R, Groom G B, Halada<br />

L, Hofer G, Howard D C, Kovar P, Mucher C A,<br />

Padoa Schioppa E, Paelinx D, Palo A, Perez Soba M,<br />

Ramos I L, Roche P, Skanes H, Wrbka T<br />

Netherlands, Denmark, Belgium, Spain, Slovakia,<br />

Switzerland, England, Czech Republic, Italy, Estonia,<br />

Portugal<br />

Ecology , Biodiversity<br />

Both science and policy require a practical, transmissible,<br />

and reproducible procedure for surveillance<br />

and monitoring of European habitats, which<br />

can produce statistics integrated at the landscape<br />

level. Over the last 30 years, landscape ecology has<br />

developed rapidly, and many studies now require<br />

spatial data on habitats. Without rigorous rules,


74<br />

changes from baseline records cannot be separated<br />

reliably from background noise. A procedure<br />

is described that satisfies these requirements and<br />

can provide consistent data for Europe, to support<br />

a range of policy initiatives and scientific projects.<br />

<strong>The</strong> methodology is based on classical plant life<br />

forms, used in biogeography since the nineteenth<br />

century, and on their statistical correlation with<br />

the primary environmental gradient. Further categories<br />

can therefore be identified for other continents<br />

to assist large scale comparisons and modelling.<br />

<strong>The</strong> model has been validated statistically<br />

and the recording procedure tested in the field<br />

throughout Europe. A total of 130 General Habitat<br />

Categories (GHCs) is defined. <strong>The</strong>se are enhanced<br />

by recording environmental, site and management<br />

qualifiers to enable flexible database interrogation.<br />

<strong>The</strong> same categories are applied to areal,<br />

linear and point features to assist recording and<br />

subsequent interpretation at the landscape level.<br />

<strong>The</strong> distribution and change of landscape ecological<br />

parameters, such as connectivity and fragmentation,<br />

can then be derived and their significance<br />

interpreted.<br />

Landscape Ecology, 2008, V23, N1, JAN, pp 11-25.<br />

08.1-98<br />

Three objectives of historical ecology: the case<br />

of litter collecting in Central European forests<br />

Bürgi M, Gimmi U<br />

Switzerland<br />

Plant Sciences , Ecology , Forestry , History<br />

Most ecosystems and landscapes worldwide are<br />

dominated or influenced by human impacts. Consequently,<br />

studies of pattern and processes of and<br />

within anthropogenic ecosystems and cultural<br />

landscapes have to consider human impacts and<br />

their historical development adequately. Three<br />

major objectives of historical ecology, i.e., the<br />

study of human impacts on ecosystems and landscapes<br />

over time, can be distinguished: (a) preserving<br />

cultural heritage in ecosystems and landscapes,<br />

(b) understanding historical trajectories<br />

of pattern and processes in ecosystems and landscapes,<br />

and (c) informing ecosystem and landscape<br />

management. In this paper, the application<br />

of these three major objectives of historical<br />

ecology is illustrated with a case study on litter<br />

collecting-a largely forgotten traditional forest<br />

use in Central Europe. Historical analyses do not<br />

allow-and should not be misused- to directly deduct<br />

management goals, as goals need to be set<br />

based on present needs and demands. Still, information<br />

on reference condition is relevant in<br />

the process of defining goals. Once specific goals<br />

are set, historical ecology may advise on how to<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

best achieve and maintain desirable pattern and<br />

processes in ecosystems or landscape.<br />

Landscape Ecology, 2007, V22, S1, pp 77-87.<br />

08.1-99<br />

Response to ozone of beech (Fagus sylvatica<br />

L.) seedlings under competition, in an opentop<br />

chamber experiment. A chlorophyll fluorescence<br />

analysis<br />

Bussotti F, Cascio C, Strasser R<br />

Italy, Switzerland<br />

Plant Sciences , Forestry , Ecology<br />

Photosynthesis Research, 2007, V91, N2-3, FEB-<br />

MAR, p 319.<br />

08.1-100<br />

Comparative typology in six european lowintensity<br />

systems of grassland management<br />

Caballero R, Riseth J A, Labba N, Tyran E, Musial<br />

W, Motik E, Boltshauser A, Hofstetter P, Gueydon<br />

A, Roeder N, Hoffmann H, Moreira M B, Coelho<br />

Inockdo S, Brito O, Gil A<br />

Spain, Norway, Poland, Switzerland, Germany,<br />

Portugal<br />

Agriculture, Soil Sciences , Ecology , Biodiversity ,<br />

Zoology<br />

Advances in Agronomy Vol 96, 2007, V96, pp<br />

351-420.<br />

08.1-101<br />

Identification of priority areas for plant conservation<br />

in Madagascar using Red List criteria:<br />

rare and threatened Pandanaceae indicate<br />

sites in need of protection<br />

Callmander M W, Schatz G E, Lowry P P Ii, Laivao<br />

M O, Raharimampionona J, Andriambololonera S,<br />

Raminosoa T, Consiglio T K<br />

USA, Switzerland, Madagascar, France<br />

Biodiversity , Plant Sciences , Ecology , Forestry<br />

A major problem in establishing effective protocols<br />

for conserving Madagascar’s biodiversity<br />

is the lack of reliable information for the identification<br />

of priority sites in need of protection.<br />

Analyses of field data and information from herbarium<br />

collections for members of the Plant family<br />

Pandanaceae (85 spp. of Pandanus; 6 spp. of<br />

Martellidendron) showed how risk of extinction<br />

assessments can inform conservation planning.<br />

Application of IUCN Red List categories and criteria<br />

showed that 91% of the species are threatened.<br />

Mapping occurrence revealed centres of richness<br />

and rarity as well as gaps in Madagascar’s existing<br />

protected area network. Protection of 10 additional<br />

sites would be required to encompass the<br />

19 species currently lacking representation in the<br />

reserve network, within which east coast littoral


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 75<br />

forests are particularly under represented and<br />

important. <strong>The</strong> effect of scale on assessments of<br />

risk of extinction was explored by applying different<br />

grid cell sizes to estimate area of occupancy.<br />

Using a grid cell size within the range suggested<br />

by IUCN overestimates threatened status if based<br />

solely upon specimen data. For poorly inventoried<br />

countries such as Madagascar measures of range<br />

size based on such data should be complemented<br />

with field observations to determine population<br />

size, sensitivity to disturbance, and specific<br />

threats to habitat and therefore potential population<br />

decline. <strong>The</strong> analysis of such data can make<br />

an important contribution to the conservation<br />

planning process by identifying threatened species<br />

and revealing the highest priority sites for<br />

their conservation.<br />

Oryx, 2007, V41, N2, APR, pp 168-176.<br />

08.1-102<br />

Heavy metal contamination in the semiarid<br />

area of Cartagena-La Union (SE Spain) and its<br />

implications for revegetation<br />

Conesa H M, Faz A, Garcia G, Arnaldos R<br />

Spain, Switzerland<br />

Plant Sciences , Agriculture, Soil Sciences , Toxicology<br />

, Geochemistry & Geophysics , Ecology<br />

In this study a mine tailing located near La Union<br />

town (SE Spain) was investigated in order to establish<br />

lines for further phytostabilization works. A<br />

plot sampling design was carried out in order to<br />

characterize the soil properties and natural occurring<br />

vegetation. <strong>The</strong> tailing is strongly eroded<br />

and vegetation on its surface is scarce. Total heavy<br />

metal concentrations were 1800 mg kg (-1) for Pb<br />

and Zn, and 180 mg kg(-1) for Cu. <strong>The</strong> pH was less<br />

than 4 and consequently, water extractable metals<br />

(14% of the total Zn) and electrical conductivity<br />

(>15 dS m(-1)) were high. Nutrient properties<br />

were poor (


76<br />

<strong>The</strong> daily fluctuations in soil water content suggest<br />

that some root uptake of groundwater was mediated<br />

through the upper soil layers by hydraulic lift.<br />

During the dry season, Q. ilex maintained higher<br />

predawn leaf water potentials, canopy conductances<br />

and transpiration rates than Q. sober: <strong>The</strong> higher<br />

water status of Q. ilex was likely associated with<br />

their deeper root systems compared with Q. sober.<br />

Whole-tree hydraulic conductance and minimum<br />

midday leaf water potential were lower in Q. ilex,<br />

indicating that Q. ilex was more tolerant to drought<br />

than Q. suber. Overall, Q. ilex seemed to have more<br />

effective drought avoidance and drought tolerance<br />

mechanisms than Q. suber.<br />

Tree Physiology, 2007, V27, N6, JUN, pp 793-803.<br />

08.1-105<br />

Impact of <strong>Swiss</strong> agricultural policies on nitrate<br />

leaching from arable land<br />

Decrem M, Spiess E, Richner W, Herzog F<br />

Switzerland<br />

Modelling , Agriculture, Soil Sciences , Water Resources<br />

, Toxicology<br />

From 1993 onwards, various policy measures aiming<br />

at reducing nitrogen (N) losses were introduced<br />

in <strong>Swiss</strong> agriculture. We studied the impact of these<br />

measures on nitrate leaching under arable land in<br />

the Fehraltorf catchment near Zürich. Because of<br />

the well- drained soils, the shallow water table and<br />

the intensive agricultural activity, the groundwater<br />

in this catchment is highly vulnerable to nitrate<br />

pollution. N fluxes and transformations on the<br />

field scale were simulated using the deterministic<br />

model LEACHMN. Following the calibration of the<br />

model with a dataset from a long- term lysimeter<br />

experiment, simulations were run for the period<br />

1998 - 2003. As far as possible, field- specific management<br />

data from farmers’ control sheets were<br />

used as input. Average nitrate leaching in the period<br />

1998 - 2003 was estimated to amount to 39 kg<br />

N ha(-1) year(-1). <strong>The</strong> conditions before the introduction<br />

of the policy measures were simulated in<br />

three scenarios with a higher use of both mineral<br />

N fertiliser and animal manure and 50% less or no<br />

catch crops. We found that lowering mineral N fertiliser<br />

and manure application by about 25% led to<br />

an average decrease in nitrate leaching of 10 kg N<br />

ha(-1) year(-1). Doubling the catch crop area yielded<br />

a further decrease of 6 kg N ha(-1) year(-1) on average.<br />

Altogether, the implementation of reduced N<br />

fertiliser inputs and increased use of catch crops<br />

proved to be effective and led to a mean reduction<br />

in N leaching of 29% (16 kg ha(-1) year(-1)) for the<br />

arable land in the Fehraltorf catchment.<br />

Agronomy For Sustainable Development, 2007,<br />

V27, N3, JUL-SEP, pp 243-253.<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

08.1-106<br />

Competition between Lythrum salicaria and a<br />

rare species: combining evidence from experiments<br />

and long-term monitoring<br />

Denoth M, Myers J H<br />

Switzerland, Canada<br />

Plant Sciences , Biodiversity , Ecology<br />

<strong>The</strong> rare endemic plant Sidalcea hendersonii (Henderson’s<br />

checker- mallow) occurs in tidal marshes<br />

of the Pacific Northwest and may be threatened<br />

by Lythrum salicaria (purple loosestrife), a European<br />

invader plant. We compared the abundances<br />

of Lythrum and Sidalcea in a wetland in British<br />

Columbia (Canada) in 1999 to those measured in<br />

1979 to track changes in both species. Although<br />

the frequency of Sidalcea decreased by more than<br />

50%, and that of Lythrum increased by almost 20%,<br />

there was no significant relationship between the<br />

changes of the two species. We assessed the potential<br />

effects of competition by Lythrum on Sidalcea<br />

in field and patio experiments. In the field, we<br />

measured the response of Sidalcea to the removal<br />

of Lythrum over a two-year period and compared<br />

this to the response of Sidalcea to the removal<br />

of native species and in unmanipulated control<br />

plots. Removal of Lythrum significantly improved<br />

the vegetative performance of Sidalcea compared<br />

to the removal of randomly selected native plants<br />

and the control treatment in the first year. In the<br />

second year, the performance of Sidealcea did not<br />

differ significantly with treatment. Removals did<br />

not influence the reproductive performance of<br />

Sidalcea in either year. A one-year additive experiment,<br />

carried out in pots, compared the competitive<br />

effect of Lythrum on Sidalcea with that of two<br />

native species. Lythrum’s impact on Sidalcea was<br />

not consistently stronger than that of the native<br />

species. Collectively, these results do not indicate<br />

a strong impact of Lythrum on the reproduction<br />

or abundance of Sidalcea.<br />

Plant Ecology, 2007, V191, N2, AUG, pp 153-161.<br />

08.1-107<br />

Effects of landscape structure and land-use<br />

intensity on similarity of plant and animal<br />

communities<br />

Dormann C F, Schweiger O, Augenstein I, Bailey<br />

D, Billeter R, de Blust G, Defilippi R, Frenzel M,<br />

Hendrickx F, Herzog F, Klotz S, Liira J, Maelfait J P,<br />

Schmidt T, Speelmans M, van Wingerden W K R E,<br />

Zobel M<br />

Germany, Switzerland, Belgium, Netherlands,<br />

Estonia<br />

Ecology , Biodiversity , Plant Sciences , Zoology<br />

Aim Species richness in itself is not always sufficient<br />

to evaluate land management strategies


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 77<br />

for nature conservation. <strong>The</strong> exchange of species<br />

between local communities may be affected by<br />

landscape structure and land-use intensity. Thus,<br />

species turnover, and its inverse, community<br />

similarity, may be useful measures of landscape<br />

integrity from a diversity perspective. Location A<br />

European transect from France to Estonia. Methods<br />

We measured the similarity of plant, bird,<br />

wild bee, true bug, carabid beetle, hoverfly and<br />

spider communities sampled along gradients in<br />

landscape composition (e.g. total availability of<br />

semi- natural habitat), landscape configuration<br />

(e.g. fragmentation) and land-use intensity (e.g.<br />

pesticide loads). Results Total availability of seminatural<br />

habitats had little effect on community<br />

similarity, except for bird communities, which<br />

were more homogeneous in more natural landscapes.<br />

Bee communities, in contrast, were less<br />

similar in landscapes with higher percentages<br />

of semi- natural habitats. Increased landscape<br />

fragmentation decreased similarity of true bug<br />

communities, while plant communities showed a<br />

nonlinear, U-shaped response. More intense land<br />

use, specifically increased pesticide burden, led<br />

to a homogenization of bee, bug and spider communities<br />

within sites. In these cases, habitat fragmentation<br />

interacted with pesticide load. Hoverfly<br />

and carabid beetle community similarity was<br />

differentially affected by higher pesticide levels:<br />

for carabid beetles similarity decreased, while for<br />

hoverflies we observed a U-shaped relationship.<br />

Main conclusions Our study demonstrates the effects<br />

of landscape composition, configuration and<br />

land-use intensity on the similarity of communities.<br />

It indicates reduced exchange of species between<br />

communities in landscapes dominated by<br />

agricultural activities. Taxonomic groups differed<br />

in their responses to environmental drivers and<br />

using but one group as an indicator for ‘biodiversity’<br />

as such would thus not be advisable.<br />

<strong>Global</strong> Ecology and Biogeography, 2007, V16, N6,<br />

NOV, pp 774-787.<br />

08.1-108<br />

Weak and variable relationships between<br />

environmental severity and small-scale cooccurrence<br />

in alpine plant communities<br />

Dullinger S, Kleinbauer I, Pauli H, Gottfried M,<br />

Brooker R, Nagy L, <strong>The</strong>urillat J P, Holten J I, Abdaladze<br />

O, Benito J L, Borel J L, Coldea G, Ghosn D,<br />

Kanka R, Merzouki A, Klettner C, Moiseev P, Molau<br />

U, Reiter K, Rossi G, Stanisci A, Tomaselli M, Unterlugauer<br />

P, Vittoz P, Grabherr G<br />

Austria, Scotland, Switzerland, Norway, Rep Of<br />

Georgia, France, Romania, Greece, Slovakia, Spain,<br />

Russia, Sweden, Italy<br />

Plant Sciences , Modelling , Ecology<br />

1. <strong>The</strong> stress gradient hypothesis suggests a shift<br />

from predominant competition to facilitation<br />

along gradients of increasing environmental<br />

severity. This shift is proposed to cause parallel<br />

changes from prevailing spatial segregation to aggregation<br />

among the species within a community.<br />

2. We used 904 1-m(2) plots, each subdivided into<br />

100 10 x 10 cm, or 25 20 x 20 cm cells, respectively,<br />

from 67 European mountain summits grouped<br />

into 18 regional altitudinal transects, to test this<br />

hypothesized correlation between fine-scale spatial<br />

patterns and environmental severity. 3. <strong>The</strong><br />

data were analysed by first calculating standardized<br />

differences between observed and simulated<br />

random co-occurrence patterns for each plot.<br />

<strong>The</strong>se standardized effect sizes were correlated to<br />

indicators of environmental severity by means of<br />

linear mixed models. In a factorial design, separate<br />

analyses were made for four different indicators<br />

of environmental severity (the mean temperature<br />

of the coldest month, the temperature sum<br />

of the growing season, the altitude above tree<br />

line, and the percentage cover of vascular plants<br />

in the whole plot), four different species groups<br />

(all species, graminoids, herbs, and all growth<br />

forms considered as pseudospecies) and at the 10<br />

x 10 cm and 20 x 20 cm grain sizes. 4. <strong>The</strong> hypothesized<br />

trends were generally weak and could only<br />

be detected by using the mean temperature of the<br />

coldest month or the percentage cover of vascular<br />

plants as the indicator of environmental severity.<br />

<strong>The</strong> spatial arrangement of the full species<br />

set proved more responsive to changes in severity<br />

than that of herbs or graminoids. <strong>The</strong> expected<br />

trends were more pronounced at a grain size of 10<br />

x 10 cm than at 20 x 20 cm. 5. Synthesis. In European<br />

alpine plant communities the relationships<br />

between small-scale co-occurrence patterns of vascular<br />

plants and environmental severity are weak<br />

and variable. This variation indicates that shifts<br />

in net interactions with environmental severity<br />

may differ among indicators of severity, growth<br />

forms and scales. Recognition of such variation<br />

may help to resolve some of the current debate<br />

surrounding the stress gradient hypothesis.<br />

Journal of Ecology, 2007, V95, N6, NOV, pp<br />

1284-1295.<br />

08.1-109<br />

Minor changes in soil organic carbon and charcoal<br />

concentrations detected in a temperate<br />

deciduous forest a year after an experimental<br />

slash-and-burn<br />

Eckmeier E, Gerlach R, Skjemstad J O, Ehrmann O,<br />

Schmidt M W I


78<br />

Switzerland, Germany, Australia<br />

Forestry, Plant Sciences, Agriculture, Soil Sciences ,<br />

Ecology<br />

Anthropogenic fires affected the temperate deciduous<br />

forests of Central Europe over millennia.<br />

Biomass burning releases carbon to the atmosphere<br />

and produces charcoal, which potentially<br />

contributes to the stable soil carbon pools and is<br />

an important archive of environmental history.<br />

<strong>The</strong> fate of charcoal in soils of temperate deciduous<br />

forests, i.e. the processes of charcoal incorporation<br />

and transportation and the effects on soil<br />

organic matter are still not clear. We investigated<br />

the effects of slash-and-burn at a longterm experimental<br />

burning site and determined soil organic<br />

carbon and charcoal carbon concentrations as<br />

well as the soil lightness of colour (L*) in the topmost<br />

soil material (0-1, 1-2.5 and 2.5-5 cm depths)<br />

before, immediately after the fire and one year<br />

later. <strong>The</strong> main results are that (i) only a few of the<br />

charcoal particles from the forest floor were incorporated<br />

into the soil matrix, presumably by soil<br />

mixing animals. In the 0-1 cm layer, during one<br />

year, the charcoal C concentration increased only<br />

by 0.4 g kg(-1) and the proportion of charcoal C<br />

to SOC concentration increased from 2.8 to 3.4%;<br />

(ii) the SOC concentrations did not show any significant<br />

differences; (iii) soil lightness decreased<br />

significantly in the topmost soil layer and correlated<br />

well with the concentrations of charcoal C<br />

(r=-0.87**) and SOC (r=-0.94**) in the samples from<br />

the 0-5 cm layer. We concluded that Holocene biomass<br />

burning could have influenced soil charcoal<br />

concentrations and soil colour.<br />

Biogeosciences, 2007, V4, N3, pp 377-383.<br />

08.1-110<br />

Conversion of biomass to charcoal and the<br />

carbon mass balance from a slash-and-burn<br />

experiment in a temperate deciduous forest<br />

Eckmeier E, Rosch M, Ehrmann O, Schmidt M W I,<br />

Schier W, Gerlach R<br />

Switzerland, Germany<br />

Forestry , Plant Sciences , History<br />

Anthropogenic burning, including slash-andburn,<br />

was deliberately used in (pre)historic Central<br />

Europe. Biomass burning has affected the<br />

global carbon cycle since, presumably, the early<br />

Holocene. <strong>The</strong> understanding of processes and<br />

rates of charcoal formation in temperate deciduous<br />

forests is limited, as is the extent of prehistoric<br />

human impact on the environment. We took<br />

advantage of an experimental burning to simulate<br />

Neolithic slash-and-burn, and we quantified<br />

the biomass fuel and charcoal produced, determined<br />

the resulting distribution of the charcoal<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

size fractions and calculated the carbon mass balance.<br />

Two-thirds of the charcoal particles (6.71 t /<br />

ha) were larger than 2000 Rm and the spatial distribution<br />

of charcoal was highly variable (15-90%<br />

per m(2)). <strong>The</strong> conversion rate of the biomass fuel<br />

to charcoal mass was 4.8%, or 8.1% for the conversion<br />

of biomass carbon to charcoal.<br />

Holocene, 2007, V17, N4, MAY, pp 539-542.<br />

08.1-111<br />

Simulating future changes in Arctic and subarctic<br />

vegetation<br />

Epstein H E, Yu Qin, Kaplan J O, Lischke H<br />

USA, Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences ,<br />

Ecology<br />

<strong>The</strong> Arctic is a sensitive system undergoing dramatic<br />

changes related to recent warming trends.<br />

Vegetation dynamics-increases in the quantity of<br />

green vegetation and a northward migration of<br />

trees into the arctic tundra-are a component of<br />

this change. Although field studies over long time<br />

periods can be logistically problematic, simulation<br />

modeling provides a means for projecting<br />

changes in arctic and subarctic vegetation caused<br />

by environmental variations.<br />

Computing in Science Engineering, 2007, V9, N4,<br />

JUL-AUG, pp 12-23.<br />

08.1-112<br />

Response of soil microbial biomass and community<br />

structures to conventional and organic<br />

farming systems under identical crop rotations<br />

Esperschuetz J, Gattinger A, Mäder P, Schloter M,<br />

Fliessbach A<br />

Germany, Switzerland<br />

Microbiology , Agriculture, Soil Sciences , Plant Sciences<br />

, Biodiversity , Ecology<br />

In this study the influence of different farming systems<br />

on microbial community structure was analyzed<br />

using soil samples from the DOK long-term<br />

field experiment in Switzerland, which comprises<br />

organic (BIODYN and BIOORG) and conventional<br />

(CONFYM and CONMIN) farming systems as well<br />

as an unfertilized control (NOFERT). We examined<br />

microbial communities in winter wheat plots at<br />

two different points in the crop rotation (after<br />

potatoes and after maize). Employing extended<br />

polar lipid analysis up to 244 different phospholipid<br />

fatty acids (PLFA) and phospholipid ether lipids<br />

(PLEL) were detected. Higher concentrations of<br />

PLFA and PLEL in BIODYN and BIOORG indicated<br />

a significant influence of organic agriculture on<br />

microbial biomass. Farmyard manure (FYM) application<br />

consistently revealed the strongest, and the<br />

preceding crop the weakest, influence on domain-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 79<br />

specific biomass, diversity indices and microbial<br />

community structures. Esterlinked PLFA from<br />

slowly growing bacteria (k- strategists) showed the<br />

strongest responses to long-term organic fertilization.<br />

Although the highest fungal biomass was<br />

found in the two organic systems of the DOK field<br />

trial, their contribution to the differentiation of<br />

community structures according to the management<br />

regime was relatively low. Prokaryotic communities<br />

responded most strongly to either conventional<br />

or organic farming management.<br />

Fems Microbiology Ecology, 2007, V61, N1, JUL, pp<br />

26-37.<br />

08.1-113<br />

Methodical study of nitrous oxide eddy covariance<br />

measurements using quantum cascade<br />

laser spectrometery over a <strong>Swiss</strong> forest<br />

Eugster W, Zeyer K, Zeeman M, Michna P, Zingg A,<br />

Buchmann N, Emmenegger L<br />

Switzerland<br />

Forestry , Plant Sciences , Ecology<br />

Nitrous oxide fluxes were measured at the Lageren<br />

CarboEurope IP flux site over the multi-species<br />

mixed forest dominated by European beech and<br />

Norway spruce. Measurements were carried out<br />

during a four-week period in October-November<br />

2005 during leaf senescence. Fluxes were measured<br />

with a standard ultrasonic anemometer in<br />

combination with a quantum cascade laser absorption<br />

spectrometer that measured N 2O, CO 2,<br />

and H 2O mixing ratios simultaneously at 5 Hz<br />

time resolution. To distinguish insignificant fluxes<br />

from significant ones it is proposed to use a new<br />

approach based on the significance of the correlation<br />

coefficient between vertical wind speed and<br />

mixing ratio fluctuations. This procedure eliminated<br />

roughly 56% of our half- hourly fluxes. Based<br />

on the remaining, quality checked N 2O fluxes we<br />

quantified the mean efflux at 0.8 +/- 0.4 µmol m(-2)<br />

h(-1) (mean + /- standard error). Most of the contribution<br />

to the N 2O flux occurred during a 6.5-h period<br />

starting 4.5 h before each precipitation event.<br />

No relation with precipitation amount could be<br />

found. Visibility data representing fog density<br />

and duration at the site indicate that wetting of<br />

the canopy may have as strong an effect on N 2O<br />

effluxes as does below-ground microbial activity.<br />

It is speculated that above- ground N 2O production<br />

from the senescing leaves at high moisture<br />

(fog, drizzle, onset of precipitation event) may be<br />

responsible for part of the measured flux.<br />

Biogeosciences, 2007, V4, N5, pp 927-939.<br />

08.1-114<br />

Improving predictive mapping in <strong>Swiss</strong> mire<br />

ecosystems through re- calibration of indicator<br />

values<br />

Feldmeyer C E, Ecker K, Kuechler M, Graf U, Waser L<br />

Switzerland<br />

Ecology , Plant Sciences , Modelling , Forestry<br />

Question: How may Landolt indicator values be recalibrated<br />

to improve the performance of predictive<br />

models? Location: Mires Gross Moos Schwandital<br />

(1250 m a.s.l.) in the Prealps, Burgymoos (465<br />

m. a.s.l.) on the Central Plateau and La Burtigniere<br />

(1000 m a.s.l.) in the Jura, Switzerland. Methods:<br />

Habitat distribution models based on high resolution<br />

remotely sensed data and vegetation field data<br />

are applied to monitor 130 mires. Instead of plant<br />

species or communities we used mean indicator<br />

values of vegetation records as response variables.<br />

To improve the differential power of indicator values<br />

for wetland habitat conditions, we calibrated<br />

these values using field data. Different methods<br />

were tested with our predictive models in three<br />

mires to see which calibration method is best in<br />

enhancing model performance. To assess the effect<br />

of the uneven distribution of vegetation records<br />

along environmental gradients. calibrations<br />

based on random and evenly distributed samples<br />

were compared. As a test of the predictive power<br />

of the models we used r(2) between ground truth<br />

and model prediction. This approach is illustrated<br />

through an application with nutrient indicator<br />

values in the mire La Burtigniere. Results: Model<br />

performances were not the same for the three<br />

mires. <strong>The</strong> predictive power was better for the nutrient<br />

values, soil reaction and humus values than<br />

for light and moisture values. 2000 records were<br />

sufficient as basis for re-calibration. Models based<br />

on original Landolt indicator values were overall<br />

the weakest compared with re-calibrated values. By<br />

comparing the predictive power of Models based<br />

on randomly or evenly selected records were about<br />

equally predictive. Conclusions: 1. A habitat-specific<br />

re-calibration of the Landolt indicator values<br />

enhances the predictive mapping of the <strong>Swiss</strong> mire<br />

ecosystems. 2. <strong>The</strong> re-calibration based on weighted<br />

averaging gives a better performance than the<br />

one based on Gaussian logistic regression. 3. <strong>The</strong><br />

uneven distribution of indicator values due to the<br />

over-representation of mire habitats does not hamper<br />

model performance. 4. 2000 vegetation records<br />

are a sufficient basis for an optimal re-calibration<br />

of the vegetation types. An illustration of the method<br />

is given by using the soil fertility pattern of the<br />

mire La Burtigniere.<br />

Applied Vegetation Science, 2007, V10, N2, AUG,<br />

pp 183-192.


80<br />

08.1-115<br />

Effects of an extended drought period on<br />

grasslands at various altitudes in Switzerland<br />

Feller U, Signarbieux C<br />

Switzerland<br />

Plant Sciences , Meteorology & Atmospheric Sciences<br />

, Ecology<br />

Photosynthesis Research, 2007, V91, N2-3, FEB-<br />

MAR, p 294.<br />

08.1-116<br />

Secondary succession and loss in plant diversity<br />

following a grazing decrease in a wooded<br />

pasture of the central <strong>Swiss</strong> Alps<br />

Frelechoux F, Meisser M, Gillet F<br />

Switzerland<br />

Plant Sciences , Agriculture, Soil Sciences , Biodiversity<br />

, Ecology<br />

Reduced cattle grazing pressure in the Alps has<br />

caused the reforestation of many subalpine pastures<br />

during the last decades. To understand the<br />

dynamics of natural reforestation and to evaluate<br />

how this change affects plant species diversity, we<br />

described the vegetation of a wooded pasture in<br />

the central <strong>Swiss</strong> Alps (Sembrancher, Valais) using<br />

the integrated synusial method. Based on stratified<br />

vegetation releves in 27 plots, we defined 11<br />

community types at the synusial level (two tree-layer,<br />

five shrub-layer, and four herb-layer synusiae),<br />

and four community types at the phytocoenosis<br />

level (pasture, tall forbs and scrub, wooded pasture<br />

and forest). <strong>The</strong> spatial distribution of these<br />

four phytocoenoses suggests that they represent<br />

successional stages after abandonment, and that<br />

the pathway of vegetation succession depends on<br />

the aspect. We suppose that on northern oriented,<br />

cool and shady locations, abandoned pastures<br />

first develop towards tall-forb meadows and scrub<br />

with Alnus viridis, and then to a preforested stage<br />

with Picea abies and Larix decidua. In contrast, on<br />

western oriented, warm and sunny location, Larix<br />

decidua (mainly) and Picea abies directly colonize<br />

the abandoned pastures, but further succession<br />

finally leads to the same pre-forested stage as on<br />

northern slopes. Plant species richness was highest<br />

in open areas and decreased by 25 % as tree<br />

cover increased from 6 % to 65 %. According to our<br />

successional model, plant species diversity is lost<br />

more rapidly on northern slopes (with speciespoor<br />

green alder scrub) than on western slopes<br />

(with species- rich young larch forests), suggesting<br />

that northern slopes most urgently need an appropriate<br />

grazing management.<br />

Botanica Helvetica, 2007, V117, N1, JUN, pp<br />

37-56.<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

08.1-117<br />

<strong>Change</strong>s of photosynthetic traits in beech saplings<br />

(Fagus sylvatica) under severe drought<br />

stress and during recovery<br />

Galle A, Feller U<br />

Switzerland<br />

Plant Sciences , Forestry<br />

In the context of an increased risk of extreme<br />

drought events across Europe during the next<br />

decades, the capacity of trees to recover and survive<br />

drought periods awaits further attention. In<br />

summer 2005, 4- year-old beech (Fagus sylvatica L.)<br />

saplings were watered regularly or were kept for 4<br />

weeks without irrigation in the field and then re-<br />

watered again. <strong>Change</strong>s of plant water status, leaf<br />

gas exchange and Chl a fluorescence parameters,<br />

as well as alterations in leaf pigment composition<br />

were followed. During the drought period, stomatal<br />

conductance (g(s)) and net photosynthesis<br />

(P-n) decreased in parallel with increased water<br />

deficit. After 14 days without irrigation, stomata<br />

remained closed and P-n was almost completely<br />

inhibited. Reversible downregulation of PSII photochemistry<br />

(the maximum quantum efficiency<br />

of PSII (F-v/F-m)), enhanced thermal dissipation<br />

of excess excitation energy and an increased ratio<br />

of xanthophyll cycle pigments to chlorophylls<br />

(because of a loss of chlorophylls) contributed to<br />

an enhanced photo-protection in severely stressed<br />

plants. Leaf water potential was restored immediately<br />

after re- watering, while g(s), P-n and F-v/F-m<br />

recovered only partially during the initial phase,<br />

even when high external CO 2 concentrations were<br />

applied during the measurements, indicating<br />

lasting non-stomatal limitations. <strong>The</strong>reafter, P-n<br />

recovered completely within 4 weeks, meanwhile<br />

g(s) remained permanently lower in stressed than<br />

in control plants, leading to an increased ‘intrinsic<br />

water use efficiency’ (P-n /g(s)). In conclusion,<br />

although severe drought stress adversely affected<br />

photosynthetic performance of F. sylvatica (a rather<br />

drought-sensitive species), P-n was completely<br />

restored after re- watering, presumably because<br />

of physiological and morphological adjustments<br />

(e.g. stomatal occlusions).<br />

Physiologia Plantarum, 2007, V131, N3, NOV, pp<br />

412-421.<br />

08.1-118<br />

Stochastic gene expression in switching environments<br />

Gander M J, Mazza C, Rummler H<br />

Switzerland<br />

Microbiology , Ecology<br />

Organisms are known to adapt to regularly varying<br />

environments. However, in most cases, the


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 81<br />

fluctuations of the environment are irregular<br />

and stochastic, alternating between favorable<br />

and unfavorable regimes, so that cells must cope<br />

with an uncertain future. A possible response is<br />

population diversification. We assume here that<br />

the cell population is divided into two groups,<br />

corresponding to two phenotypes, having distinct<br />

growth rates, and that cells can switch randomly<br />

their phenotypes. In static environments, the net<br />

growth rate is maximized when the population is<br />

homogeneously composed of cells having the largest<br />

growth rate. In random environments, growth<br />

rates fluctuate and observations reveal that sometimes<br />

heterogeneous populations have a larger<br />

net growth rate than homogeneous ones, a fact<br />

illustrated recently through Monte-Carlo simulations<br />

based on a birth and migration process in<br />

a random environment. We study this process<br />

mathematically by focusing on the proportion f<br />

(t) of cells having the largest growth rate at time<br />

t, and give explicitly the related steady state distribution<br />

pi. We also prove the convergence of<br />

empirical averages along trajectories to the first<br />

moment Epsilon pi (f), and provide efficient numerical<br />

methods for computing Epsilon pi (f).<br />

Journal of Mathematical Biology, 2007, V55, N2,<br />

AUG, pp 249-269.<br />

08.1-119<br />

Natural forest regrowth as a proxy variable for<br />

agricultural land abandonment in the <strong>Swiss</strong><br />

mountains: a spatial statistical model based on<br />

geophysical and socio-economic variables<br />

Gellrich M, Baur P, Zimmermann N E<br />

Switzerland<br />

Forestry , Agriculture, Soil Sciences , Plant Sciences<br />

Modelling<br />

In many European mountain regions, natural forest<br />

regrowth on abandoned agricultural land and<br />

the related consequences for the environment are<br />

issues of increasing concern. We developed a spatial<br />

statistical model based on multiple geophysical<br />

and socio-economic variables to investigate<br />

the pattern of natural forest regrowth in the <strong>Swiss</strong><br />

mountain area between the 1980s and 1990s. Results<br />

show that forest regrowth occurred primarily<br />

in areas with low temperature sum, intermediate<br />

steepness and soil stoniness as well as close to<br />

forest edges and relatively close to roads. Model<br />

results suggest that regions with weak labor markets<br />

are favored in terms of land abandonment<br />

and forest regrowth. We could not find an effect<br />

of population change on land abandonment and<br />

forest regrowth. <strong>The</strong>refore, we conclude that decision<br />

makers should consider non-linearities in<br />

the pattern of forest regrowth and the fact that la-<br />

bor markets have an effect on land abandonment<br />

and forest regrowth when designing measures to<br />

prevent agricultural land abandonment and natural<br />

forest regrowth in the <strong>Swiss</strong> mountains.<br />

Environmental Modeling Assessment, 2007, V12,<br />

N4, NOV, pp 269-278.<br />

08.1-120<br />

Challenges to the uptake of the ecosystem<br />

service rationale for conservation<br />

Ghazoul J<br />

Switzerland<br />

Biodiversity , Ecology<br />

Conservation Biology, 2007, V21, N6, DEC, pp<br />

1651-1652.<br />

08.1-121<br />

What you see is where you go? Modeling<br />

dispersal in mountainous landscapes<br />

Graf R F, Kramer Schadt S, Fernandez N, Grimm V<br />

Germany, Switzerland, Spain<br />

Modelling , Ecology<br />

Inter-patch connectivity can be strongly influenced<br />

by topography and matrix heterogeneity,<br />

particularly when dealing with species with high<br />

cognitive abilities. To estimate dispersal in such<br />

systems, simulation models need to incorporate a<br />

behavioral component of matrix effects to result<br />

in more realistic connectivity measures. Interpatch<br />

dispersal is important for the persistence of<br />

capercaillie (Tetrao urogallus) in central Europe,<br />

where this endangered grouse species lives in<br />

patchy populations embedded in a mountainous<br />

landscape. We simulated capercaillie movements<br />

with an individual-based, spatially explicit dispersal<br />

model (IBM) and compared the resulting connectivity<br />

measure with distance and an expert<br />

estimation. We used a landscape comprising discrete<br />

habitat patches, temporary habitat, non-habitat<br />

forests, and non-habitat open land. First, we<br />

assumed that dispersing individuals have perfect<br />

knowledge of habitat cells within the perceptual<br />

range (null model). <strong>The</strong>n, we included constraints<br />

to perception and accessibility, i.e., mountain<br />

chains, open area and valleys (three sub-models).<br />

In a full model, all sub-models were included at<br />

once. Correlations between the different connectivity<br />

measures were high (Spearman’s rho > 0.7)<br />

and connectivity based on the full IBM was closer<br />

to expert estimation than distance. For selected<br />

cases, simple distance differed strongly from the<br />

full IBM measure and the expert estimation. Connectivity<br />

based on the IBM was strongly sensitive<br />

to the size of perceptual range with higher sensitivity<br />

for the null model compared to the full<br />

model that included context dependent perceptu-


82<br />

al ranges. Our heuristic approach is adequate for<br />

simulating movements of species with high cognitive<br />

abilities in strongly structured landscapes<br />

that influence perception and permeability.<br />

Landscape Ecology, 2007, V22, N6, JUL, pp<br />

853-866.<br />

08.1-122<br />

A predictive model of the density of airborne<br />

insects in agricultural environments<br />

Grübler M U, Morand M, Naef Dänzer B<br />

Switzerland<br />

Modelling , Agriculture, Soil Sciences , Zoology ,<br />

Ecology<br />

This paper presents a model to predict the daily<br />

spatio-temporal variation in the abundance of<br />

airborne insects in agricultural landscapes on the<br />

basis of publicly available environmental data.<br />

Data on the abundance of insects flying near<br />

ground level were collected by a robust and effective<br />

point-count method. <strong>The</strong> validation of the<br />

model using extra data revealed a high correspondence<br />

between predicted and observed insect density.<br />

<strong>The</strong> final model showed that the abundance<br />

of airborne insects depended largely on the daily<br />

weather conditions. Agricultural habitats differed<br />

in the abundance of airborne insects, with peak<br />

insect numbers found along hedgerows and trees.<br />

This accumulation pattern was most pronounced<br />

at low temperatures and in windy conditions. Efforts<br />

to enhance insect abundance in agricultural<br />

landscapes therefore need to increase the number<br />

of structural elements such as hedgerows, single<br />

trees and orchards. This study highlights how<br />

weather conditions and agricultural land-use<br />

affect aerial food webs in agri-environments, including<br />

the dynamics of food patches for all kinds<br />

of aerial foragers. (c) 2007 Elsevier B.V. All rights<br />

reserved.<br />

Agriculture Ecosystems Environment, 2008, V123,<br />

N1-3, JAN, pp 75-80.<br />

08.1-123<br />

Measured microwave radiative transfer properties<br />

of a deciduous forest canopy<br />

Guglielmetti M, Schwank M, Mätzler C, Oberdoerster<br />

C, Vanderborght J, Flühler H<br />

Switzerland, Germany<br />

Remote Sensing , Forestry , Plant Sciences , Modelling<br />

A field experiment was performed with an L- and<br />

X-band radiometer operating at 1.4 GHz and 11.4<br />

GHz in a deciduous forest in Julich (Germany)<br />

from September to November 2004. <strong>The</strong> radiometers<br />

were installed on the ground being directed<br />

upwards through the canopy. In this position<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

downwelling microwave radiation was measured<br />

during the defoliation of the forest with a time<br />

resolution of 4 h. Simultaneously we measured<br />

the air and soil temperatures. Based on these data,<br />

the transmissivities of the forest canopy were estimated<br />

at different foliation states. Typical L-band<br />

transmissivities determined for the foliated and<br />

the defoliated states were 0.41 and 0.46, confirming<br />

the semi-transparency of the canopy at low<br />

microwave frequencies. Due to the anisotropic<br />

crown structure the L-band brightness temperatures<br />

were slightly horizontally polarized to the<br />

same degree for any state of the vegetation. From<br />

this we conclude that branches are the prevailing<br />

emitters of the canopy whereas leaves and trunks<br />

are less relevant for L-band observations. In the Xband,<br />

the canopy was opaque in the foliated state<br />

and became semi-transparent in the course of defoliation<br />

indicating that leaves are an important<br />

radiation source at this wavelength. Our results<br />

provide the experimental evidence to quantify<br />

the radiation properties of a deciduous forest canopy.<br />

This is crucial for interpreting the microwave<br />

radiation emitted from forested areas measured<br />

from space-borne microwave sensing platforrns.<br />

Remote Sensing of Environment, 2007, V109, N4,<br />

AUG 30, pp 523-532.<br />

08.1-124<br />

What matters for predicting the occurrences<br />

of trees: Techniques, data, or species’ characteristics?<br />

Guisan A, Zimmermann N E, Elith J, Graham C H,<br />

Phillips S, Peterson A T<br />

Switzerland, Australia, USA<br />

Forestry , Modelling , Plant Sciences , Ecology<br />

Data characteristics and species traits are expected<br />

to influence the accuracy with which species’<br />

distributions can be modeled and predicted. We<br />

compare 10 modeling techniques in terms of predictive<br />

power and sensitivity to location error,<br />

change in map resolution, and sample size, and<br />

assess whether some species traits can explain<br />

variation in model performance. We focused on<br />

30 native tree species in Switzerland and used<br />

presence-only data to model current distribution,<br />

which we evaluated against independent presence<br />

absence data. While there are important differences<br />

between the predictive performance of<br />

modeling methods, the variance in model performance<br />

is greater among species than among techniques.<br />

Within the range of data perturbations<br />

in this study, some extrinsic parameters of data<br />

affect model performance more than others: location<br />

error and sample size reduced performance<br />

of many techniques, whereas grain had little ef-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 83<br />

fect on most techniques. No technique can rescue<br />

species that are difficult to predict. <strong>The</strong> predictive<br />

power of species-distribution models can partly<br />

be predicted from a series of species characteristics<br />

and traits based on growth rate, elevational<br />

distribution range, and maximum elevation.<br />

Slow-growing species or species with narrow and<br />

specialized niches tend to be better modeled. <strong>The</strong><br />

<strong>Swiss</strong> presence-only tree data produce models<br />

that are reliable enough to be useful in planning<br />

and management applications.<br />

Ecological Monographs, 2007, V77, N4, NOV, pp<br />

615-630.<br />

08.1-125<br />

Temporal changes in grazing intensity and<br />

herbage quality within a <strong>Swiss</strong> fen meadow<br />

Güsewell S, Pohl M, Gander A, Strehler C<br />

Switzerland<br />

Agriculture, Soil Sciences, Plant Sciences , Ecology ,<br />

Biodiversity<br />

Grazing is a possible tool for conservation management<br />

in wetlands, but a frequent problem is<br />

spatial variation in grazing intensity, which may<br />

promote the degradation of the vegetation. Temporal<br />

changes in grazing patterns may reduce<br />

this problem by leading to a more homogeneous<br />

overall use of the area. In a lakeshore wetland<br />

(2.8 ha) grazed by Scottish Highland cattle from<br />

May till September, we studied how the grazing<br />

of nine vegetation types changes seasonally and<br />

between years, and how this is related to the<br />

quantity and quality of the herbage. We observed<br />

cattle activity weekly throughout two grazing<br />

periods, determined the biomass and nutrient<br />

concentrations of the vegetation, analysed dung<br />

samples, and carried out clipping experiments to<br />

assess shoot regeneration after grazing. <strong>The</strong> annual<br />

grazing intensity varied seven-fold among<br />

vegetation types, and this pattern was closely<br />

similar in both years. In several vegetation types,<br />

however, grazing intensity changed seasonally.<br />

Cattle first grazed tall grass-dominated vegetation<br />

(Phragmition, Phalaridion), which had the<br />

most digestible and nutrient-rich herbage, but<br />

the poor regeneration of dominant species forced<br />

the cattle to then graze small-sedge dominated,<br />

nutrient-poor fen vegetation (Caricion davallianae).<br />

<strong>The</strong>se temporal changes in grazing patterns<br />

slightly reduced the spatial variation in grazing<br />

intensity. To take advantage of this effect,<br />

relatively long grazing seasons are preferable to<br />

shorter ones. Four years of grazing reduced the<br />

above- ground biomass production and nutrient<br />

concentrations of several vegetation types.<br />

<strong>The</strong>refore, years without grazing may be needed<br />

to prevent a degradation of palatable plant communities<br />

with low grazing tolerance.<br />

Botanica Helvetica, 2007, V117, N1, JUN, pp<br />

57-73.<br />

08.1-126<br />

Biodiversity and ecosystem functioning: reconciling<br />

the results of experimental and observational<br />

studies<br />

Hector A, Joshi J, Scherer Lorenzen M, Schmid B,<br />

Spehn E M, Wacker L, Weilenmann M, Bazeley<br />

White E, Beierkuhnlein C, Caldeira M C, Dimitrakopoulos<br />

P G, Finn J A, Huss Danell K, Jumpponen A,<br />

Leadley P W, Loreau M, Mulder C P H, Nesshoever<br />

C, Palmborg C, Read D J, Siamantziouras A S D,<br />

Terry A C, Troumbis A Y<br />

Switzerland, Germany, England, Portugal, Greece,<br />

Ireland, Sweden, France, Canada<br />

Biodiversity , Ecology , Plant Sciences<br />

Functional Ecology, 2007, V21, N5, OCT, pp<br />

998-1002.<br />

08.1-127<br />

<strong>The</strong> generality of habitat suitability models: A<br />

practical test with two insect groups<br />

Hein S, Binzenhöfer B, Poethke H J, Biedermann R,<br />

Settele J, Schroeder B<br />

Switzerland, Germany<br />

Biodiversity , Ecology , Modelling , Zoology<br />

For the design and declaration of conservation areas<br />

as well as for planning habitat management<br />

it is important to quantitatively know the habitat<br />

preferences of the focal species. To take into account<br />

the requirements of as many species as possible,<br />

it would be of great advantage if one would<br />

either (i) find one or several species whose habitat<br />

requirements cover those of a large number of<br />

other species or if one could (ii) identify a common<br />

set of habitat parameters that is important<br />

for the occurrence of many species. Ideally such<br />

common habitat parameters should be easy to<br />

measure. Only then they may be of practical value<br />

in applied conservation biology. In this study, we<br />

compared the habitat preferences of different insect<br />

species (grasshoppers, bush crickets, butterflies,<br />

moths) in the same region by applying identical<br />

methods. To identify common explanatory<br />

variables that predict the occurrence probability<br />

of these species, we first tested the transferability<br />

of the specific ‘species models’ to other species<br />

within the same insect group. We tested how well<br />

the incidence of one species can be predicted by<br />

the occurrence probability of another species. <strong>The</strong><br />

‘best’ models within each group were then tested<br />

for transferability between the different groups.<br />

Additionally, we tested the predictive power of the


84<br />

predictor variable ‘habitat type’ as an easy and often<br />

available measure for conservation practice.<br />

Although in the different ‘species models’ different<br />

key factors determine habitat suitability,<br />

some models were successfully transferred and<br />

were able to reasonably predict the distribution<br />

of other species. <strong>The</strong> habitat preferences of the<br />

burnet moth Zygaena carniolica were particularly<br />

well suited for the prediction of suitable habitats<br />

for all other species. In addition, the predictor<br />

variable ‘habitat type’ played a dominant role in<br />

all models. Models using this aggregated predictor<br />

variable may well predict suitable habitat for<br />

all species.<br />

Basic and Applied Ecology, 2007, V8, N4, pp<br />

310-320.<br />

08.1-128<br />

Fragmented environment affects birch leaf<br />

endophytes<br />

Helander M, Ahlholm J, Sieber T N, Hinneri S, Saikkonen<br />

K<br />

Finland, Switzerland<br />

Plant Sciences , Forestry , Ecology , Microbiology ,<br />

Biodiversity<br />

<strong>The</strong> effect of environmental fragmentation on<br />

the species distribution and frequency of horizontally<br />

transmitted endophytic fungi in Betula<br />

pubescens and Betula pendula leaves was studied<br />

in an archipelago in southwestern Finland. <strong>The</strong><br />

study system consisted of 14 islands, ranging in<br />

size and distance to the mainland, and five mainland<br />

sites. Endophytic fungi were grown out from<br />

surface-leaves. <strong>The</strong> frequency of endophytic fungi<br />

mainly depended on the size of the island, explaining<br />

32-35% of the variation, and the distance<br />

to the mainland explaining 29-35% of the variation.<br />

<strong>The</strong> birch trees on the largest islands near<br />

the mainland had the highest endophyte frequencies.<br />

Fusicladium betulae, Gnomonia setacea and<br />

Melanconium betulinum were the most commonly<br />

isolated fungi. Foliar endophytes of birch trees<br />

are able to disperse to fairly fragmented areas, but<br />

their frequencies seem to depend on environmental<br />

isolation and size of the island.<br />

New Phytologist, 2007, V175, N3, pp 547-553.<br />

08.1-129<br />

Host-parasitoid spatial dynamics in heterogeneous<br />

landscapes<br />

Hirzel A H, Nisbet R M, Murdoch W W<br />

Switzerland, USA<br />

Biodiversity , Ecology , Modelling<br />

This paper explores the effect of spatial processes<br />

in a heterogeneous environment on the dynamics<br />

of a host-parasitoid interaction. <strong>The</strong> environment<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

consists of a lattice of favourable (habitat) and<br />

hostile (matrix) hexagonal cells, whose spatial distribution<br />

is measured by habitat proportion and<br />

spatial autocorrelation (inverse of fragmentation).<br />

At each time step, a fixed fraction of both populations<br />

disperses to the adjacent cells where it reproduces<br />

following the Nicholson-Bailey model.<br />

Aspects of the dynamics analysed include extinction,<br />

stability, cycle period and amplitude, and the<br />

spatial patterns emerging from the dynamics. We<br />

find that, depending primarily on the fraction of<br />

the host population that disperses in each generation<br />

and on the landscape geometry, five classes<br />

of spatio-temporal dynamics can be objectively<br />

distinguished: spatial chaos, spirals, metapopulation,<br />

mainland- island and spiral fragments. <strong>The</strong><br />

first two are commonly found in theoretical studies<br />

of homogeneous landscapes. <strong>The</strong> other three<br />

are direct consequences of the heterogeneity and<br />

have strong similarities to dynamic patterns observed<br />

in real systems (e.g. extinction- recolonisation,<br />

source-sink, outbreaks, spreading waves). We<br />

discuss the processes that generate these patterns<br />

and allow the system to persist. <strong>The</strong> importance of<br />

these results is threefold: first, our model merges<br />

into a same theoretical framework dynamics commonly<br />

observed in the field that are usually modelled<br />

independently. Second, these dynamics and<br />

patterns are explained by dispersal rate and common<br />

landscape statistics, thus linking in a practical<br />

way population ecology to landscape ecology.<br />

Third, we show that the landscape geometry has a<br />

qualitative effect on the length of the cycles and,<br />

in particular, we demonstrate how very long periods<br />

can be produced by spatial processes.<br />

Oikos, 2007, V116, N12, DEC, pp 2082-2096.<br />

08.1-130<br />

Mating patterns and contemporary gene flow<br />

by pollen in a large continuous and a small<br />

isolated population of the scattered forest tree<br />

Sorbus torminalis<br />

Hoebee S E, Arnold U, Düggelin C, Gugerli F, Brodbeck<br />

S, Rotach P, Holderegger R<br />

Switzerland<br />

Plant Sciences , Forestry , Microbiology , Ecology ,<br />

Biodiversity<br />

<strong>The</strong> influence of population size and spatial isolation<br />

on contemporary gene flow by pollen and<br />

mating patterns in temperate forest trees are<br />

not well documented, although they are crucial<br />

factors in the life history of plant species. We<br />

analysed a small, isolated population and a large,<br />

continuous population of the insect- pollinated<br />

tree species Sorbus torminalis in two consecutive<br />

years. <strong>The</strong> species recently experienced increased


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 85<br />

habitat fragmentation due to altered forest management<br />

leading to forests with closed canopies.<br />

We estimated individual plant size, percentage of<br />

flowering trees, intensity of flowering, degree of<br />

fruiting and seed set per fruit, and we determined<br />

mating patterns, pollen flow distances and external<br />

gene flow in a genetic paternity analysis based<br />

on microsatellite markers. We found clear effects<br />

of small population size and spatial isolation in<br />

S. torminalis. Compared with the large, continuous<br />

population, the small and isolated population<br />

harboured a lower percentage of flowering trees,<br />

showed less intense flowering, lower fruiting,<br />

less developed seeds per fruit, increased selfing<br />

and received less immigrant pollen. However, the<br />

negative inbreeding coefficients (F-IS) of offspring<br />

indicated that this did not result in inbred seed at<br />

the population level. We also show that flowering,<br />

fruiting and pollen flow patterns varied among<br />

years, the latter being affected by the size of individuals.<br />

Though our study was unreplicated at<br />

the factor level (i.e. isolated vs non-isolated populations),<br />

it shows that small and spatially isolated<br />

populations of S. torminalis may also be genetically<br />

isolated, but that their progeny is not necessarily<br />

more inbred.<br />

Heredity, 2007, V99, N1, JUL, pp 47-55.<br />

08.1-131<br />

Time series of landscape fragmentation caused<br />

by transportation infrastructure and urban<br />

development: a case study from Baden- Wurttemberg,<br />

Germany<br />

Jäger J, Schwarz von Raumer H G , Esswein H, Müller<br />

M, Schmidt Lüttman M<br />

Switzerland, Germany<br />

Urban Studies , Biodiversity , Ecology<br />

Landscape fragmentation is increasingly considered<br />

an important environmental indicator in<br />

the fields of sustainable land use and biodiversity.<br />

To set goals for future development and to plan<br />

appropriate measures, suitable empirical data on<br />

the degree of landscape fragmentation are needed<br />

to identify trends and compare different regions.<br />

However, there is still a significant lack of data on<br />

landscape fragmentation as an indicator, despite<br />

the substantial scientific literature on this topic,<br />

likely because of confusion over the definition of<br />

“fragmentation, “ questions associated with scale<br />

and data issues, and lack of general agreement on<br />

a fragmentation measure. This study presents a<br />

state-wide quantitative analysis of landscape fragmentation<br />

in Baden-Wurttemberg, Germany, by<br />

means of the “ effective mesh size” (m(eff)), which<br />

characterizes the anthropogenic penetration of<br />

landscapes from a geometric point of view and is<br />

based on the probability that two randomly chosen<br />

points in a landscape are connected, i.e., not<br />

separated by barriers such as roads, railroads, or<br />

urban areas. Baden-Wurttemberg is fragmented<br />

to a far greater extent than indicated by previous<br />

studies. <strong>The</strong> m(eff) has decreased by 40% since<br />

1930. This development is strongly related to the<br />

growing number of inhabitants, the increased<br />

use of motorized vehicles, and the hierarchical regional<br />

planning system based on the central place<br />

theory. To illustrate the suitability of the meff<br />

method for environmental monitoring, as a planning<br />

instrument and as an assessment instrument<br />

for impact assessment studies, we explored several<br />

variations of applying the method with regard to<br />

choice of fragmenting elements, consideration of<br />

noise bands, spatial differentiation (e. g., administrative<br />

districts vs. ecoregions), and way of dealing<br />

with patches at the boundaries of the reporting<br />

units. Depending on the objectives of the investigation<br />

(e. g., recreational quality vs. suitability for<br />

wildlife habitat), different variations may be most<br />

appropriate. <strong>The</strong> insights and quantitative results<br />

from Baden-Wurttemberg provide a yardstick for<br />

analyzing and assessing landscape fragmentation<br />

in other countries.<br />

Ecology and Society, 2007, V12, N1, JUN ARTN: 22.<br />

08.1-132<br />

Rapid mixing between old and new C pools in<br />

the canopy of mature forest trees<br />

Keel S G, Siegwolf R T W, Jäggi M, Körner C<br />

Switzerland<br />

Forestry , Plant Sciences , Meteorology & Atmospheric<br />

Sciences<br />

Stable C isotope signals in plant tissues became a<br />

key tool in explaining growth responses to the environment.<br />

<strong>The</strong> technique is based on the fundamental<br />

assumption that the isotopic composition<br />

of a given unit of tissue (e.g. a tree ring) reflects<br />

the specific C uptake conditions in the leaf at a<br />

given time. Beyond the methodological implications<br />

of any deviation from this assumption, it is<br />

of physiological interest whether new C is transferred<br />

directly from sources (a photosynthesizing<br />

leaf) to structural sinks (e.g. adjacent stem tissue),<br />

or inherently passes through existing (mobile) C<br />

pools, which may be of variable (older) age. Here,<br />

we explore the fate of C-13-labelled photosynthates<br />

in the crowns of a 30-35 m tall, mixed forest using<br />

a canopy crane. In all nine study species labelled<br />

C reached woody tissue within 2-9 h after labelling.<br />

Four months later, very small signals were<br />

left in branch wood of Tilia suggesting that low<br />

mixing of new, labelled C with old C had taken<br />

place. In contrast, signals in Fagus and Quercus


86<br />

had increased, indicating more intense mixing.<br />

This species-specific mixing of new with old C<br />

pools is likely to mask year- or season-specific linkages<br />

between tree ring formation and climate and<br />

has considerable implications for climate reconstruction<br />

using stable isotopes as proxies for past<br />

climatic conditions.<br />

Plant Cell and Environment, 2007, V30, N8, AUG,<br />

pp 963-972.<br />

08.1-133<br />

Identifying the early genetic consequences of<br />

habitat degradation in a highly threatened<br />

tropical conifer, Araucaria nemorosa Laubenfels<br />

Kettle C J, Hollingsworth P M, Jaffre T, Moran B,<br />

Ennos R A<br />

Switzerland, Scotland, New Caledonia<br />

Biodiversity , Ecology , Plant Sciences , Forestry<br />

<strong>The</strong> early genetic effects of habitat degradation<br />

were investigated in the critically endangered<br />

conifer Araucaria nemorosa. This species occurs<br />

in New Caledonia, a global biodiversity hotspot<br />

where the world’s greatest concentration of endemic<br />

conifer species coincides with an extremely<br />

high level of habitat destruction due to fire and<br />

mining. Using seven microsatellite loci, estimates<br />

were made of genetic marker variation, inbreeding<br />

coefficients and population differentiation of<br />

adult and seedling cohorts of A. nemorosa. <strong>The</strong>se<br />

were contrasted with equivalent estimates, made<br />

over similar spatial scales and with the same<br />

marker loci, in the locally common and more<br />

widespread sister species Araucaria columnaris.<br />

<strong>The</strong>re were no significant differences in population<br />

genetic parameters between adult populations<br />

of the two species, despite their different<br />

abundances. However, in A. nemorosa, the juvenile<br />

cohort showed a loss of rare alleles and elevated<br />

levels of inbreeding when compared to the<br />

adult cohort. <strong>The</strong>se genetic differences between<br />

the cohorts were not observed in the locally common<br />

A. columnaris. This suggests that recent environmental<br />

degradation is influencing the genetic<br />

structure of A. nemorosa populations. Although<br />

this is not detectable among predisturbance adult<br />

populations, an early warning of these impacts<br />

is evident in more recently established seedling<br />

cohorts. <strong>The</strong> conservation implications of these<br />

results are discussed.<br />

Molecular Ecology, 2007, V16, N17, SEP, pp<br />

3581-3591.<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

08.1-134<br />

Arbuscular mycorrhizal symbiosis can counterbalance<br />

the negative influence of the exotic<br />

tree species Eucalyptus camaldulensis on the<br />

structure and functioning of soil microbial<br />

communities in a sahelian soil<br />

Kisa M, Sanon A, Thioulouse J, Assigbetse K, Sylla<br />

S, Spichiger R, Dieng L, Berthelin J, Prin Y, Galiana<br />

A, Lepage M, Duponnois R<br />

Senegal, France, Switzerland, Burkina Faso<br />

Forestry , Plant Sciences , Agriculture, Soil Sciences<br />

, Microbiology<br />

<strong>The</strong> hypothesis of the present study was that bacterial<br />

communities would differentiate under Eucalyptus<br />

camaldulensis and that an enhancement<br />

of arbuscular mycorrhizal (AM) density would<br />

minimize this exotic plant species effect. Treatments<br />

consisted of control plants, preplanting<br />

fertilizer application and AM inoculation. After 4<br />

months of culture in autoclaved soil, E. camaldulensis<br />

seedlings were either harvested for growth<br />

measurement or transferred into containers filled<br />

with the same soil but not sterilized. Other containers<br />

were kept without E. camaldulensis seedlings.<br />

After 12 months, effects of fertilizer amendment<br />

and AM inoculation were measured on the<br />

growth of Eucalyptus seedlings and on soil microbial<br />

communities. <strong>The</strong> results clearly show that<br />

this plant species significantly modified the soil<br />

bacterial community. Both community structure<br />

(assessed by denaturing gradient gel electrophoresis<br />

profiles) and function (assessed by substrateinduced<br />

respiration responses including soil catabolic<br />

evenness) were significantly affected. Such<br />

changes in the bacterial structure and function<br />

were accompanied by disturbances in the composition<br />

of the herbaceous plant species layer.<br />

<strong>The</strong>se results highlight the role of AM symbiosis<br />

in the processes involved in soil bio-functioning<br />

and plant coexistence and in afforestation programmes<br />

with exotic tree species that target preservation<br />

of native plant diversity.<br />

Fems Microbiology Ecology, 2007, V62, N1, OCT,<br />

pp 32-44.<br />

08.1-135<br />

Response of net ecosystem productivity of<br />

three boreal forest stands to drought (vol 9,<br />

pg 1128, 2006)<br />

Kljun N, Black T A, Griffis T J, Barr A G, Gaumont<br />

Guay D, Morgenstern K, Mccaughey J H, Nesic Z<br />

Canada, USA, Switzerland<br />

Forestry , Plant Sciences , Ecology<br />

In 2000-03, continuous eddy covariance measurements<br />

of carbon dioxide (CO 2) flux were made<br />

above mature boreal aspen, black spruce, and jack


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 87<br />

pine forests in Saskatchewan, Canada, prior to and<br />

during a 3- year drought. During the 1st drought<br />

year, ecosystem respiration (R) was reduced at the<br />

aspen site due to the drying of surface soil layers.<br />

Gross ecosystem photosynthesis (GEP) increased<br />

as a result of a warm spring and a slow decrease<br />

of deep soil moisture. <strong>The</strong>se conditions resulted<br />

in the highest annual net ecosystem productivity<br />

(NEP) in the 9 years of flux measurements at<br />

this site. During 2002 and 2003, a reduction of 6%<br />

and 34% in NEP, respectively, compared to 2000<br />

was observed as the result of reductions in both<br />

R and GEP, indicating a conservative response to<br />

the drought. Although the drought affected most<br />

of western Canada, there was considerable spatial<br />

variability in summer rainfall over the 100-km extent<br />

of the study area; summer rainfalls in 2001<br />

and 2002 at the two conifer sites minimized the<br />

impact of the drought. In 2003, however, precipitation<br />

was similarly low at all three sites. Due to<br />

low topographic position and consequent poor<br />

drainage at the black spruce site and the coarse<br />

soil with low water-holding capacity at the jack<br />

pine site almost no reduction in R, GEP, and NEP<br />

was observed at these two sites. This study shows<br />

that the impact of drought on carbon sequestration<br />

by boreal forest ecosystems strongly depends<br />

on rainfall distribution, soil characteristics, topography,<br />

and the presence of vegetation that is<br />

well adapted to these conditions.<br />

Ecosystems, 2007, V10, N6, SEP, pp 1039-1055.<br />

08.1-136<br />

Assessment of land use impacts on the natural<br />

environment - Part 2: Generic characterization<br />

factors for local species diversity in central<br />

Europe<br />

Köllner T, Scholz R W<br />

Switzerland<br />

Agriculture, Soil Sciences , Biodiversity , Ecology<br />

Goal, Scope and Background. Land use is an economic<br />

activity that generates large benefits for<br />

human society. One side effect, however, is that<br />

it has caused many environmental problems<br />

throughout history and still does today. Biodiversity,<br />

in particular, has been negatively influenced<br />

by intensive agriculture, forestry and the increase<br />

in urban areas and infrastructure. Integrated assessment<br />

such as Life Cycle Assessment (LCA),<br />

thus, incorporate impacts on biodiversity. <strong>The</strong><br />

main objective of this paper is to develop generic<br />

characterization factors for land use types using<br />

empirical information on species diversity from<br />

Central Europe, which can be used in the assessment<br />

method developed in the first part of this<br />

series of paper. Methods. Based on an extensive<br />

meta-analysis, with information about species<br />

diversity on 5581 sample plots, we calculated<br />

characterization factors for 53 land use types and<br />

six intensity classes. <strong>The</strong> typology is based on the<br />

CORINE Plus classification. We took information<br />

on the standardized alpha-diversity of plants,<br />

moss and mollusks into account. In addition,<br />

threatened plants were considered. Linear and<br />

nonlinear models were used for the calculation of<br />

damage potentials (EDPs). In our approach, we use<br />

the current mean species number in the region<br />

as a reference, because this determines whether<br />

specific land use types hold more or less species<br />

diversity per area. <strong>The</strong> damage potential calculated<br />

here is endpoint oriented. <strong>The</strong> corresponding<br />

characterization factors EDPs can be used in the<br />

Life Cycle Impact Assessment as weighting factors<br />

for different types of land occupation and land<br />

use change as described in Part 1 of this paper series.<br />

Results. <strong>The</strong> result from ranking the intensity<br />

classes based on the mean plant species number<br />

is as expected. High intensive forestry and agriculture<br />

exhibit the lowest species richness (5.7-5.8<br />

plant species/m(2)), artificial surfaces, low intensity<br />

forestry and non- use have medium species richness<br />

(9.4-11.1 plant species/m2) and low- intensity<br />

agriculture has the highest species richness (16.6<br />

plant species/m(2)). <strong>The</strong> mean and median are<br />

very close, indicating that the skewedness of the<br />

distribution is low. Standard error is low and is<br />

similar for all intensity classes. Linear transformations<br />

of the relative species numbers are linearly<br />

transformed into ecosystem damage potentials<br />

(EDPlinears). <strong>The</strong> inte gration of threatened plant<br />

species diversity into a more differentiated damage<br />

function EDPlinearStotal makes it possible<br />

to differentiate between land use types that have<br />

similar total species numbers, but intensities of<br />

land use that are clearly different (e.g., artificial<br />

meadow and broad-leafed forest). Negative impact<br />

values indicate that land use types hold more species<br />

per m(2) than the reference does. In terms of<br />

species diversity, these land use types are superior<br />

(e.g. near-to- nature meadow, hedgerows, agricultural<br />

fallow). Discussion. Land use has severe impacts<br />

on the environment. <strong>The</strong> ecosystem damage<br />

potential EDPS is based on assessment of impacts<br />

of land use on species diversity. We clearly base<br />

EDPs factors on alpha- diversity, which correlates<br />

with the local aspect of species diversity of land<br />

use types. Based on an extensive meta-analysis of<br />

biologists’ field research, we were able to include<br />

data on the diversity of plant species, threatened<br />

plant species, moss and mollusks in the EDPS.<br />

<strong>The</strong> integration of other animal species groups<br />

(e.g. insects, birds, mammals, amphibians) with


88<br />

their specific habitat preferences could change<br />

the characterization factors values specific for<br />

each land use type. Those mobile species groups<br />

support ecosystem functions, because they provide<br />

functional links between habitats in the<br />

landscape. Conclusions. <strong>The</strong> use of generic characterization<br />

factors in Life Cycle Impact Assessment<br />

of land use, which we have developed, can<br />

improve the basis for decision-making in industry<br />

and other organizations. It can best be applied for<br />

marginal land use decisions. However, if the goal<br />

and scope of an LCA requires it this generic assessment<br />

can be complemented with a site-dependent<br />

assessment. Recommendations and Perspectives.<br />

We recommend utilizing the developed characterization<br />

factors for land use in Central Europe<br />

and as a reference methodology for other regions.<br />

In order to assess the impacts of land use in other<br />

regions it would be necessary to sample empirical<br />

data on species diversity and to develop region<br />

specific characterization factors on a worldwide<br />

basis in LCA. This is because species diversity and<br />

the impact of land use on it can very much differ<br />

from region to region.<br />

International Journal of Life Cycle Assessment,<br />

2008, V13, N1, JAN, pp 32-48.<br />

08.1-137<br />

<strong>The</strong> use of ‘altitude’ in ecological research<br />

Körner C<br />

Switzerland<br />

Ecology , Biodiversity , Plant Sciences<br />

Altitudinal gradients are among the most powerful<br />

‘natural experiments’ for testing ecological and<br />

evolutionary responses of biota to geophysical influences,<br />

such as low temperature. However, there<br />

are two categories of environmental changes with<br />

altitude: those physically tied to meters above sea<br />

level, such as atmospheric pressure, temperature<br />

and clear-sky turbidity; and those that are not generally<br />

altitude specific, such as moisture, hours of<br />

sunshine, wind, season length, geology and even<br />

human land use. <strong>The</strong> confounding of the first category<br />

by the latter has introduced confusion in<br />

the scientific literature on altitude phenomena.<br />

Trends in Ecology Evolution, 2007, V22, N11, NOV,<br />

pp 569-574.<br />

08.1-138<br />

Creative use of mountain biodiversity databases:<br />

<strong>The</strong> Kazbegi research agenda of GMBA-<br />

DIVERSITAS<br />

Körner C, Donoghue M, Fabbro T, Hauser C,<br />

Nogues Bravo D, Kalin Arroyo M T, Soberon J,<br />

Speers L, Spehn E M, Sun H, Tribsch A, Tykarski P,<br />

Zbinden N<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

Switzerland, USA, Germany, Denmark, Chile,<br />

Peoples R China, Austria, Poland<br />

Biodiversity , Ecology<br />

Geo-referenced archive databases on mountain<br />

organisms are very promising tools for achieving<br />

a better understanding of mountain biodiversity<br />

and predicting its changes. <strong>The</strong> <strong>Global</strong> Mountain<br />

Biodiversity Assessment (GMBA) of DIVERSITAS, in<br />

cooperation with the <strong>Global</strong> Biodiversity Information<br />

Facility, encourages a global effort to mine<br />

biodiversity databases on mountain organisms.<br />

<strong>The</strong> wide range of climatic conditions and topographies<br />

across the world’s mountains offers an<br />

unparalleled opportunity for developing and testing<br />

biodiversity theory. <strong>The</strong> power of openly accessible,<br />

interconnected electronic databases for scientific<br />

biodiversity research, which by far exceeds<br />

the original intent of archiving for mainly taxonomic<br />

purposes, has been illustrated. <strong>The</strong>re is an<br />

urgent need to increase the amount and quality<br />

of geo-referenced data on mountain biodiversity<br />

provided online, in order to meet the challenges<br />

of global change in mountains.<br />

Mountain Research and Development, 2007, V27,<br />

N3, AUG, pp 276-281.<br />

08.1-139<br />

Mobility of black carbon in drained peatland<br />

soils<br />

Leifeld J, Fenner S, Müller M<br />

Switzerland<br />

Agriculture, Soil Sciences , Ecology , Geochemistry<br />

& Geophysics<br />

Amount, stability, and distribution of black carbon<br />

(BC) were studied at four sites of a large peatland<br />

(“Witzwil”) formerly used as a disposal for<br />

combustion residues from households to derive<br />

BC displacement rates in the profile. Possible artefacts<br />

from thermal oxidation with Differential<br />

Scanning Calorimetry (DSC) on BC quantification<br />

of C-rich deposits were inferred by choosing<br />

three sites from a second peatland with no<br />

historical record of waste disposal as a reference<br />

(“Seebodenalp”). All sites were under grassland at<br />

time of sampling, but were partially cropped in<br />

the past at Witzwil. Mean BC contents in topsoils<br />

of Witzwil ranged from 10.7 to 91.5 (0-30 cm) and<br />

from 0.44 to 51.3 (30-140 cm) mg BC g(-1) soil, corresponding<br />

to BC/OC ratios of 0.04 to 0.3 (topsoil)<br />

and 0.02 to 0.18 (deeper soil). At three sites of Seebodenalp,<br />

BC was below the detection limit of 0.4<br />

mg g(-1) organic soil, indicating negligible formation<br />

of BC during thermal oxidation of peat. C-13<br />

NMR spectra corroborated the high BC contents at<br />

Witzwil. <strong>The</strong> data support a considerable vertical<br />

transport of BC given that soils were ploughed not


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 89<br />

deeper than 30 cm since abandonment of waste<br />

application about 50 years ago. <strong>The</strong> total amount<br />

of BC in the Witzwil profiles ranged from 3.2 to 7.5<br />

kg BC m(-2), with 21 to 69 percent of it stemming<br />

from below the former ploughing depth. Under<br />

the premise of negligible rates of BC consumption<br />

since abandonment of waste application, minimum<br />

BC transport rates in these peats are 0.6 to<br />

1.2 cm a(-1). <strong>The</strong> high mobility of BC might be explained<br />

by high macropore volumes in combination<br />

with occasional water saturation. By means<br />

of DSC peak temperatures, different types of BC<br />

could be distinguished, with deeper horizons containing<br />

BC of higher thermal stability. Application<br />

of combustion residues likely involved a mixture<br />

of various BC types, of which thermally more<br />

stable ones, most likely soots, were preferentially<br />

transported downwards.<br />

Biogeosciences, 2007, V4, N3, pp 425-432.<br />

08.1-140<br />

Tree species diversity affects canopy leaf temperatures<br />

in a mature temperate forest<br />

Leuzinger S, Körner C<br />

Switzerland<br />

Forestry , Biodiversity , Plant Sciences , Ecology<br />

Forest canopies play a major role in biosphereatmosphere<br />

interaction. <strong>The</strong>ir actual temperature<br />

may deviate substantially from ambient atmospheric<br />

conditions as reported by weather stations.<br />

While there is a long tradition of false-colour imagery,<br />

new digital technologies in combination<br />

with IR transmission lenses and autocalibration<br />

routines permit unprecedented insight into the<br />

actual temperature regimes in canopies. We report<br />

canopy leaf temperature distribution over<br />

space and time assessed over a 35 m tall mixed<br />

deciduous forest in NW Switzerland by means of<br />

a construction crane and a high resolution thermal<br />

camera. At an air temperature of 25 degrees<br />

C, conifers (Picea abies, Pinus sylverstris and Larix<br />

decidua) and deciduous broad-leaved trees with<br />

exceptionally high transpiration (Quercus petraea)<br />

or very open, low density canopies (Prunus<br />

avium) exhibited mean canopy leaf temperatures<br />

close to air temperature (0.3-2.7 K above ambient)<br />

and the maximum amplitude within a given<br />

crown reached 69 K. In contrast, broad-leaved deciduous<br />

species with dense canopies (Fagus sylvatica,<br />

Carpinus betulus and Tilia platyphyllos)<br />

were 4.5-5 K warmer than air temperature and<br />

showed within canopy temperature amplitudes of<br />

10-12 K. Calculated leaf boundary resistance was<br />

clearly lower for conifers (3-24 m s(-1)) than for<br />

broad-leaved trees (33-64 m s(-1)). <strong>The</strong> study illustrates<br />

that mean leaf temperatures in forest trees<br />

are not adequately explained by either stomatal<br />

conductance or leaf dimensions, but strongly depend<br />

on canopy architecture (leaf area density,<br />

branching habits) in combination with leaf traits.<br />

Aerodynamic leaf and canopy characteristics lead<br />

to strongly enhanced vapour pressure gradients<br />

(evaporative forcing) and leaf temperatures vary<br />

enormously over short distances, calling for statistical<br />

temperature models (frequency distribution)<br />

rather than the use of means in any flux calculations.<br />

<strong>The</strong> presence/absence of certain tree taxa<br />

plays a key role in forest surface temperature.<br />

Agricultural and Forest Meteorology, 2007, V146,<br />

N1-2, SEP 11, pp 29-37.<br />

08.1-141<br />

Water savings in mature deciduous forest<br />

trees under elevated CO 2<br />

Leuzinger S, Körner C<br />

Switzerland<br />

Forestry , Plant Sciences , Biodiversity , Ecology<br />

Stomatal conductance of plants exposed to elevated<br />

CO 2 is often reduced. Whether this leads<br />

to water savings in tall forest-trees under future<br />

CO 2 concentrations is largely unknown but could<br />

have significant implications for climate and hydrology.<br />

We used three different sets of measurements<br />

(sap flow, soil moisture and canopy temperature)<br />

to quantify potential water savings under<br />

elevated CO 2 in a ca. 35 m tall, ca. 100 years old<br />

mixed deciduous forest. Part of the forest canopy<br />

was exposed to 540 ppm CO 2 during daylight<br />

hours using free air CO 2 enrichment (FACE) and<br />

the <strong>Swiss</strong> Canopy Crane (SCC) . Across species and<br />

a wide range of weather conditions, sap flow was<br />

reduced by 14% in trees subjected to elevated CO 2,<br />

yielding ca. 10% reduction in evapotranspiration.<br />

This signal is likely to diminish as atmospheric<br />

feedback through reduced moistening of the air<br />

comes into play at landscape scale. Vapour pressure<br />

deficit (VPD)-sap flow response curves show<br />

that the CO 2 effect is greatest at low VPD, and that<br />

sap flow saturation tends to occur at lower VPD<br />

in CO 2-treated trees. Matching stomatal response<br />

data, the CO 2 effect was largely produced by Carpinus<br />

and Fagus, with Quercus contributing little.<br />

In line with these findings, soil moisture at 10<br />

cm depth decreased at a slower rate under high-<br />

CO 2 trees than under control trees during rainless<br />

periods, with a reversal of this trend during<br />

prolonged drought when CO 2-treated trees take<br />

advantage from initial water savings. High-resolution<br />

thermal images taken at different heights<br />

above the forest canopy did detect reduced water<br />

loss through altered energy balance only at < 5 m<br />

distance (0.44 K leaf warming of CO 2- treated Fa-


90<br />

gus trees). Short discontinuations of CO 2 supply<br />

during morning hours had no measurable canopy<br />

temperature effects, most likely because the stomatal<br />

effects were small compared with the aerodynamic<br />

constraints in these dense, broad-leaved<br />

canopies. Hence, on a seasonal basis, these data<br />

suggest a < 10% reduction in water consumption<br />

in this type of forest when the atmosphere reaches<br />

540% ppm CO 2.<br />

<strong>Global</strong> <strong>Change</strong> Biology, 2007, V13, N12, DEC, pp<br />

2498-2508.<br />

08.1-142<br />

Anchorage of mature conifers: Resistive turning<br />

moment, root-soil plate geometry and root<br />

growth orientation<br />

Lundstroem T, Jonas T, Stöckli V, Ammann W<br />

Switzerland<br />

Forestry , Plant Sciences<br />

Eighty-four mature Norway spruce (Picea abies L.<br />

Karst), silver fir (Abies alba Mill) and Scots pine<br />

(Pinus sylvestris L.) trees were winched over to determine<br />

the maximum resistive turning moment<br />

(M-a) of the root-soil system, the root-soil plate geometry,<br />

the azimuthal orientation of root growth,<br />

and the occurrence of root rot. <strong>The</strong> calculation of<br />

M-a, based on digital image tracking of stem deflection,<br />

accounted not only for the force application<br />

and its changing geometry, but also for the<br />

weight of the overhanging tree, representing up<br />

to 42% of M-a. Root rot reduced M-a significantly<br />

and was detected in 25% of the Norway spruce and<br />

5% of the silver fir trees. Excluding trees with root<br />

rot, differences in M. between species were small<br />

and insignificant. About 75% of the variance in M.<br />

could be explained by one of the four variablestree<br />

mass, stem mass, stem diameter at breast<br />

height squared times tree height, and stern diameter<br />

at breast height squared. Among the seven<br />

allometric variables assessed above ground, stem<br />

diameter at breast height best described the rootsoil<br />

plate dimensions, but the correlations were<br />

weak and the differences between species were<br />

insignificant. <strong>The</strong> shape of the root-soil plate was<br />

well described by a depth-dependent taper model<br />

with an elliptical cross section. Roots displayed<br />

a preferred azimuthal orientation of growth in<br />

the axis of prevailing, winds, and the direction of<br />

frequent weak winds matched the orientation of<br />

growth better than that of rare strong winds. <strong>The</strong><br />

lack of difference in anchorage parameters among<br />

species probably reflects the similar belowground<br />

growth conditions of the mature trees.<br />

Tree Physiology, 2007, V27, N9, SEP, pp<br />

1217-1227.<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

08.1-143<br />

Wheat quality in organic and conventional<br />

farming: results of a 21 year field experiment<br />

Mäder P, Hahn D, Dubois D, Gunst L, Alföldi T,<br />

Bergmann H, Oehme M, Amado R, Schneider H,<br />

Graf U, Velimirov A, Fliebbach A, Niggli U<br />

Switzerland, Germany, Austria<br />

Agriculture, Soil Sciences , Plant Sciences<br />

Consumers have become more aware of healthy<br />

and safe food produced with low environmental<br />

impact. Organic agriculture is of particular interest<br />

in this respect, as manifested by 5.768 million<br />

hectares managed pursuant to Council Regulation<br />

(EEC) 2092/91 in Europe. However, there can be a<br />

considerable risk that the avoidance of chemical<br />

inputs in organic farming will result in poor food<br />

quality. Here the results of a study on the quality<br />

of wheat (Triticum aestivum L.) grown in a 21<br />

year agrosystem comparison between organic and<br />

conventional farming in central Europe are reported.<br />

Wheat was grown in a ley (grass/clover) rotation.<br />

<strong>The</strong> 71% lower addition of plant-available<br />

nitrogen and the reduced input of other means<br />

of production to the organic field plots led to 14%<br />

lower wheat yields. However, nutritional value<br />

(protein content, amino acid composition and<br />

mineral and trace element contents) and baking<br />

quality were not affected by the farming systems.<br />

Despite exclusion of fungicides from the organic<br />

production systems, the quantities of mycotoxins<br />

detected in wheat grains were low in all systems<br />

and did not differ. In food preference tests, as an<br />

integrative method, rats significantly preferred<br />

organically over conventionally produced wheat.<br />

<strong>The</strong> findings indicate that high wheat quality in<br />

organic farming is achievable by lower inputs,<br />

thereby safeguarding natural resources. (c) 2007<br />

Society of Chemical Industry.<br />

Journal of the Science of Food and Agriculture,<br />

2007, V87, N10, AUG 15, pp 1826-1835.<br />

08.1-144<br />

No difference in competitive ability between<br />

invasive North American and native European<br />

Lepidium draba populations<br />

Mckenney J L, Cripps M G, Price W J, Hinz H L,<br />

Schwarzlaender M<br />

USA, Switzerland<br />

Ecology , Plant Sciences , Biodiversity<br />

<strong>The</strong> evolution of increased competitive ability<br />

(EICA) hypothesis states that plants introduced<br />

into a new range experience reduced herbivory,<br />

which in turn results in a shift in resource allocation<br />

from herbivore defense to growth. If genotypes<br />

of an invasive plant species from its native<br />

and introduced ranges are grown under common


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 91<br />

conditions, introduced genotypes are expected<br />

to grow more vigorously than conspecific native<br />

genotypes. We tested predictions of the EICA hypothesis<br />

with the invasive species Lepidium draba<br />

by comparing the growth of genotypes from<br />

its native European and introduced western US<br />

ranges under common conditions. To test potential<br />

differences in competitive ability, we grew L.<br />

draba from both continents with either Festuca<br />

idahoensis, a weak competitor native to North<br />

America, or Festuca ovina, a strong competitor native<br />

to Europe. Contrary to EICA predictions, there<br />

were no differences in the performance of native<br />

and introduced L. draba, independent of whether<br />

plants were grown with F. idahoensis, F. ovina, or<br />

alone. <strong>The</strong> strong competitor, F. ovina impaired<br />

the growth of L. draba more than the weak competitor<br />

F. idahoensis and conversely, F. idahoensis<br />

was generally more impaired by L. draba than was<br />

F. ovina. While the native F. idahoensis was equally<br />

affected by L. draba regardless of range, F. ovina<br />

was not: US L. draba had a stronger negative effect<br />

on F. ovina growth than European L. draba. Our<br />

data suggest that the EICA hypothesis is not suitable<br />

to explain the invasion success of L. draba in<br />

the US. Instead, the greater competitive effect of<br />

L. draba on the North American F. idahoensis and<br />

the asymmetric competitive effect of L draba from<br />

different origins on F. ovina may indicate superior<br />

competitive ability for resources, or the presence<br />

of allelopathic traits in L. draba, to which plant<br />

species in non-native ranges are maladapted.<br />

Plant Ecology, 2007, V193, N2, DEC, pp 293-303.<br />

08.1-145<br />

Effects of heavy metal soil pollution and acid<br />

rain on growth and water use efficiency of a<br />

young model forest ecosystem<br />

Menon M, Hermle S, Günthardt Goerg M S, Schulin<br />

R<br />

USA, Switzerland<br />

Agriculture, Soil Sciences , Modelling , Plant Sciences<br />

, Forestry , Ecology<br />

In a 4-year lysimeter experiment, we investigated<br />

the effects of topsoil heavy metal pollution (3,000<br />

mg kg(-1) Zn, 640 mg kg(-1) Cu, 90 mg kg(-1) Pb and<br />

10 mg kg(-1) Cd) and (synthetic) acid rain (pH 3.5)<br />

on tree growth and water use efficiency of young<br />

forest ecosystems consisting of Norway spruce (Picea<br />

abies), willow (Salix viminalis), poplar (Populus<br />

tremula) and birch (Betula pendula) trees and<br />

a variety of understorey plants. <strong>The</strong> treatments<br />

were applied in a Latin square factorial design<br />

(contaminated vs uncontaminated topsoil, acidified<br />

rain vs ambient rain) to 16 open-top chambers,<br />

with 4 replicates each. Each open-top chamber<br />

contained two lysimeters, one with a calcareous,<br />

and the other with acidic subsoil. <strong>The</strong> four tree<br />

species responded quite differently to heavy metal<br />

pollution and type of subsoil. <strong>The</strong> fine root mass,<br />

which was only sampled at the end of the experiment<br />

in 2003, was significantly reduced by heavy<br />

metal pollution in P. abies, P. tremula and B. pendula,<br />

but not in S. viminalis. <strong>The</strong> metal treatment<br />

responses of above-ground biomass and leaf area<br />

varied between years. In 2002, the heavy metal<br />

treatment reduced above-ground biomass and<br />

leaf area in P. tremula, but not in the other species.<br />

In 2003, metals did not reduce above-ground<br />

growth in P. tremula, but did so in the other<br />

species. It appears that the responses in aboveground<br />

biomass and leaf area, which paralleled<br />

each other, were related to changes in the relative<br />

competitive strength of the various species<br />

in the two experimental years. S. viminalis gained<br />

relative to P. tremula in absence of metal stress,<br />

in particular on calcareous subsoil, while P. abies<br />

showed the largest increases in growth rates in all<br />

treatments. Above- and below-ground growth was<br />

strongly inhibited by acidic subsoil in S. viminalis<br />

and to a lesser degree also in P. abies. In P. abies,<br />

this subsoil effect was enhanced by metal stress.<br />

Acid rain was not found to have any substantial<br />

effect. Whole-system water use efficiency was reduced<br />

by metal stress and higher on calcareous<br />

than on acidic subsoil.<br />

Plant and Soil, 2007, V297, N1-2, AUG, pp<br />

171-183.<br />

08.1-146<br />

Distribution of polychlorinated biphenyls and<br />

polybrominated diphenyl ethers in birds of<br />

prey from Switzerland<br />

Naert C, van Peteghem C, Kupper J, Jenni L,<br />

Nägeli H<br />

Belgium, Switzerland<br />

Zoology , Toxicology<br />

Polychlorinated biphenyls (PCBs) and the structurally<br />

related polybrominated diphenyl ethers<br />

(PBDEs) have been associated with chronic neurotoxicity<br />

involving reduced motor activity and<br />

impaired attentiveness. Such fleurobehavioral<br />

effects indicate that the central nervous system<br />

may represent an important target organ for the<br />

action of these persistent contaminants in wildlife.<br />

As a consequence, the brain of different terrestrial<br />

and aquatic birds collected in Switzerland<br />

was analysed for PCBs and PBDEs. In parallel, the<br />

same contaminants were examined in the accompanying<br />

adipose tissue. After clean-up by means<br />

of glass columns containing acidified silica, deactivated<br />

alumina and anhydrous sodium sulphate,


92<br />

the samples were analysed by high resolution<br />

gas chromatography /tandem mass spectrometry<br />

(HRGC-MS/MS). Median PCB concentrations in the<br />

brain (sum of PCB 28, PCB 52, PCB 101, PCB 118,<br />

PCB 138, PCB 153 and PCB 180) ranged between<br />

13 ng g (-1) wet weight (ww) in blackbirds (Turdus<br />

merula) and 428 ng g(-1) ww in sparrow hawks (Accipiter<br />

nisus). Median PBDE concentrations in the<br />

brain (sum of BDE 28, BDE 47, BIDE 99, BDE 100,<br />

BDE 153, BDE 154 and BDE 183) ranged from below<br />

the decision limit in buzzards (Buteo buteo) and<br />

blackbirds, to 14 ng g(-1) ww in sparrow hawks.<br />

After correction for the respective lipid content,<br />

higher PCB or PBDE concentrations in brain compared<br />

to adipose tissue, were found in three sparrow<br />

hawks, four buzzards and in all investigated<br />

blackbirds. <strong>The</strong>se results suggest that a deficit in<br />

the neuroprotective function of the blood-brain<br />

barrier may cause unexpected levels of PCBs and<br />

PBDEs in the central nervous system.<br />

Chemosphere, 2007, V68, N5, JUN, pp 977-987.<br />

08.1-147<br />

Effects of experimental lead pollution on the<br />

microbial communities associated with Sphagnum<br />

fallax (Bryophyta)<br />

Nguyen Viet H, Gilbert D, Mitchell E A D, Badot P<br />

M, Bernard N<br />

France, Switzerland<br />

Microbiology , Biodiversity , Ecology , Agriculture,<br />

Soil Sciences , Toxicology<br />

Ecotoxicological studies usually focus on single<br />

microbial species under controlled conditions.<br />

As a result, little is known about the responses<br />

of different microbial functional groups or individual<br />

species to stresses. In an aim to assess the<br />

response of complex microbial communities to<br />

pollution in their natural habitat, we studied the<br />

effect of a simulated lead pollution on the microbial<br />

community (bacteria, cyanobacteria, protists,<br />

fungi, and micrometazoa) living on Sphagnum<br />

fallax. Mosses were grown in the laboratory with<br />

0 (control), 625, and 2,500 µg L-1 of Pb2+ diluted<br />

in a standard nutrient solution and were sampled<br />

after 0, 6, 12, and 20 weeks. <strong>The</strong> biomasses of bacteria,<br />

microalgae, testate amoebae, and ciliates<br />

were dramatically and significantly decreased in<br />

both Pb addition treatments after 6, 12, and 20<br />

weeks in comparison with the control. <strong>The</strong> biomass<br />

of cyanobacteria declined after 6 and 12<br />

weeks in the highest Pb treatment. <strong>The</strong> biomasses<br />

of fungi, rotifers, and nematodes decreased along<br />

the duration of the experiment but were not significantly<br />

affected by lead addition. Consequently,<br />

the total microbial biomass was lower for both Pb<br />

addition treatments after 12 and 20 weeks than<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

in the controls. <strong>The</strong> community structure was<br />

strongly modified due to changes in the densities<br />

of testate amoebae and ciliates, whereas the<br />

relative contribution of bacteria to the microbial<br />

biomass was stable. Differences in responses<br />

among the microbial groups suggest changes in<br />

the trophic links among them. <strong>The</strong> correlation between<br />

the biomass of bacteria and that of ciliates<br />

or testate amoebae increased with increasing Pb<br />

loading. We interpret this result as an effect on<br />

the grazing pathways of these predators and by<br />

the Pb effect on other potential prey (i.e., smaller<br />

protists) . <strong>The</strong> community approach used here<br />

complements classical ecotoxicological studies by<br />

providing clues to the complex effect of pollutantaffecting<br />

organisms both directly and indirectly<br />

through trophic effects and could potentially find<br />

applications for pollution monitoring.<br />

Microbial Ecology, 2007, V54, N2, AUG, pp<br />

232-241.<br />

08.1-148<br />

High specificity but contrasting biodiversity<br />

of Sphagnum-associated bacterial and plant<br />

communities in bog ecosystems independent<br />

of the geographical region<br />

Opelt K, Berg C, Schönmann S, Eberl L, Berg G<br />

Austria, Switzerland<br />

Microbiology , Biodiversity , Ecology , Plant Sciences<br />

Mosses represent ecological niches that harbor a<br />

hitherto largely uncharacterized microbial diversity.<br />

To investigate which factors affect the biodiversity<br />

of bryophyte-associated bacteria, we analyzed<br />

the bacterial communities associated with<br />

two moss species, which exhibit different ecological<br />

behaviors and importance in bog ecosystems,<br />

Sphagnum magellanicum and Sphagnum fallax,<br />

from six temperate and boreal bogs in Germany<br />

and Norway. Furthermore, their surrounding<br />

plant communities were studied. Molecular analysis<br />

of bacterial communities was determined by<br />

single-strand conformation polymorphism (SSCP)<br />

analysis using eubacterial and genus-specific<br />

primers for the dominant genera Burkholderia<br />

and Serratia as well as by sequence analysis of a<br />

Burkholderia 16S rRNA gene clone library. Plant<br />

communities were analyzed by monitoring the<br />

abundance and composition of bryophyte and vascular<br />

plant species, and by determining ecological<br />

indicator values. Interestingly, we found a high<br />

degree of host specificity for associated bacterial<br />

and plant communities of both Sphagnum species<br />

independent of the geographical region. Calculation<br />

of diversity indices on the basis of SSCP<br />

gels showed that the S. fallax-associated communities<br />

displayed a statistically significant higher


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 93<br />

degree of diversity than those associated with S.<br />

magellanicum. In contrast, analyses of plant communities<br />

of Sphagnum-specific habitats resulted<br />

in a higher diversity of S. magellanicum-specific<br />

habitats for all six sites. <strong>The</strong> higher content of nutrients<br />

in the S. fallax-associated ecosystems can<br />

explain higher diversity of microorganisms.<br />

Isme Journal, 2007, V1, N6, OCT, pp 502-516.<br />

08.1-149<br />

Degradation of an arid coastal landscape in<br />

relation to land use changes in Southern Tenerife<br />

(Canary Islands)<br />

Otto R, Krüsi B O, Kienast F<br />

Spain, Switzerland<br />

Agriculture, Soil Sciences , Ecology<br />

<strong>The</strong> results of the first study of land use changes<br />

between 1964 and 1992 in Southern Tenerife<br />

(Canary Islands) are presented and discussed in<br />

relation to the general socio-economic processes<br />

and the current nature conservation policy. <strong>The</strong><br />

analysis of five main land use types with a geographic<br />

information system (GIS) revealed that<br />

the and coastal landscape has been dramatically<br />

transformed during the past decades due to the<br />

increase of mass tourism and the intensification<br />

of agriculture, resulting in a large-scale destruction<br />

of the coastal scrub, the natural, endemicrich<br />

vegetation. Between 1964 and 1992, the area<br />

occupied by irrigated crops increased strongly due<br />

to the transition from tomato to banana production.<br />

During the same period of time, the amount<br />

of abandoned farmland as well as the area used<br />

for housing and infrastructure increased markedly,<br />

the latter by more than 20 times. In nature<br />

reserves, most of the natural vegetation has survived<br />

but only in a degraded state, mainly due to<br />

recreation activities and illegal waste dumping. In<br />

unprotected areas, by contrast, 60% of the natural<br />

vegetation was lost between 1964 and 1992,<br />

and 86% of the native vegatation of recent lava<br />

flows. <strong>The</strong> results show that the current practice<br />

of protecting comparatively small natural areas is<br />

not sufficient to stop the massive destruction of<br />

natural vegetation. Surprisingly and disturbingly,<br />

there is evidence, that a substantial part (40%) of<br />

these losses could easily have been avoided by better<br />

environmental planning. (c) 2007 Elsevier Ltd.<br />

All rights reserved.<br />

Journal of Arid Environments, 2007, V70, N3, AUG,<br />

pp 527-539.<br />

08.1-150<br />

Probing the responses of barley cultivars (Hordeum<br />

vulgare L.) by chlorophyll a fluorescence<br />

OLKJIP under drought stress and re- watering<br />

Oukarroum A, El Madidi S, Schansker G, Strasser R J<br />

Switzerland, Morocco<br />

Plant Sciences , Agriculture, Soil Sciences , Ecology<br />

<strong>The</strong> main objective of this study was to evaluate<br />

the effects of drought and re-watering on 10 varieties<br />

of barley (Hordeum vulgare L.) originating<br />

from Morocco. Five varieties obtained from the<br />

National Institute of Agricultural Research (INRA)<br />

of Morocco and five landraces (local varieties defined<br />

by high stress tolerance, high yield stability,<br />

an intermediate yield and low-input demand)<br />

collected at five localities in the south of Morocco<br />

were used in the present study. After 2 weeks of<br />

growth, drought stress was initiated by withholding<br />

water for 2 weeks followed by 1 week of re-watering.<br />

<strong>The</strong> polyphasic OJIP fluorescence transient<br />

was used to evaluate photosystem, II (PSII) criteria<br />

at the end of the first week of drought stress (moderate<br />

drought), at the end of the second week (severe<br />

drought) and the end of the recovery phase.<br />

Drought and re- watering had little effect on the<br />

maximum quantum yield of primary photochemistry<br />

phi(Po)(=F-V/F-M). <strong>The</strong> photosynthetic performance<br />

index (PI) is the product of an antenna,<br />

reaction center and electron transport dependent<br />

parameter. It revealed differences between varieties<br />

as a function of drought and re-watering. For<br />

the screening for drought stress tolerance, changes<br />

in the PI during a 2-week drought stress treatment<br />

were analysed and a new parameter was defined:<br />

the drought factor index (DFI) = log(PIweek<br />

1/PIcontrol) + 2 log(PIweek 2/PIcontrol). <strong>The</strong> DFI of<br />

the tested varieties correlated with their drought<br />

tolerance. Another parameter that was analysed<br />

was the relative water content. It decreased during<br />

the drought stress treatment varying between 61%<br />

and 78.2% at the end of the drought period. During<br />

the subsequent recovery period, it increased in<br />

a species-dependent manner (65.1-94.1%). A third<br />

parameter studied were changes in the initial<br />

fluorescence rise. <strong>The</strong> fluorescence rise during the<br />

first 300 µs (L-band) can give information on the<br />

energetic connectivity between PSII units whereas<br />

changes in the rise during the first 2 ms (K-band)<br />

offer information on developing limitations on<br />

the donor side of PSII. <strong>Change</strong>s in respectively the<br />

L and K-bands of the fluorescence transients OJIP<br />

were shown to have predictive value with respect<br />

to the vitality of leaves and the tolerance of the<br />

varieties to drought stress.<br />

Environmental and Experimental Botany, 2007,<br />

V60, N3, JUL, pp 438-446.


94<br />

08.1-151<br />

Integrating environmental and economic<br />

performance to assess modern silvoarable<br />

agroforestry in Europe<br />

Palma J, Graves A R, Burgess P J, van der Werf W,<br />

Herzog F<br />

Switzerland, England, Netherlands<br />

Agriculture, Soil Sciences , Ecology , Biodiversity ,<br />

Economics<br />

<strong>The</strong> environmental and economic performance<br />

of silvoarable agroforestry in Europe is highly<br />

variable. Multi-criteria analysis, using the PRO-<br />

METHEE outranking approach, was used to evaluate<br />

the integrated performance of silvoarable<br />

agroforestry on hypothetical farms in nineteen<br />

landscape test sites in Spain, France, and <strong>The</strong><br />

Netherlands. <strong>The</strong> silvoarable scenarios allocated a<br />

proportion of the hypothetical farms (10 or 50%)<br />

to silvoarable agroforestry at two different tree<br />

densities (50 or 113 trees ha(-1)) on two different<br />

qualities of land (best or worst quality land). <strong>The</strong><br />

status quo (conventional arable farming) was also<br />

assessed for comparison. <strong>The</strong> criteria used in the<br />

evaluation (soil erosion, nitrogen leaching, carbon<br />

sequestration, landscape biodiversity, and<br />

infinite net present value) were assessed at each<br />

landscape test site; infinite net present value was<br />

assessed under six levels of government support.<br />

In France, the analysis showed, assuming equal<br />

weighting between environmental and economic<br />

performance, that silvoarable agroforestry was<br />

preferable to conventional arable farming. <strong>The</strong><br />

best results were observed when agroforestry was<br />

implemented on 50% of the highest quality land<br />

on the farm; the effect of tree density (50113 trees<br />

ha(-1)) was small. By contrast, in Spain and <strong>The</strong><br />

Netherlands, the consistently greater profitability<br />

of conventional arable agriculture relative to<br />

the agroforestry alternatives made overall performance<br />

of agroforestry systems dependent on the<br />

proportion of the farm planted, and the tree density<br />

and land quality used.<br />

Ecological Economics, 2007, V63, N4, SEP 15, pp<br />

759-767.<br />

08.1-152<br />

<strong>The</strong> odd man out? Might climate explain the<br />

lower tree alpha-diversity of African rain forests<br />

relative to Amazonian rain forests?<br />

Parmentier I, Malhi Y, Senterre B, Whittaker R J,<br />

Alonso A, Balinga M P B, Bakayoko A, Bongers<br />

F, Chatelain C, Comiskey J A, Cortay R, Kamdem<br />

M N D, Doucet J L, Gautier L, Hawthorne W D,<br />

Issembe Y A, Kouame F N, Kouka L A, Leal M E,<br />

Lejoly J, Lewis S L, Nusbaumer L, Parren M P E, Peh<br />

K S H, Phillips O L, Sheil D, Sonke B, Sosef M S M,<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

Sunderland T C H, Stropp J, Ter Steege H, Swaine<br />

M D, Tchouto M G P, van Gemerden Barend S, van<br />

Valkenburg J L C H, Wöll H<br />

Belgium, England, USA, Cameroon, Cote Ivoire,<br />

Switzerland, Gabon, Ghana, Indonesia, Netherlands,<br />

Scotland<br />

Meteorology & Atmospheric Sciences , Forestry ,<br />

Plant Sciences , Ecology , Biodiversity<br />

1. Comparative analyses of diversity variation<br />

among and between regions allow testing of alternative<br />

explanatory models and ideas. Here, we<br />

explore the relationships between the tree alphadiversity<br />

of small rain forest plots in Africa and<br />

in Amazonia and climatic variables, to test the<br />

explanatory power of climate and the consistency<br />

of relationships between the two continents. 2.<br />

Our analysis included 1003 African plots and 512<br />

Amazonian plots. All are located in old-growth primary<br />

non-flooded forest under 900 m altitude. Tree<br />

alpha-diversity is estimated using Fisher’s alpha calculated<br />

for trees with diameter at breast height >=<br />

10 cm. Mean diversity values are lower in Africa by a<br />

factor of two. 3. Climate-diversity analyses are based<br />

on data aggregated for grid cells of 2.5 x 2.5 km. <strong>The</strong><br />

highest Fisher’s alpha values are found in Amazonian<br />

forests with no climatic analogue in our African<br />

data set. When the analysis is restricted to pixels of<br />

directly comparable climate, the mean diversity of<br />

African forests is still much lower than that in Amazonia.<br />

Only in regions of low mean annual rainfall<br />

and temperature is mean diversity in African forests<br />

comparable with, or superior to, the diversity in<br />

Amazonia. 4. <strong>The</strong> climatic variables best correlated<br />

with the tree alpha- diversity are largely different<br />

in the African and Amazonian data, or correlate<br />

with African and Amazonian diversity in opposite<br />

directions. 5. <strong>The</strong>se differences in the relationship<br />

between local/landscape- scale alpha-diversity and<br />

climate variables between the two continents point<br />

to the possible significance of an array of factors<br />

including: macro-scale climate differences between<br />

the two regions, overall size of the respective species<br />

pools, past climate variation, other forms of<br />

long-term and short-term environmental variation,<br />

and edaphics. We speculate that the lower alpha-diversity<br />

of African lowland rain forests reported here<br />

may be in part a function of the smaller regional<br />

species pool of tree species adapted to warm, wet<br />

conditions. 6. Our results point to the importance<br />

of controlling for variation in plot size and for gross<br />

differences in regional climates when undertaking<br />

comparative analyses between regions of how local<br />

diversity of forest varies in relation to other putative<br />

controlling factors.<br />

Journal of Ecology, 2007, V95, N5, SEP, pp<br />

1058-1071.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 95<br />

08.1-153<br />

Are the living collections of the world’s<br />

botanical gardens following species-richness<br />

patterns observed in natural ecosystems?<br />

Pautasso M, Parmentier I<br />

England, Switzerland, Belgium<br />

Biodiversity , Plant Sciences , Ecology , Urban<br />

Studies<br />

Botanical gardens aim to promote the awareness,<br />

study and conservation of plant species diversity,<br />

but little is known about the species diversity of<br />

botanical gardens themselves. We therefore investigated<br />

whether the species richness of the<br />

world’s botanical gardens is related to their size,<br />

age and geographical location by compiling data<br />

from gardens in 124 different countries. <strong>The</strong> data<br />

show that even in these highly managed ecosystems,<br />

species richness can be described in terms of<br />

a relatively small number of large-scale patterns.<br />

As with most natural ecosystems, there were positive<br />

species-area and species-age relationships.<br />

<strong>The</strong>re was also a positive latitudinal gradient in<br />

species richness, which contrasts with the trend<br />

observed in natural ecosystems. This discrepancy<br />

may be due to the use of heated greenhouses at<br />

high latitudes, the rarity of old botanical gardens<br />

in the tropics, and the problem of poverty in developing<br />

countries, where most hotspots of plant<br />

biodiversity are located. <strong>The</strong>re is thus a need to allocate<br />

more funds to botanical gardens in speciesrich<br />

regions. This study also calls for an increase<br />

in the coordination of data management between<br />

botanical gardens.<br />

Botanica Helvetica, 2007, V117, N1, JUN, pp<br />

15-28.<br />

08.1-154<br />

Common species determine richness patterns<br />

in biodiversity indicator taxa<br />

Pearman P B, Weber D<br />

Switzerland<br />

Biodiversity , Ecology , Zoology , Plant Sciences<br />

Identification of spatial patterns of species diversity<br />

is a central problem in conservation biology,<br />

with the patterns having implications for<br />

the design of biodiversity monitoring programs.<br />

Nonetheless, there are few field data with which<br />

to examine whether variation in species richness<br />

represents consistent correlations among taxa in<br />

the richness of rare or common species, or the<br />

relative importance of common and rare species<br />

in establishing trends in species richness within<br />

taxa. We used field data on three higher taxa<br />

(birds, butterflies, vascular plants) to examine the<br />

correlation of species richness among taxa and<br />

the contribution of rare and common species to<br />

these correlations. We used graphical analysis to<br />

compare the contributions to spatial variation in<br />

species richness by widely- distributed (‘common’)<br />

and sparsely- distributed (‘rare’) species. <strong>The</strong> data<br />

came from the <strong>Swiss</strong> Biodiversity Monitoring Program,<br />

which is national in scope and based on a<br />

randomly located, regular sampling grid of 1 kM2<br />

cells, a scale relevant to real-world monitoring<br />

and managerrient. We found that the correlation<br />

of species richness between groups of rare and<br />

common species varies among higher taxa, with<br />

butterflies exhibiting the highest levels of correlation.<br />

Species richness of common species is consistently<br />

positively correlated among these three<br />

taxa, but in no case exceeded 0.69. Spatial patterns<br />

of species richness are determined mainly<br />

by common species, in agreement with coarse resolution<br />

studies, but the contribution of rare species<br />

to variation in species richness varies within<br />

the study area in accordance with elevation. our<br />

analyses suggest that spatial patterns in species<br />

richness can be described by sampling widely distributed<br />

species alone. Butterflies differ from the<br />

other two taxa in that the richness of red-listed<br />

species and other rare species is correlated with<br />

overall butterfly species richness. Monitoring of<br />

butterfly species richness may provide information<br />

on rare butterflies and on species richness of<br />

other taxa as well.<br />

Biological Conservation, 2007, V138, N1-2, AUG,<br />

pp 109-119.<br />

08.1-155<br />

Earthworm populations in two low-input<br />

cereal farming systems<br />

Pfiffner L, Luka H<br />

Switzerland<br />

Agriculture, Soil Sciences , Ecology<br />

Earthworm populations in low-input integrated<br />

crop management (ICM: no application of insecticides,<br />

fungicides and growth regulators) and organic<br />

farming systems were compared. <strong>The</strong> study<br />

was performed as a 3-year field survey using a<br />

paired-farm approach in six different locations in<br />

northwestern Switzerland. Earthworms were extracted<br />

from soils sampled from 24 winter cereal<br />

fields using a combined method of extraction by<br />

mustard flour solution and handsorting. Earthworm<br />

communities differed between these farming<br />

systems. Over all sites, the mean biomass, abundance<br />

and species richness of earthworms found<br />

in the low-input ICM fields were significantly lower<br />

than in the organic fields. Adult earthworms<br />

in organic fields were 114% more abundant than<br />

in ICM fields, but the frequencies of most species<br />

within the respective systems were similar in both


96<br />

farming systems. <strong>The</strong> numbers of earthworm species<br />

and juveniles were higher in organic fields.<br />

Five species - Lumbricus terrestris (L.), Nicodrilus<br />

longus (Ude), Nicodrilus nocturnus (Evans), Nicodrilus<br />

caliginosus (Sav.) and Allolobo-phora rosea<br />

(Sav.) - were significantly more numerous in the<br />

organic fields than in the ICM fields. Multivariate<br />

analysis showed that the farming system explained<br />

most of the variance and was found to be<br />

the key factor in altering the earthworm fauna.<br />

Late ploughing in autumn was found to have a<br />

major negative effect on earthworm abundance,<br />

irrespective of the farming system. Farming practices<br />

that differ between these farming systems<br />

and may considerably influence earthworm populations<br />

and diversity are discussed. (c) 2007 Elsevier<br />

B.V. All rights reserved.<br />

Applied Soil Ecology, 2007, V37, N3, NOV, pp<br />

184-191.<br />

08.1-156<br />

Combining probabilistic land-use change and<br />

tree population dynamics modelling to simulate<br />

responses in mountain forests<br />

Rickebusch S, Gellrich M, Lischke H, Guisan A, Zimmermann<br />

N E<br />

Switzerland<br />

Agriculture, Soil Sciences , Ecology<br />

Altitudinal tree lines are mainly constrained by<br />

temperature, but can also be influenced by factors<br />

such as human activity, particularly in the European<br />

Alps, where centuries of agricultural use have<br />

affected the tree-line. Over the last decades this<br />

trend has been reversed due to changing agricultural<br />

practices and land-abandonment. We aimed<br />

to combine a statistical land-abandonment model<br />

with a forest dynamics model, to take into account<br />

the combined effects of climate and human<br />

land-use on the Alpine tree-line in Switzerland.<br />

Land-abandonment probability was expressed by<br />

a logistic regression function of degree-day sum,<br />

distance from forest edge, soil stoniness, slope,<br />

proportion of employees in the secondary and tertiary<br />

sectors, proportion of commuters and proportion<br />

of full-time farms. This was implemented<br />

in the TreeMig spatio-temporal forest model. Distance<br />

from forest edge and degree-day sum vary<br />

through feed-back from the dynamics part of<br />

TreeMig and climate change scenarios, while the<br />

other variables remain constant for each grid cell<br />

over time. <strong>The</strong> new model, TreeMig-LAb, was tested<br />

on theoretical landscapes, where the variables<br />

in the land-abandonment model were varied one<br />

by one. This confirmed the strong influence of distance<br />

from forest and slope on the abandonment<br />

probability. Degree-day sum has a more complex<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

role, with opposite influences on land-abandonment<br />

and forest growth. TreeMig-LAb was also applied<br />

to a case study area in the Upper Engadine<br />

(<strong>Swiss</strong> Alps), along with a model where abandonment<br />

probability was a constant. Two scenarios<br />

were used: natural succession only (100% probability)<br />

and a probability of abandonment based<br />

on past transition proportions in that area (2.1%<br />

per decade). <strong>The</strong> former showed new forest growing<br />

in all but the highest-altitude locations. <strong>The</strong><br />

latter was more realistic as to numbers of newly<br />

forested cells, but their location was random and<br />

the resulting landscape heterogeneous. Using the<br />

logistic regression model gave results consistent<br />

with observed patterns of land-abandonment: existing<br />

forests expanded and gaps closed, leading<br />

to an increasingly homogeneous landscape.<br />

Ecological Modelling, 2007, V209, N2-4, DEC 16,<br />

pp 157-168.<br />

08.1-157<br />

Understanding the low-temperature limitations<br />

to forest growth through calibration of a<br />

forest dynamics model with tree-ring data<br />

Rickebusch S, Lischke H, Bugmann H, Guisan A,<br />

Zimmermann N E<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , Forestry ,<br />

Modelling , Plant Sciences<br />

<strong>The</strong> sensitivity of altitudinal and latitudinal treeline<br />

ecotones to climate change, particularly that<br />

of temperature, has received much attention. To<br />

improve our understanding of the factors affecting<br />

tree-line position, we used the spatially explicit<br />

dynamic forest model TreeMig. Although<br />

well-suited because of its landscape dynamics<br />

functions, TreeMig features a parabolic temperature<br />

growth response curve, which has recently<br />

been questioned. and the species parameters are<br />

not specifically calibrated for cold temperatures.<br />

Our main goals were to improve the theoretical<br />

basis of the temperature growth response curve<br />

in the model and develop a method for deriving<br />

that curve’s parameters from tree-ring data. We<br />

replaced the parabola with an asymptotic curve,<br />

calibrated for the main species at the subalpine<br />

(<strong>Swiss</strong> Alps: Pinus cembra, Larix decidua, Picea<br />

abies) and boreal (Fennoscandia: Pinus sylvestris,<br />

Betula pubescens, P. abies) tree-lines. After fitting<br />

new parameters, the growth curve matched observed<br />

tree- ring widths better. For the subalpine<br />

species, the minimum degree-day sum allowing,<br />

growth (kDDMin) was lowered by around 100<br />

degree-days; in the case of Larix, the maximum<br />

potential ring-width was increased to 5.19 mm. At<br />

the boreal tree-line, the kDDMin for P. sylvestris


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 97<br />

was lowered by 210 degree-days and its maximum<br />

ring-width increased to 2.943 mm; for Betula (new<br />

in the model) kDDMin was set to 325 degree- days<br />

and the maximum ring-width to 2.51 mm; the<br />

values from the only boreal sample site for Picea<br />

were similar to the subalpine ones, so the same<br />

parameters were used. However, adjusting the<br />

growth response alone did not improve the model’s<br />

output concerning species’ distributions and<br />

their relative importance at tree-line. Minimum<br />

winter temperature (MinWiT, mean of the coldest<br />

winter month), which controls seedling establishment<br />

in TreeMig, proved more important for<br />

determining distribution. Picea, P. sylvestris and<br />

Betula did not previously have minimum winter<br />

temperature limits, so these values were set to the<br />

95th percentile of each species’ coldest MinWiT<br />

site (respectively -7, -11, -13). In a case study for the<br />

Alps, the original and newly calibrated versions of<br />

TreeMig were compared with biomass data from<br />

the National Forest Inventor), (NFI). Both models<br />

gave similar, reasonably realistic results. In conclusion,<br />

this method of deriving temperature responses<br />

from tree-rings works well. However, regeneration<br />

and its underlying factors seem more<br />

important for controlling species’ distributions<br />

than previously thought. More research on regeneration<br />

ecology, especially at the upper limit of<br />

forests. is needed to improve predictions of treeline<br />

responses to climate change further.<br />

Forest Ecology and Management, 2007, V246,<br />

N2-3, JUL 31, pp 251-263.<br />

08.1-158<br />

Effects of grazing and soil micro-climate on<br />

decomposition rates in a spatio-temporally<br />

heterogeneous grassland<br />

Risch A C, Jurgensen M F, Frank D A<br />

Switzerland, USA<br />

Plant Sciences , Ecology , Agriculture, Soil Sciences<br />

Grazing and seasonal variation in precipitation<br />

and temperature are important controls of soil<br />

and plant processes in grasslands. As these ecosystems<br />

store up to 30% of the world’s belowground<br />

carbon (C), it is important to understand how<br />

this variability affects mineral soil C pools/fluxes,<br />

and how C cycling might be affected by changes<br />

in precipitation and temperature, due to climate<br />

change. <strong>The</strong> aim of this study was to investigate<br />

the effects of grazing and differences in soil temperature<br />

and moisture on standard organic matter<br />

(OM) decomposition rates (cotton cloth) incubated<br />

in the top 10 cm soil of grasslands with<br />

variable topography in Yellowstone National Park<br />

(YNP) during the 2004 growing season. Grazing<br />

did not affect soil temperature, moisture, cot-<br />

ton cloth decomposition rates, soil bulk density,<br />

soil C and N concentrations, or soil C:N ratios.<br />

However, a large spatio-temporal variability in<br />

decomposition was observed: cotton cloth decomposition<br />

was positively related to soil moisture<br />

and soil C and N concentrations, and negatively<br />

to soil temperature. Highest decomposition rates<br />

were found in wetter slope bottom soils (season<br />

averages of decomposition given as rate of decomposition<br />

(cotton rotting rate=CRR)=23-26%) and<br />

lower rates in drier, hill-top soils (season averages,<br />

CRR=20%). Significantly higher decomposition<br />

rates were recorded in spring, early summer and<br />

early fall when soils were moist and cool (spring,<br />

CRR=25%; early summer, CRR=26%; fall, CRR=20%)<br />

compared to mid-summer (CRR=18%) when soils<br />

were dry and warm. Our findings suggest that<br />

climate-change related decreases in precipitation<br />

and increases in temperature predicted for North<br />

American grasslands would decrease soil OM decomposition<br />

in YNP, which contrasts the general<br />

assumption that increases in temperature would<br />

accelerate OM decomposition rates.<br />

Plant and Soil, 2007, V298, N1-2, SEP, pp 191-201.<br />

08.1-159<br />

Natural avalanche disturbance shapes plant<br />

diversity and species composition in subalpine<br />

forest belt<br />

Rixen C, Haag S, Kulakowski D, Bebi P<br />

Switzerland, USA<br />

Plant Sciences , Biodiversity , Ecology , Forestry ,<br />

Cryology / Glaciology<br />

Background: Disturbances by avalanches have<br />

created unique habitats for animals and plants<br />

in subalpine ecosystems worldwide, but at the<br />

same time avalanches can pose a major threat<br />

to humans. Thus, avalanches are suppressed by<br />

means of avalanche barriers to protect settlements<br />

and infrastructures in populated areas of<br />

the European Alps. As a consequence, the disturbance<br />

regime in avalanche tracks has fundamentally<br />

changed. Methods: In the present study we<br />

address ecological consequences of avalanche<br />

suppression on plant diversity. We analysed plant<br />

diversity and species composition in recent and<br />

old avalanche tracks with and without avalanche<br />

suppression and in undisturbed adjacent forests<br />

at high and low elevations. Results: <strong>The</strong> number<br />

of species was higher in both active and inactive<br />

avalanche tracks as compared to undisturbed subalpine<br />

forest. <strong>The</strong> species composition indicated<br />

a wider range of ecological niches in active than<br />

in inactive avalanche tracks. <strong>The</strong> vegetation from<br />

active tracks showed lower indicator values for<br />

temperature and nitrogen availability. <strong>The</strong> pro-


98<br />

portion of alpine species was lower in formerly<br />

active tracks. Conclusions: <strong>The</strong> conditions that<br />

exist in active avalanche tracks increase plant<br />

diversity in relation to undisturbed forest. In the<br />

few decades following avalanche suppression, species<br />

composition changes in tracks from which<br />

avalanches have been excluded. Continued suppression<br />

of avalanche disturbance may lead to a<br />

decline in plant and habitat diversity. Avalanche<br />

disturbance can exert an important influence on<br />

the biodiversity of subalpine forests and provide<br />

important habitats. Anthropogenic changes in<br />

the natural regime of avalanche disturbance are<br />

likely to contribute significantly to future landscape<br />

changes in subalpine forests.<br />

Journal of Vegetation Science, 2007, V18, N5, OCT,<br />

pp 735-A7.<br />

08.1-160<br />

<strong>The</strong> Rauischholzhausen agenda for road ecology<br />

Roedenbeck I A, Fahrig L, Findlay C S, Houlahan J E,<br />

Jäger J, Klar N, Kramer Schadt S, van der Grift E A<br />

Germany, Canada, Switzerland, Netherlands<br />

Ecology , Biodiversity , Zoology , Social Sciences<br />

Despite the documented negative effects of roads<br />

on wildlife, ecological research on road effects<br />

has had comparatively little influence on road<br />

planning decisions. We argue that road research<br />

would have a larger impact if researchers carefully<br />

considered the relevance of the research<br />

questions addressed and the inferential strength<br />

of the studies undertaken. At a workshop at the<br />

German castle of Rauischholzhausen we identified<br />

five particularly relevant questions, which<br />

we suggest provide the framework for a research<br />

agenda for road ecology: (1) Under what circumstances<br />

do roads affect population persistence? (2)<br />

What is the relative importance of road effects vs.<br />

other effects on population persistence? (3) Under<br />

what circumstances can road effects be mitigated?<br />

(4) What is the relative importance of the<br />

different mechanisms by which roads affect population<br />

persistence? (5) Under what circumstances<br />

do road networks affect population persistence at<br />

the landscape scale? We recommend experimental<br />

designs that maximize inferential strength,<br />

given existing constraints, and we provide hypothetical<br />

examples of such experiments for each of<br />

the five research questions. In general, manipulative<br />

experiments have higher inferential strength<br />

than do nonmanipulative experiments, and full<br />

before-after-control- impact designs are preferable<br />

to before-after or control-impact designs. Finally,<br />

we argue that both scientists and planners must<br />

be aware of the limits to inferential strength that<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

exist for a given research question in a given situation.<br />

In particular, when the maximum inferential<br />

strength of any feasible design is low, decision<br />

makers must not demand stronger evidence before<br />

incorporating research results into the planning<br />

process, even though the level of uncertainty<br />

may be high.<br />

Ecology and Society, 2007, V12, N1, JUN ARTN: 11.<br />

08.1-161<br />

Detecting the role of individual species for<br />

overyielding in experimental grassland communities<br />

composed of potentially dominant<br />

species<br />

Roscher C, Schumacher J, Weisser W W, Schmid B,<br />

Schulze E D<br />

Germany, Switzerland<br />

Biodiversity , Plant Sciences , Ecology<br />

Several studies have shown that the contribution<br />

of individual species to the positive relationship<br />

between species richness and community biomass<br />

production cannot be easily predicted from<br />

species monocultures. Here, we used a biodiversity<br />

experiment with a pool of nine potentially<br />

dominant grassland species to relate the species<br />

richness-productivity relationship to responses in<br />

density, size and aboveground allocation patterns<br />

of individual species. Aboveground community<br />

biomass increased strongly with the transition<br />

from monocultures to two-species mixtures but<br />

only slightly with the transition from two- to ninespecies<br />

mixtures. Tripartite partitioning showed<br />

that the strong increase shown by the former was<br />

due to trait-independent complementarity effects,<br />

while the slight increase shown by the latter<br />

was due to dominance effects. Trait- dependent<br />

complementarity effects depended on species<br />

composition. Relative yield total (RYT) was greater<br />

than 1 (RYT > 1) in mixtures but did not increase<br />

with species richness, which is consistent with<br />

the constant complementarity effect. <strong>The</strong> relative<br />

yield (RY) of only one species, Arrhenatherum elatius,<br />

continually increased with species richness,<br />

while those of the other species studied decreased<br />

with species richness or varied among different<br />

species compositions within richness levels. High<br />

observed/expected RYs (RYo/RYe > 1) of individual<br />

species were mainly due to increased module densities,<br />

whereas low observed/expected RYs (RYo/<br />

RYe < 1) were due to more pronounced decreases<br />

in module density (species with stoloniferous or<br />

creeping growth) or module size (species with<br />

clearly-defined plant individuals). <strong>The</strong> trade-off<br />

between module density and size, typical for<br />

plant populations under the law of constant final<br />

yield, was compensated among species. <strong>The</strong> posi-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 99<br />

tive trait-independent complementarity effect<br />

could be explained by an increase in community<br />

module density, which reached a maximum at<br />

low species richness. In contrast, the increasing<br />

dominance effect was attributable to the speciesspecific<br />

ability, in particular that of A. elatius, to<br />

increase module size, while intrinsic growth limitations<br />

led to a suppression of the remaining species<br />

in many mixtures.<br />

Oecologia, 2007, V154, N3, DEC, pp 535-549.<br />

08.1-162<br />

A Bayesian state-space formulation of dynamic<br />

occupancy models<br />

Royle J A, Kery M<br />

USA, Switzerland<br />

Modelling , Zoology , Instruments & Instrumentation<br />

, Ecology<br />

Species occurrence and its dynamic components,<br />

extinction and colonization probabilities, are focal<br />

quantities in biogeography and metapopulation<br />

biology, and for species conservation assessments.<br />

It has been increasingly appreciated that<br />

these parameters must be estimated separately<br />

from detection probability to avoid the biases induced<br />

by nondetection error. Hence, there is now<br />

considerable theoretical and practical interest in<br />

dynamic occupancy models that contain explicit<br />

representations of metapopulation dynamics<br />

such as extinction, colonization, and turnover as<br />

well as growth rates. We describe a hierarchical<br />

parameterization of these models that is analogous<br />

to the state-space formulation of models in<br />

time series, where the model is represented by<br />

two components, one for the partially observable<br />

occupancy process and another for the observations<br />

conditional on that process. This parameterization<br />

naturally allows estimation of all parameters<br />

of the conventional approach to occupancy<br />

models, but in addition, yields great flexibility<br />

and extensibility, e.g., to modeling heterogeneity<br />

or latent structure in model parameters. We<br />

also highlight the important distinction between<br />

population and finite sample inference; the latter<br />

yields much more precise estimates for the particular<br />

sample at hand. Finite sample estimates can<br />

easily be obtained using the state-space representation<br />

of the model but are difficult to obtain under<br />

the conventional approach of likelihood-based<br />

estimation. We use R and Win BUGS to apply the<br />

model to two examples. In a standard analysis for<br />

the European Crossbill in a large <strong>Swiss</strong> monitoring<br />

program, we fit a model with year-specific<br />

parameters. Estimates of the dynamic parameters<br />

varied greatly among years, highlighting the irruptive<br />

population dynamics of that species. In<br />

the second example, we analyze route occupancy<br />

of Cerulean Warblers in the North American<br />

Breeding Bird Survey (BBS) using a model allowing<br />

for site-specific heterogeneity in model parameters.<br />

<strong>The</strong> results indicate relatively low turnover<br />

and a stable distribution of Cerulean Warblers<br />

which is in contrast to analyses of counts of individuals<br />

from the same survey that indicate important<br />

declines. This discrepancy illustrates the<br />

inertia in occupancy relative to actual abundance.<br />

Furthermore, the model reveals a declining patch<br />

survival probability, and increasing turnover, toward<br />

the edge of the range of the species, which is<br />

consistent with metapopulation perspectives on<br />

the genesis of range edges. Given detection/nondetection<br />

data, dynamic occupancy models as described<br />

here have considerable potential for the<br />

study of distributions and range dynamics.<br />

Ecology, 2007, V88, N7, JUL, pp 1813-1823.<br />

08.1-163<br />

Microsatellite diversity of the agriculturally<br />

important alpine grass Poa alpina in relation<br />

to land use and natural environment<br />

Rudmann Maurer K, Weyand A, Fischer M,<br />

Stöcklin J<br />

Switzerland<br />

Biodiversity , Agriculture, Soil Sciences , Ecology ,<br />

Plant Sciences<br />

Background and Aims <strong>The</strong> Alpine Meadow Grass<br />

Poa alpina is common in subalpine and alpine natural<br />

sites and agriculturally used land, where it is<br />

an important fodder grass. Natural factors and human<br />

land use are supposed to have been shaping<br />

its genetic diversity for hundreds of years. <strong>The</strong> species<br />

comprises sexually and vegetatively reproducing<br />

plants. <strong>The</strong> aim of this study was to investigate<br />

the effects of agricultural land use, environmental<br />

factors and the mode of reproduction on the<br />

distribution of its microsatellite diversity within<br />

and among populations and to analyse whether<br />

its genetic diversity is correlated with plant species<br />

diversity in grassland parcels. Methods Genetic<br />

diversity of P. alpina was assessed with five<br />

microsatellite markers for 569 plants originating<br />

from 20 natural sites and from 54 grassland parcels<br />

of different cultural tradition, land use and<br />

altitude in the <strong>Swiss</strong> Alps. Due to polyploidy and<br />

frequent aneuploidy of the species, data analyses<br />

were based on the presence of microsatellite<br />

bands. Key Results A low but significant differentiation<br />

was found in microsatellite bands among<br />

natural sites and agriculturally used parcels, while<br />

their microsatellite band diversity within populations<br />

did not differ. An increased differentiation<br />

was found in microsatellite bands with increas-


100<br />

ing geographic distance among parcels, and a<br />

differentiation among grazed and mown parcels,<br />

and among sexually and vegetatively reproducing<br />

populations. Band richness of sampled plants per<br />

village was higher for villages where parcels represented<br />

more different land-use types. Within<br />

populations, microsatellite band diversity was<br />

higher in grazed than in mown parcels. Conclusions<br />

<strong>The</strong> diversity of human land use in the Alps<br />

was associated with genetic diversity of P. alpina.<br />

<strong>The</strong>refore, the ongoing socio-economically motivated<br />

land-use changes, which reduce the number<br />

of different land-use types, will affect the genetic<br />

diversity of P. alpina negatively.<br />

Annals of Botany, 2007, V100, N6, NOV, pp<br />

1249-1258.<br />

08.1-164<br />

Recent decline in precipitation and tree<br />

growth in the eastern Mediterranean<br />

Sarris D, Christodoulakis D, Körner C<br />

Greece, Switzerland<br />

Meteorology & Atmospheric Sciences , Plant Sciences<br />

, Forestry<br />

We present evidence of a recent drying in the<br />

eastern Mediterranean, based on weather and<br />

tree-ring data for Samos, an island of the eastern<br />

Aegean Sea. Rainfall declined rapidly after the<br />

late 1970s following trends for the entire Mediterranean<br />

and was associated with reduced tree-ring<br />

width in Pinus brutia. <strong>The</strong> most recent decline<br />

led to the lowest annual radial stem increment<br />

after the last 100 years (as far as records reach).<br />

As moisture availability decreased best correlations<br />

of tree growth with rainfall were obtained<br />

for progressively longer integration periods (1-2<br />

years in moister periods, 5-6 years during the severe<br />

dryness of 20th century’s last decades), suggesting<br />

increasing dependency in deep soil water.<br />

Such long-term integration periods of tree-growth<br />

responses to precipitation have not been reported<br />

before. <strong>The</strong>y may reflect a tree- rooting pattern<br />

adapted to cope with even several successive dry<br />

years. In late summer 2000, moisture reserves became<br />

exhausted, however, and a substantial fraction<br />

of low altitude pines died, including some<br />

80-year-old trees, which underlines the exceptional<br />

extent this trend had reached. Our findings<br />

provide empirical support for Intergovernmental<br />

Panel on Climate <strong>Change</strong> projections derived<br />

from global circulation models that the Mediterranean,<br />

its eastern basin in particular, should become<br />

drier as temperature rises, as was the case in<br />

the recent past.<br />

<strong>Global</strong> <strong>Change</strong> Biology, 2007, V13, N6, JUN, pp<br />

1187-1200.<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

08.1-165<br />

Modeling the forest transition: Forest scarcity<br />

and ecosystem service hypotheses<br />

Satake A, Rudel T K<br />

Switzerland, USA<br />

Modelling , Forestry , Social Sciences , Ecology ,<br />

Economics<br />

An historical generalization about forest cover<br />

change in which rapid deforestation gives way<br />

over time to forest restoration is called “the forest<br />

transition.” Prior research on the forest transition<br />

leaves three important questions unanswered:<br />

(1) How does forest loss influence an individual<br />

landowner’s incentives to reforest? (2) How does<br />

the forest recovery rate affect the likelihood of<br />

forest transition? (3) What happens after the forest<br />

transition occurs? <strong>The</strong> purpose of this paper is<br />

to develop a minimum model of the forest transition<br />

to answer these questions. We assume that<br />

deforestation caused by landowners’ decisions<br />

and forest regeneration initiated by agricultural<br />

abandonment have aggregated effects that characterize<br />

entire landscapes. <strong>The</strong>se effects include<br />

feedback mechanisms called the “forest scarcity”<br />

and “ecosystem service” hypotheses. In the forest<br />

scarcity hypothesis, forest losses make forest products<br />

scarcer, which increases the economic value<br />

of forests. In the ecosystem service hypothesis, the<br />

environmental degradation that accompanies the<br />

loss of forests causes the value of ecosystem services<br />

provided by forests to decline. We examined the<br />

impact of each mechanism on the likelihood of<br />

forest transition through an investigation of the<br />

equilibrium and stability of landscape dynamics.<br />

We found that the forest transition occurs only<br />

when landowners employ a low rate of future discounting.<br />

After the forest transition, regenerated<br />

forests are protected in a sustainable way if forests<br />

regenerate slowly. When forests regenerate rapidly,<br />

the forest scarcity hypothesis expects instability<br />

in which cycles of large- scale deforestation<br />

followed by forest regeneration repeatedly characterize<br />

the landscape. In contrast, the ecosystem<br />

service hypothesis predicts a catastrophic shift<br />

from a forested to an abandoned landscape when<br />

the amount of deforestation exceeds the critical<br />

level, which can lead to a resource degrading<br />

poverty trap. <strong>The</strong>se findings imply that incentives<br />

for forest conservation seem stronger in settings<br />

where forests regenerate slowly as well as when<br />

decision makers value the future.<br />

Ecological Applications, 2007, V17, N7, OCT, pp<br />

2024-2036.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 101<br />

08.1-166<br />

Ecological niche modelling of two cryptic bat<br />

species calls for a reassessment of their conservation<br />

status<br />

Sattler T, Bontadina F, Hirzel A H, Arlettaz R<br />

Switzerland<br />

Modelling , Ecology , Biodiversity , Zoology<br />

It is difficult to establish conservation priorities<br />

for cryptic species when their ecological requirements<br />

are confounded by problems with species<br />

identification. In some cases, such as Chiroptera,<br />

cryptic taxa may actually consist of both widespread,<br />

abundant species and localized, rare species.<br />

Discrimination between these species may<br />

be facilitated by phenotypic, species-specific traits<br />

such as echolocation calls. Echolocation studies<br />

supported by genetic data have revealed that<br />

one of the most abundant bat species in Europe<br />

actually consists of two cryptic species: Pipistrellus<br />

pipistrellus and P. pygmaeus. We recorded<br />

echolocation calls from both species along road<br />

transects in Switzerland to study their distribution<br />

and abundance. Using Ecological Niche Factor<br />

Analysis and discriminant analysis, we characterized<br />

species-specific habitat requirements,<br />

built habitat suitability maps and examined interspecific<br />

differences in niche parameters. <strong>The</strong><br />

presence of P. pygmaeus was associated with landscape<br />

matrices comprising large rivers and lakes,<br />

human settlements and open woodland. P. pipistrellus<br />

utilized similar habitat matrices but was<br />

far more tolerant to deviations from its optimal<br />

habitat. P. pygmaeus occupied a much narrower<br />

ecological niche, encompassed mainly within that<br />

of its sister taxon. Synthesis and applications. P.<br />

pipistrellus is ranked as ‘not threatened’ in Switzerland.<br />

<strong>The</strong> results from this study indicate an<br />

abundance approximately 30 times higher than<br />

that of P. pygmaeus. In contrast, P. pygmaeus is<br />

distributed patchily and occurs at comparatively<br />

low densities. We recommend reclassification of<br />

P. pygmaeus as ‘rare and potentially threatened’.<br />

Conservation of P. pygmaeus should focus on the<br />

management of riparian woodland in areas with<br />

a high probability of occurrence. This study emphasizes<br />

the need to recognize the potential existence<br />

of cryptic taxa so that effective conservation<br />

management of rare species can be put into place<br />

before they are seriously endangered.<br />

Journal of Applied Ecology, 2007, V44, N6, DEC,<br />

pp 1188-1199.<br />

08.1-167<br />

Use of integrated modeling to enhance estimates<br />

of population dynamics obtained from<br />

limited data<br />

Schaub M, Gimenez O, Sierro A, Arlettaz R<br />

Switzerland, Scotland, France<br />

Modelling , Zoology , Ecology , Biodiversity<br />

Demographic data of rare and endangered species<br />

are often too sparse to estimate vital rates<br />

and population size with sufficient precision for<br />

understanding population growth and decline.<br />

Yet, the combination of different sources of demographic<br />

data into one statistical model holds<br />

promise. We applied Bayesian integrated population<br />

modeling to demographic data from a colony<br />

of the endangered greater horseshoe bats (Rhinolophus<br />

ferrumequinum). Available data were the<br />

number of subadults and adults emerging from<br />

the colony roost at dusk, the number of newborns<br />

from 1991 to 2005, and recapture data of subadults<br />

and adults from 2004 and 2005. Survival rates did<br />

not differ between sexes, and demographic rates<br />

remained constant across time. <strong>The</strong> greater horseshoe<br />

bat is a long-lived species with high survival<br />

rates (first year: 0.49 (SD 0.06); adults: 0.91 (SD<br />

0.02)) and low fecundity (0.74 (SD 0.12)). <strong>The</strong> yearly<br />

average population growth was 4.4% (SD 0.1%) and<br />

there were 92 (SD 10) adults in the colony in year<br />

2005. Had we analyzed each data set separately,<br />

we would not have been able to estimate fecundity,<br />

the estimates of survival would have been less<br />

precise, and the estimate of population growth<br />

biased. Our results demonstrate that integrated<br />

models are suitable for obtaining crucial demographic<br />

information from limited data.<br />

Conservation Biology, 2007, V21, N4, AUG, pp<br />

945-955.<br />

08.1-168<br />

Tree species richness affects litter production<br />

and decomposition rates in a tropical biodiversity<br />

experiment<br />

Scherer Lorenzen M, Bonilla J L, Potvin C<br />

Switzerland, Panama, Canada<br />

Forestry , Plant Sciences , Biodiversity , Ecology<br />

We report data on leaf litter production and decomposition<br />

from a manipulative biodiversity<br />

experiment with trees in tropical Panama, which<br />

has been designed to explore the relationship between<br />

tree diversity and ecosystem functioning. A<br />

total of 24 plots (2025 m(2)) were established in<br />

2001 using six native tree species, with 1-, 3-, and<br />

6-species mixtures. We estimated litter production<br />

during the dry season 2005 with litter traps;<br />

decomposition was assessed with a litter bag approach<br />

during the following wet season. Litter


102<br />

production during the course of the dry season<br />

was highly variable among the tree species. Tree<br />

diversity significantly affected litter production,<br />

and the majority of the intermediate diverse mixtures<br />

had higher litter yields than expected based<br />

on yields in monoculture. In contrast, high diverse<br />

mixtures did not show such overyielding in<br />

litter production. Litter decomposition rates were<br />

also highly species-specific, and were related to<br />

various measures of litter quality (C/N, lignin/N,<br />

fibre content). We found no overall effect of litter<br />

diversity if the entire litter mixtures were analyzed,<br />

i.e. mixing species resulted in pure additive<br />

effects and observed decomposition rates were<br />

not different from expected rates. However, the<br />

individual species changed their decomposition<br />

pattern depending on the diversity of the litter<br />

mixture, i.e. there were species-specific responses<br />

to mixing litter. <strong>The</strong> analysis of temporal C and<br />

N dynamics within litter mixtures gave only limited<br />

evidence for nutrient transfer among litters<br />

of different quality. At this early stage of our tree<br />

diversity experiment, there are no coherent and<br />

general effects of tree species richness on both<br />

litter production and decomposition. Within the<br />

scope of the biodiversity- ecosystem functioning<br />

relationship, our results therefore highlight the<br />

process-specific effects diversity may have. Additionally,<br />

species-specific effects on ecosystem<br />

processes and their temporal dynamics are important,<br />

but such effects may change along the gradient<br />

of tree diversity.<br />

Oikos, 2007, V116, N12, DEC, pp 2108-2124.<br />

08.1-169<br />

Exploring the functional significance of forest<br />

diversity: A new long-term experiment with<br />

temperate tree species (BIOTREE)<br />

Scherer Lorenzen M, Schulze E D, Don A, Schumacher<br />

J, Weller E<br />

Switzerland, Germany<br />

Ecology , Plant Sciences , Biodiversity , Forestry<br />

Effects of biodiversity on ecosystem functioning<br />

have been mainly studied in experiments that<br />

artificially create gradients in grassland plant diversity.<br />

Woody species were largely excluded from<br />

these early experiments, despite the ecological<br />

and socioeconomic importance of forest ecosystems.<br />

We discuss conceptual aspects of mechanistically<br />

driven research on the biodiversity-ecosystem<br />

functioning relationship in forests, including<br />

the comparison of scientific approaches like ‘observational<br />

studies’, ‘removal experiments’, and<br />

‘synthetic-assemblage experiments’. We give a<br />

short overview on the differences between herbaceous<br />

and forest ecosystems, focusing on can-<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

opy characteristics, and the possibilities for individual<br />

versus population-based investigations.<br />

We present detailed information about the first<br />

large-scale, multisite and long-term biodiversityecosystem<br />

functioning experiment with tree species<br />

of temperate forests (BIOTREE - BIOdiversity<br />

and ecosystem processes in experimental TREE<br />

stands). At three sites of differing geology and local<br />

climate, we planted 200,000 saplings on a total<br />

area of 70 ha. At two sites, diversity gradients were<br />

established by varying the number of tree species<br />

(BIOTREE-SPECIES). At a third site, only functional<br />

diversity at a constant level of tree species<br />

richness was manipulated by selecting mixtures<br />

that differ in the functional trait values of the<br />

corresponding species (BIOTREE-FD). Additional<br />

experimental treatments at the subplot level include<br />

silvicultural management options, the addition<br />

of subdominant species, and the reduction<br />

of genetic diversity. Response variables focus on<br />

productivity, biogeochemical cycles and carbon<br />

sequestration, and resource use complementarity.<br />

We explore the use of different measures of functional<br />

diversity for a posteriori classifications of<br />

functional richness and their use in the analysis<br />

of our tree diversity experiment. <strong>The</strong> experiment<br />

is thought to provide a long-term research platform<br />

for a variety of scientific questions related to<br />

forest biodiversity and ecosystem processes.<br />

Perspectives in Plant Ecology Evolution and Systematics,<br />

2007, V9, N2, pp 53-70.<br />

08.1-170<br />

Patterns of variation of a common fern<br />

(Athyrium filix-femina; Woodsiaceae): Population<br />

structure along and between altitudinal<br />

gradients<br />

Schneller J, Liebst B<br />

Switzerland<br />

Plant Sciences , Ecology , Biodiversity<br />

Genetic variability of Athyrium filix-femina populations<br />

was evaluated with regard to phenotypic,<br />

allozyme, and RAPD variation in 20 <strong>Swiss</strong> populations<br />

along five altitudinal gradients at four<br />

different elevations in the northern <strong>Swiss</strong> Alps.<br />

Additionally, allozyme and phenotypic variations<br />

in one Italian and two Spanish populations were<br />

compared with the variation in the <strong>Swiss</strong> populations.<br />

We hypothesized that there will be statistically<br />

significant genetic differences among populations<br />

of different altitudes and sites. <strong>The</strong> results<br />

showed no substantial correlation between genetic<br />

variation and phenotypic variation among <strong>Swiss</strong><br />

populations. <strong>The</strong>se results imply that outbreeding<br />

and effective gene exchange (long-distance spore<br />

dispersal) are the keys to population structure


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 103<br />

in this fern species, and as a consequence, phenotypic<br />

plasticity is assumed to be favored. This<br />

contrasts with results found in similar studies<br />

of herbaceous flowering plants where genetic<br />

adaptation to gradients like altitude is common.<br />

However, when data from the more distant Italian<br />

and Spanish populations of A. filix- femina were<br />

included, significant variation was detected.<br />

American Journal of Botany, 2007, V94, N6, JUN,<br />

pp 965-971.<br />

08.1-171<br />

Examining native and exotic species diversity<br />

in European riparian forests<br />

Schnitzler A, Hale B W, Alsum E M<br />

Switzerland, France, USA<br />

Plant Sciences , Ecology , Biodiversity , Forestry<br />

This study performs a meta-analysis of existing<br />

studies of European riparian forests to investigate<br />

which exotic species have successfully established<br />

in intact riparian forests and which characteristics<br />

of these forests correspond with successful establishment.<br />

We used analysis of covariance models<br />

to investigate the relationship between community<br />

species richness, percent exotic species, and<br />

several environmental variables. We found a total<br />

richness of 1380 species, of which 45 (3.3%) were<br />

exotic. Species- rich communities generally had<br />

the higher percentage of exotics, but were not<br />

significantly related to latitude or environmental<br />

variables. Exotics, in contrast, were at generally<br />

higher levels at lower latitudes and were more<br />

abundant in large river plains and communities<br />

with intermediate levels of disturbance. <strong>The</strong>se<br />

results suggest that future climate change and<br />

human actions that mimic intermediate levels of<br />

disturbance may further enhance the spread of<br />

exotic species.<br />

Biological Conservation, 2007, V138, N1-2, AUG,<br />

pp 146-156.<br />

08.1-172<br />

Speciation reversal and biodiversity dynamics<br />

with hybridization in changing environments<br />

Seehausen O, Takimoto G, Roy D, Jokela J<br />

Switzerland, USA<br />

Biodiversity , Ecology<br />

A considerable fraction of the world’s biodiversity<br />

is of recent evolutionary origin and has evolved<br />

as a by-product of, and is maintained by, divergent<br />

adaptation in heterogeneous environments.<br />

Conservationists have paid attention to genetic<br />

homogenization caused by human-induced translocations<br />

(e.g. biological invasions and stocking),<br />

and to the importance of environmental heterogeneity<br />

for the ecological coexistence of species.<br />

However, far less attention has been paid to the<br />

consequences of loss of environmental heterogeneity<br />

to the genetic coexistence of sympatric species.<br />

Our review of empirical observations and our<br />

theoretical considerations on the causes and consequences<br />

of interspecific hybridization suggest<br />

that a loss of environmental heterogeneity causes<br />

a loss of biodiversity through increased genetic<br />

admixture, effectively reversing speciation. Loss<br />

of heterogeneity relaxes divergent selection and<br />

removes ecological barriers to gene flow between<br />

divergently adapted species, promoting interspecific<br />

introgressive hybridization. Since heterogeneity<br />

of natural environments is rapidly deteriorating<br />

in most biomes, the evolutionary ecology<br />

of speciation reversal ought to be fully integrated<br />

into conservation biology.<br />

Molecular Ecology, 2008, V17, N1, JAN, pp 30-44.<br />

08.1-173<br />

Altitudinal and horizontal shifts of the upper<br />

boundaries of open and closed forests in the<br />

Polar Urals in the 20th century<br />

Shiyatov S G, Terentev M M, Fomin V V, Zimmermann<br />

N E<br />

Russia, Switzerland<br />

Meteorology & Atmospheric Sciences , Forestry ,<br />

Plant Sciences , Ecology<br />

In the Polar Urals (the Rai-Iz massif and Mounts<br />

Tchernaya and Malaya Tchernaya), altitudinal and<br />

horizontal shifts of the upper boundary of open<br />

and closed larch forests in the 20th century have<br />

been studied. Spatiotemporal parameters of these<br />

shifts have been assessed with the aid of the ARC/<br />

INFO geographic information system (ESRI Inc.,<br />

United States), using our original large-scale geobotanical<br />

maps showing the distribution of different<br />

types of forest-tundra communities in the<br />

early 1910s and 2000s. <strong>The</strong> results show that tree<br />

vegetation has been actively expanding to higher<br />

elevations over the past 90 years. On average, the<br />

upper boundaries of open and closed forests have<br />

ascended 26 and 35 m and shifted horizontally<br />

290 and 520 m, respectively. <strong>The</strong>se shifts have been<br />

conditioned by climate warming and increasing<br />

humidity observed since the 1920s.<br />

Russian Journal of Ecology, 2007, V38, N4, JUL, pp<br />

223-227.<br />

08.1-174<br />

Temperate grasslands and global atmospheric<br />

change: a review<br />

Soussana J F, Lüscher A<br />

France, Switzerland<br />

Meteorology & Atmospheric Sciences , Plant Sciences<br />

, Ecology , Agriculture, Soil Sciences


104<br />

Recent reviews confirm and extend previous observations<br />

that elevated carbon dioxide (COD<br />

concentrations Stimulate photosyn thesis, leading<br />

to increased plant productivity. Elevated CO 2<br />

concentrations tend to reduce the sensitivity of<br />

grassland ecosystems to low levels of precipitation<br />

but induce progressive nitrogen (N) limitations<br />

on plant growth which can be alleviated<br />

by supplying a significant external input of N in<br />

the form of mineral fertilizer or through the increased<br />

use of N-fixing legumes. Other nutrients,<br />

such as phosphorus, can act as the main limiting<br />

factor restricting the growth response in legumes<br />

to atmospheric CO 2 concentration. <strong>The</strong> botanical<br />

composition of temperate grasslands is affected<br />

by the rise in atmospheric CO 2 concentration, possibly<br />

through a decline in the relaTive abundance<br />

of grasses. Elevated CO 2 concentration will also<br />

alter the feeding value of herbage to grazers both<br />

in terms of fine- scale (for example, crude protein<br />

concentration and C:N ratio) and coarse-scale (legumes<br />

vs. grasses and C-3- VS. C-4-species) changes.<br />

<strong>The</strong> management guidelines of grasslands will<br />

need to be adapted to global atmospheric and<br />

climatic changes and to increased variability in<br />

climate.<br />

Grass and Forage Science, 2007, V62, N2, JUN, pp<br />

127-134.<br />

08.1-175<br />

Conservation of grasshopper diversity in a<br />

changing environment<br />

Steck C E, Bürgi M, Bolliger J, Kienast F, Lehmann<br />

A, Gonseth Y<br />

Switzerland<br />

Biodiversity , Ecology , Zoology , Agriculture, Soil<br />

Sciences<br />

Land-use change is a major driver for changes in<br />

biodiversity. In this study, we investigated how the<br />

objectives of two conservation strategies (largescale<br />

conservation of species richness versus conservation<br />

of diversity hotspots) can be achieved<br />

for grasshopper diversity under different scenarios<br />

of environmental change (land-use and climate<br />

change). Based on surveys of 95 grasshopper<br />

species from 2001 to 2004 recorded by the <strong>Swiss</strong><br />

Centre for Faunal Cartography, we modelled the<br />

actual richness pattern as a function of different<br />

environmental variables. <strong>The</strong> impact of potential<br />

future environmental change on species richness<br />

was evaluated by applying four land-use scenarios<br />

(‘liberalization’, ‘business as usual’, ‘lowered agricultural<br />

production’, and ‘complete conversion<br />

of intensive open land’) and one climate change<br />

scenario. <strong>The</strong> effects of the scenarios were assessed<br />

at the national scale, as well as on small-<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

scale hotspots. Environmental change has considerable<br />

effect on grasshopper species richness.<br />

At the national scale, the number of grasshopper<br />

species decreased under the ‘liberalization’ scenario<br />

(-0.24 species per 1 ha pixel) and increased<br />

under a climate change scenario (+0.63 species<br />

per 1 ha pixel). For most environmental change<br />

scenarios, species richness in small-scale hotspots<br />

was more negatively affected than on average on<br />

the national scale. <strong>The</strong> response of species richness<br />

to the scenarios did not differ significantly<br />

between hotspots of endangered and the hotspots<br />

of common grasshopper species. We conclude<br />

that conservation efforts at the national scale<br />

and small-scale hotspot conservation programs<br />

should be combined to conserve species richness<br />

most successfully. For the long-term conservation<br />

of species richness, common species as well as the<br />

combined effects of land-use and climate change<br />

have to be considered.<br />

Biological Conservation, 2007, V138, N3-4, SEP, pp<br />

360-370.<br />

08.1-176<br />

Hotspots and richness pattern of grasshopper<br />

species in cultural landscapes<br />

Steck C E, Bürgi M, Coch T, Duelli P<br />

Switzerland<br />

Zoology , Biodiversity , Ecology , Agriculture, Soil<br />

Sciences<br />

<strong>The</strong> success of the hotspot approach for biodiversity<br />

conservation depends on the spatial scale and<br />

the indicator species used. In this study, we investigated<br />

grasshopper species richness in Switzerland<br />

at a 1 ha resolution including a total of 111<br />

species. We compared the representativeness of<br />

common and of endangered grasshopper species<br />

for the overall grasshopper species richness and<br />

we assessed the efficiency of the hotspot approach<br />

for grasshopper conservation. <strong>The</strong> pattern of overall<br />

grasshopper species richness was well represented<br />

by both the number of common and the<br />

number of endangered grasshopper species. For<br />

evaluating the efficiency of different hotspot approaches<br />

for conservation, we compared hotspots<br />

of common species, hotspots of endangered species<br />

(rarity hotspots), and hotspots of all grasshopper<br />

species (richness hotspots). Among these<br />

hotspot types, richness hotspots not only featured<br />

most common grasshopper species, but they even<br />

contained more endangered species than the rarity<br />

hotspots. <strong>The</strong> combination of rarity hotspots<br />

and hotspots of common species featured more<br />

species than the other combinations of hotspot<br />

types. However, the gain of combining two hotspot<br />

types compared to the single-hotspot approach


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 105<br />

was low (max. 3 species). About 24% of the species<br />

were not contained in any of the hotspots. <strong>The</strong>se<br />

grasshopper species require species-specific action<br />

plans. As rarity hotspots were located in areas that<br />

are rather strongly affected by landscape change,<br />

species richness in rarity hotspots may decrease<br />

in the future. We conclude that, for grasshoppers,<br />

the hotspot approach on the 1 ha scale can be an<br />

effective way to conserve a high proportion of species<br />

richness.<br />

Biodiversity and Conservation, 2007, V16, N7, JUN,<br />

pp 2075-2086.<br />

08.1-177<br />

Floral free fall in the <strong>Swiss</strong> lowlands: environmental<br />

determinants of local plant extinction<br />

in a peri-urban landscape<br />

Stehlik I, Caspersen J P, Wirth L, Holderegger R<br />

Switzerland, Canada<br />

Plant Sciences , Urban Studies , Biodiversity , Ecology<br />

, Agriculture, Soil Sciences<br />

1. Local floras are being depleted by a host of human<br />

activities, including habitat destruction and<br />

fragmentation, eutrophication, and the intensification<br />

of agriculture. Species with particular ecological<br />

demands or life-history attributes are more<br />

prone to extinction than species with a broader<br />

niche. 2. We used an old herbarium from the municipality<br />

of Kusnacht (<strong>Swiss</strong> lowlands) as a historical<br />

record for comparison with contemporary<br />

plant diversity. This comparison revealed that 17%<br />

to 28% of all vascular plants that occurred between<br />

1839 and 1915 were extinct by 2003. 3. Species of<br />

different habitats and life-forms had significantly<br />

different rates of extinction: wetlands, disturbed<br />

sites and meadows lost most species, whereas forests<br />

and rocky habitats were least affected; aquatics<br />

and annuals were most prone to extinction,<br />

geophytes and hemicryptophytes were intermediate,<br />

and phanerophytes and chamaephytes were<br />

least affected. 4. Species adapted to nutrient-poor<br />

soils suffered highest extinction in all habitats,<br />

indicating that eutrophication poses an urgent<br />

threat to species diversity. Light and soil moisture<br />

requirements also had significant effects on extinction,<br />

but the direction of the effect varied by<br />

habitat. 5. When species were grouped into IUCN<br />

categories of the red list of Switzerland, the rank<br />

order of the observed extinction matched the red<br />

list assignment. 6. Because many of the remaining<br />

species had high estimated extinction probabilities<br />

and because extinction is often delayed<br />

(extinction debt), a substantial part of the remaining<br />

flora of Kusnacht is likely to go extinct in the<br />

near future. This will increase the dominance of<br />

the common species that already comprise 81% of<br />

the local flora. 7. <strong>The</strong> rates and patterns of extinction<br />

in Kusnacht are probably representative of<br />

surrounding <strong>Swiss</strong> lowlands and peri-urban landscapes<br />

in most developed countries. Studies such<br />

as ours can serve as a call for action and form a<br />

basis for future monitoring of biodiversity.<br />

Journal of Ecology, 2007, V95, N4, JUL, pp<br />

734-744.<br />

08.1-178<br />

Cooccurring Gentiana verna and Gentiana<br />

acaulis and their neighboring plants in two<br />

swiss upper montane meadows harbor distinct<br />

arbuscular mycorrhizal fungal communities<br />

Sykorova Z, Wiemken A, Redecker D<br />

Switzerland<br />

Plant Sciences , Biodiversity , Ecology<br />

<strong>The</strong> community composition of arbuscular mycorrhizal<br />

fungi (AMF) was analyzed in roots of Gentiana<br />

verna, Gentiana acaulis, and accompanying<br />

plant species from two species-rich <strong>Swiss</strong> alpine<br />

meadows located in the same area. <strong>The</strong> aim of the<br />

study was to elucidate the impact of host preference<br />

or host specificity on the AMF community in<br />

the roots. <strong>The</strong> roots were analyzed by nested PCR,<br />

restriction fragment length polymorphism screening,<br />

and sequencing of ribosomal DNA small-subunit<br />

and internal transcribed spacer regions. <strong>The</strong><br />

AMF sequences were analyzed phylogenetically<br />

and used to define monophyletic sequence types.<br />

<strong>The</strong> AMF community composition was strongly<br />

influenced by the host plant species, but compositions<br />

did not significantly differ between the two<br />

sites. Detailed analyses of the two cooccurring<br />

gentian species G. verna and G. acaulis, as well as<br />

of neighboring Trifolium spp., revealed that their<br />

AMF communities differed significantly. All three<br />

host plant taxa harbored AMF communities comprising<br />

multiple phylotypes from different fungal<br />

lineages. A frequent fungal phylotype from Glomus<br />

group B was almost exclusively found in Trifolium<br />

spp., suggesting some degree of host preference<br />

for this fungus in this habitat. In conclusion, the<br />

results indicate that within a relatively small area<br />

with similar soil and climatic conditions, the host<br />

plant species can have a major influence on the<br />

AMF communities within the roots. No evidence<br />

was found for a narrowing of the mycosymbiont<br />

spectrum in the two green gentians, in contrast<br />

to previous findings with their achlorophyllous<br />

relatives.<br />

Applied and Environmental Microbiology, 2007,<br />

V73, N17, SEP, pp 5426-5434.


106<br />

08.1-179<br />

An improved canopy integration scheme for<br />

a land surface model with prognostic canopy<br />

structure<br />

Thornton P E, Zimmermann N E<br />

USA, Switzerland<br />

Modelling , Forestry , Plant Sciences , Ecology<br />

A new logical framework relating the structural<br />

and functional characteristics of a vegetation canopy<br />

is presented, based on the hypothesis that the<br />

ratio of leaf area to leaf mass (specific leaf area)<br />

varies linearly with overlying leaf area index within<br />

the canopy. Measurements of vertical gradients<br />

in specific leaf area and leaf carbon:nitrogen<br />

ratio for five species (two deciduous and three<br />

evergreen) in a temperate climate support this<br />

hypothesis. This new logic is combined with a<br />

two-leaf (sunlit and shaded) canopy model to arrive<br />

at a new canopy integration scheme for use in<br />

the land surface component of a climate system<br />

model. An inconsistency in the released model<br />

radiation code is identified and corrected. Also introduced<br />

here is a prognostic canopy model with<br />

coupled carbon and nitrogen cycle dynamics. <strong>The</strong><br />

new scheme is implemented within the Community<br />

Land Model and tested in both diagnostic<br />

and prognostic canopy modes. <strong>The</strong> new scheme<br />

increases global gross primary production by 66%<br />

(from 65 to 108 Pg carbon yr(-1)) for diagnostic<br />

model simulations driven with reanalysis surface<br />

weather, with similar results (117 PgC yr (-1)) for<br />

the new prognostic model. Comparison of model<br />

predictions to global syntheses of observations<br />

shows generally good agreement for net primary<br />

productivity (NPP) across a range of vegetation<br />

types, with likely underestimation of NPP in tundra<br />

and larch communities. Vegetation carbon<br />

stocks are higher than observed in forest systems,<br />

but the ranking of stocks by vegetation type is accurately<br />

captured.<br />

Journal of Climate, 2007, V20, N15, AUG 1, pp<br />

3902-3923.<br />

08.1-180<br />

Fitness-related parameters improve presenceonly<br />

distribution modelling for conservation<br />

practice: <strong>The</strong> case of the red-backed shrike<br />

Titeux N, Dufrene M, Radoux J, Hirzel A H, Defourny<br />

P<br />

Belgium, Switzerland<br />

Modelling , Biodiversity , Ecology , Zoology<br />

<strong>The</strong> red-backed shrike (Lanius collurio L.) is a bird<br />

living in human- altered agricultural areas that<br />

are managed by extensive farming techniques.<br />

This passerine species has declined significantly<br />

in Western Europe over the last 30-40 years. <strong>The</strong><br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

development of efficient species-specific conservation<br />

strategies relies on fine- grained information<br />

about the ecological resources and environmental<br />

conditions that constitute its reproductive habitat<br />

in this agricultural landscape. Species distribution<br />

models are used increasingly in conservation<br />

biology to provide such information. Most studies<br />

investigate the environmental pattern of species<br />

distribution, assuming that species records are<br />

reliable indicators of habitat suitability. However,<br />

ecological theory on source-sink dynamics and<br />

ecological traps points out that some individuals<br />

may be located outside the environmental bounds<br />

of their species’ reproductive niche. Those individuals<br />

could reduce model accuracy and limit<br />

model utility. Parameters related to the reproductive<br />

success of this shrike in Southern Belgium<br />

were integrated into a fine-scale presence-only<br />

modelling framework to demonstrate this problem<br />

and to address critical habitat requirements<br />

of this species relative to conservation management.<br />

Integrating reproductive parameters into<br />

the modelling framework showed that individuals<br />

occurred, but did not reproduce successfully,<br />

above a certain environmental threshold. This indicated<br />

that the reproductive niche of the shrike<br />

is ecologically narrower than standard practice in<br />

species distribution modelling would suggest. <strong>The</strong><br />

major resources (nest sites availability, distance to<br />

human settlements, suitable perching sites, foraging<br />

areas and insect abundance) required for the<br />

reproduction of the red-backed shrike were quantified<br />

and ranked to offer concrete species -specific<br />

conservation management guidelines<br />

Biological Conservation, 2007, V138, N1-2, AUG,<br />

pp 207-223.<br />

08.1-181<br />

Response of Pinus leucodermis to climate and<br />

anthropogenic activity in the National Park of<br />

Pollino (Basilicata, Southern Italy)<br />

Todaro L, Andreu L, D’alessandro C M, Gutirrez E,<br />

Cherubinic P, Saracino A<br />

Italy, Spain, Switzerland<br />

Forestry , Plant Sciences , Ecology , Biodiversity<br />

Pinus leucodermis (=P. heldreichii var. leucodermis)<br />

is widespread in the Balkan Peninsula and is<br />

present as a post-glacial relict in Southern Italy.<br />

<strong>The</strong> oldest Italian populations of this species are<br />

located at high elevation in the National Park of<br />

Pollino, where grazing and logging had endangered<br />

their survival, especially during the 20th<br />

century. In 1993 the National Park was founded<br />

and anthropogenic activities were restricted. To<br />

understand the response of P. leucodermis at the<br />

upper tree-line to climatic and anthropogenic ac-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 107<br />

tivity variations, we developed a tree-ring width<br />

chronology (1464-2003). For the period 1804-2003<br />

separate chronologies for the earlywood and latewood<br />

were built, and resin duct density was assessed<br />

on total ring, earlywood and latewood. Age<br />

structure of saplings was also determined. After<br />

1950 a steep decline in tree-ring width was followed<br />

by a recovery since 1981. During the 20th<br />

century radial growth response to climate was not<br />

strong and not stable. In the period 19532000 P.<br />

leucadermis radial growth seemed to take advantage<br />

of high temperatures and low precipitation.<br />

Resin duct density chronologies were not a reliable<br />

dendroecological variable, but they documented<br />

a metabolic trade-off between growth and differentiation<br />

processes. <strong>The</strong> gap in the age structure<br />

between long- lived trees (over 200 years old) and<br />

saplings around 40 years old, which mainly grow<br />

in protected microsites between rocks, could indicate<br />

a negative influence of grazing and related<br />

human activities. We suggest that the protection<br />

strategies introduced by the National Park could<br />

play a positive role in the recruitment of new saplings<br />

and in the ring growth recovery of old trees<br />

of P. leucodermis.<br />

Biological Conservation, 2007, V137, N4, JUL, pp<br />

507-519.<br />

08.1-182<br />

Regional assessment of climate change impacts<br />

on maize productivity and associated<br />

production risk in Switzerland<br />

Torriani D S, Calanca P, Lips M, Ammann H, Beniston<br />

M, Fuhrer J<br />

Switzerland<br />

Agriculture, Soil Sciences , Modelling , Ecology ,<br />

Plant Sciences<br />

A simple model of yield was used along with climate<br />

scenarios to assess the impact of climate<br />

change on grain maize productivity and associated<br />

economic risk in Switzerland. In a first application,<br />

changes in the precipitation regime<br />

alone were shown to affect the distribution of<br />

yield considerably, with shifts not only in the<br />

mean but also in the standard deviation and the<br />

skewness. Production risk was found to respond<br />

more markedly to changes in the long-term mean<br />

than in the inter-annual variability of seasonal<br />

precipitation amounts. In a further application,<br />

yield projections were generated with respect to a<br />

full climate scenario, with the emission pathway<br />

as specified in the IPCC A2 scenario. Anticipation<br />

of the sowing date was found to reduce the negative<br />

impact of climate change on yield stability,<br />

but was not sufficient to ensure average productivity<br />

levels comparable to those observed at pres-<br />

ent. We argued that this was caused by the reduction<br />

in the duration of the growing season, which<br />

had a stronger impact than suggested by previous<br />

studies. Assuming no change in price relations,<br />

the results also revealed a strong increase in production<br />

risk with climate change, with more than<br />

a doubling in the probability of yield falling short<br />

of a critical threshold as compared to today’s situation.<br />

Regional Environmental <strong>Change</strong>, 2007, V7, N4,<br />

DEC, pp 209-221.<br />

08.1-183<br />

Potential effects of changes in mean climate<br />

and climate variability on the yield of winter<br />

and spring crops in Switzerland<br />

Torriani D S, Calanca P, Schmid S, Beniston M,<br />

Fuhrer J<br />

Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences ,<br />

Agriculture, Soil Sciences , Ecology , Biodiversity<br />

Climate change is expected to affect both the average<br />

level and the variability of crop yields. In<br />

this modelling study, we quantified mean and<br />

inter-annual variability of grain yield for maize<br />

Zea mays L., winter wheat Triticum spp. L. and<br />

winter canola Brassica napus L. for climatic conditions<br />

corresponding to current and doubled atmospheric<br />

CO 2 concentrations. Climate scenarios<br />

with and without taking into account changes<br />

in the inter-annual variability of climate were<br />

developed from the output of a regional climate<br />

model for the time window 2071 to 2100. Climate<br />

change effects on the mean yield of maize and<br />

canola were consistently negative, but a positive<br />

impact was simulated for mean yield of winter<br />

wheat for elevated CO 2 concentration. <strong>The</strong> coefficient<br />

of yield variation increased in the scenarios<br />

for maize and canola, but decreased for wheat.<br />

Higher thermal time requirements increased<br />

mean yield and reduced yield variability for all<br />

crops. Shifts in the sowing dates had a beneficial<br />

impact on the yield of maize, but not on the yield<br />

of canola and wheat. It is concluded that in the Alpine<br />

region, the potential effect of climate change<br />

is crop-specific. However, the introduction of new<br />

cultivars may provide means by which to maintain<br />

or even increase current productivity levels<br />

for most of the crops.<br />

Climate Research, 2007, V34, N1, JUN 14, pp<br />

59-69.


108<br />

08.1-184<br />

Effect of supplementation of fresh and ensiled<br />

clovers to ryegrass on nitrogen loss and methane<br />

emission of dairy cows<br />

van Dorland H A, Wettstein H R, Leuenberger H,<br />

Kreuzer M<br />

Switzerland<br />

Zoology , Agriculture, Soil Sciences<br />

Two experiments were carried out to compare<br />

white clover with red clover as supplementation to<br />

ryegrass, in ensiled and fresh form, for differences<br />

in nitrogen loss and methane emission by dairy<br />

cows. In experiment 1, fresh ryegrass was mixed<br />

with fresh white (WF) or red clover (RF) (60/40 on<br />

dry matter basis). Experiment 2 involved similar<br />

mixed diets in ensiled form (WS and RS, respectively),<br />

and two ryegrass silage diets, without (GS)<br />

or with supplementary maize gluten meal (600 g<br />

protein/kg DM; GS+). Barley was supplemented to<br />

meet the calculated requirements for milk production.<br />

<strong>The</strong> type of clover did not affect crude<br />

protein (CP) intake in experiment 1. In experiment<br />

2, the highest CP intakes were observed for cows<br />

on the GS+ diet (P


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 109<br />

tive power of the models and the obtained r ranging<br />

from 0.5 for lichens on soil to 0.8 for lichens<br />

on trees can be regarded as satisfactory to good,<br />

respectively. <strong>The</strong> study revealed that a combination<br />

of airborne and spaceborne remote sensing<br />

data produced a variety of ecological meaningful<br />

variables.<br />

Environmental Modeling Assessment, 2007, V12,<br />

N4, NOV, pp 315-328.<br />

08.1-188<br />

Radial growth responses to drought of Pinus<br />

sylvestris and Quercus pubescens in an inner-<br />

Alpine dry valley<br />

Weber P, Bugmann H, Rigling A<br />

Switzerland<br />

Plant Sciences , Forestry , Ecology<br />

Question: Lower montane treeline ecotones<br />

such as the inner Alpine dry valleys are regarded<br />

as sensitive to climate change. In the dry Valais<br />

valley (Switzerland) the composition of the<br />

widespread, low altitude Pinus forests is shifting<br />

towards a mixed deciduous state. <strong>The</strong> subboreal<br />

P. sylvestris shows high mortality rates,<br />

whereas the deciduous sub-mediterranean<br />

Quercus pubescens is spreading. <strong>The</strong>se species<br />

may act as early indicators of climate change.<br />

We evaluate this hypothesis by focusing on<br />

their differences in drought tolerance, which<br />

are hardly known, but are likely to be crucial in<br />

the current forest shift and also for future forest<br />

development. Methods: We used dendroecological<br />

methods to detect species-specific patterns<br />

in the growth response to drought. <strong>The</strong> relationship<br />

between radial growth of 401 trees from 15<br />

mixed stands and drought was analysed by calculating<br />

response functions using yearly treering<br />

indices and monthly drought indices. PCA<br />

was applied to the response ratios to discover<br />

spatial patterns of drought response. Results: A<br />

species-specific response to moisture as well as<br />

a sub- regional differentiation of the response<br />

patterns were found. While Quercus showed a<br />

response mainly to the conditions of the previous<br />

autumn and those of current spring, Pinus<br />

did not start responding before May, but showed<br />

responses throughout the whole summer. Quercus<br />

may restrict physiological activity to moist<br />

periods; growth of Pinus was much more dependent<br />

on prior growth. Conclusions: Given that<br />

the climate is changing towards (1) longer summer<br />

drought periods, (2) higher mean temperatures<br />

and (3) shifted seasonality of moisture<br />

availability, Quercus may benefit from adapting<br />

better to drier conditions. Pinus may increasingly<br />

face problems related to drought stress<br />

as it depends on summer moisture and has a<br />

smaller adaptive capacity due to its long-lived<br />

photosynthetic tissue.<br />

Journal of Vegetation Science, 2007, V18, N6, DEC,<br />

pp 777-792.<br />

08.1-189<br />

Landscape-level gene flow in Lobaria pulmonaria,<br />

an epiphytic lichen<br />

Werth S, Gugerli F, Holderegger R, Wagner H H,<br />

Csencsics D, Scheidegger C<br />

Switzerland<br />

Plant Sciences , Forestry , Ecology , Biodiversity ,<br />

Microbiology<br />

Epiphytes are strongly affected by the population<br />

dynamics of their host trees. Owing to the spatiotemporal<br />

dynamics of host tree populations, substantial<br />

dispersal rates - corresponding to high<br />

levels of gene flow - are needed for populations to<br />

persist in a landscape. However, several epiphytic<br />

lichens have been suggested to be dispersal-limited,<br />

which leads to the expectation of low gene flow<br />

at the landscape scale. Here, we study landscapelevel<br />

genetic structure and gene flow of a putatively<br />

dispersal-limited epiphytic lichen, Lobaria pulmonaria.<br />

<strong>The</strong> genetic structure of L. pulmonaria<br />

was quantified at three hierarchical levels, based<br />

on 923 thalli collected from 41 plots situated<br />

within a pasture-woodland landscape and genotyped<br />

at six fungal microsatellite loci. We found<br />

significant isolation by distance, and significant<br />

genetic differentiation both among sampling<br />

plots and among trees. Landscape configuration,<br />

i.e. the effect of a large open area separating two<br />

forested regions, did not leave a traceable pattern<br />

in genetic structure, as assessed with partial Mantel<br />

tests and analysis of molecular variance. Gene<br />

pools were spatially intermingled in the pasturewoodland<br />

landscape, as determined by Bayesian<br />

analysis of population structure. Evidence for local<br />

gene flow was found in a disturbed area that<br />

was mainly colonized from nearby sources. Our<br />

analyses indicated high rates of gene flow of L.<br />

pulmonaria among forest patches, which may reflect<br />

the historical connectedness of the landscape<br />

through gene movement. <strong>The</strong>se results support<br />

the conclusion that dispersal in L. pulmonaria is<br />

rather effective, but not spatially unrestricted.<br />

Molecular Ecology, 2007, V16, N13, JUL, pp<br />

2807-2815.


110<br />

08.1-190<br />

Rhizodeposition of C and N in peas and oats<br />

after C-13-N-15 double labelling under field<br />

conditions<br />

Wichern F, Mayer J, Jörgensen R G, Müller T<br />

Germany, Switzerland<br />

Agriculture, Soil Sciences , Geochemistry & Geophysics<br />

, Plant Sciences<br />

Compounds released by plant roots during growth<br />

can make up a high proportion of below-ground<br />

plant (BGP) carbon and nitrogen, and therefore<br />

influence soil organic matter turnover and plant<br />

nutrient availability by stimulating the soil microorganisms.<br />

<strong>The</strong> present study was conducted<br />

to examine the amount and fate of C (CdfR) and N<br />

rhizodeposits (NdfR), in this study defined as rootderived<br />

C or N present in the soil after removal<br />

of roots and root fragments, released during reproductive<br />

growth. BGP biomass of peas (Pisum<br />

satiumn L.) and oats (Avena sativa L.) was successfully<br />

labelled in situ with a C-13-glucose (15) Nurea<br />

mixture under field conditions using a stem<br />

feeding method. Pea plants were labelled at the<br />

beginning of flowering and harvested 36 and 52<br />

days after labelling at pod filling (Pp) and maturity<br />

(Pm), respectively. Oat plants were labelled<br />

at grain filling and harvested 42 days after labelling<br />

at maturity (O-M). CdfR was 24.2% (Pp), 29.6%<br />

(Pm) and 30.8% (O-M) of total recovered plant C.<br />

NdfR was 32.1% (Pp), 36.4% (Pm) and 30.0% (O-M)<br />

of total plant N. Due to higher N assimilation,<br />

amounts of NdfR were four times higher in peas<br />

in comparison with oats. <strong>The</strong> results for NdfR in<br />

peas were higher than results from other studies.<br />

<strong>The</strong> C- to-N ratio of rhizodeposits was lower under<br />

peas (17.3) than under oats (41.9) at maturity.<br />

At maturity, microbial CdfR at 0 30cm soil depth<br />

was 37% of the microbial biomass C in peas and<br />

59% in oats. Microbial NdfR was 15% of microbial<br />

N in peas and 5% in oats. Furthermore, inorganic<br />

NdfR was 34% in peas and 9% in oats at 0-30cm at<br />

maturity. <strong>The</strong>se results show that rhizodeposits of<br />

peas provide a more easily available substrate to<br />

soil microorganisms, which are incorporated to a<br />

greater extent and turned over faster in comparison<br />

with oats. Beside the higher amounts of N released<br />

from pea roots, this process contributes to<br />

the higher N-availability for subsequent crops.<br />

Soil Biology Biochemistry, 2007, V39, N10, OCT, pp<br />

2527-2537.<br />

08.1-191<br />

Genetic rescue persists beyond first-generation<br />

outbreeding in small populations of a rare<br />

plant<br />

Willi Y, van Kleunen M, Dietrich S, Fischer M<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

Switzerland, Australia, South Africa, Germany<br />

Biodiversity , Plant Sciences , Ecology<br />

Habitat fragmentation commonly causes genetic<br />

problems and reduced fitness when populations<br />

become small. Stocking small populations with<br />

individuals from other populations may enrich<br />

genetic variation and alleviate inbreeding, but<br />

such artificial gene flow is not commonly used<br />

in conservation owing to potential outbreeding<br />

depression. We addressed the role of long-term<br />

population size, genetic distance between populations<br />

and test environment for the performance of<br />

two generations of offspring from between-population<br />

crosses of the locally rare plant Ranunculus<br />

reptans L. Interpopulation outbreeding positively<br />

affected an aggregate measure of fitness, and the<br />

fitness superiority of interpopulation hybrids was<br />

maintained in the second offspring (F2) generation.<br />

Small populations benefited more strongly<br />

from interpopulation outbreeding. Genetic distance<br />

between crossed populations in neutral<br />

markers or quantitative characters was not important.<br />

<strong>The</strong>se results were consistent under<br />

near-natural competition-free and competitive<br />

conditions. We conclude that the benefits of interpopulation<br />

outbreeding are likely to outweigh<br />

potential drawbacks, especially for populations<br />

that suffer from inbreeding.<br />

Proceedings of the Royal Society B Biological Sciences,<br />

2007, V274, N1623, SEP 22, pp 2357-2364.<br />

08.1-192<br />

Vegetation effects on pedogenetic forms of<br />

Fe, Al and Si and on clay minerals in soils in<br />

southern Switzerland and northern Italy<br />

Zanelli R, Egli M, Mirabella A, Giaccai D, Abdelmoula<br />

M<br />

Switzerland, Italy, France<br />

Agriculture, Soil Sciences , Geochemistry & Geophysics<br />

, Ecology<br />

<strong>The</strong> older forest type Quercetum-Bettiletum (oak/<br />

birch; Q-type vegetation) in southern Switzerland<br />

and northern Italy was to a large extent replaced<br />

by chestnut forests (Castanea sativa; C-type vegetation)<br />

in roman times. When laurophylloid vegetation<br />

(L-type vegetation) invaded some of these<br />

chestnut systems during the last few decades, it<br />

caused detectable changes in organic chemistry.<br />

<strong>The</strong> invasion of the L-type vegetation was predominately<br />

due to increased winter temperatures. We<br />

tested whether these vegetation changes led to<br />

measurable long-term and short-term responses<br />

of the mineral matrix by comparing soils under<br />

Q-type with C-type vegetation (probing for longterm<br />

effects; >100-2000 years) and soils under C-<br />

type with L-type vegetation (short-term effects;


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems 111<br />

a few decades). To do so, we examined soil characteristics<br />

including the dithionite-, oxalate- and<br />

pyrophosphate-extractable forms of Fe, Al and<br />

Si as well as the phyllosilicate mineralogy of the<br />

clay fraction with a pair- wise comparison procedure.<br />

On L-type patches, short-term changes<br />

resulted in higher contents of secondary, poorly<br />

crystalline Fe. <strong>The</strong> accumulation of pedogenetic<br />

Fe probably results from a lower availability of<br />

organic complexing moieties under L-type vegetation<br />

and thus leading to a reduced removal. As<br />

soil acidity did not change with the vegetation<br />

types, a strong effect of organic compounds on Fe<br />

and At chemistry must be assumed. A correlation<br />

analysis confirmed that metal binding to organic<br />

matter was different between L-type stands (correlation<br />

of Fe and Al with organic matter was less<br />

significant) and C-type stands. <strong>The</strong> differences in<br />

clay phyllosilicate assemblage between the different<br />

vegetation sites were rather small. <strong>The</strong>re<br />

was, however, a trend towards higher contents of<br />

hydroxy-interlayered vermiculite (HIV) under Ltype<br />

vegetation when compared to C-type sites. It<br />

seems that Al-polymers fixation in interlayers of<br />

2:1 clay minerals was increased or their removal<br />

hindered at sites having L-type vegetation. <strong>Change</strong>s<br />

in the long-term (response to C-type vegetation)<br />

were only measurable for the pyrophosphateextractable<br />

Si content (formation of phytolithe?).<br />

<strong>The</strong> colonisation of laurophyllous species led in<br />

the short-term to significant alterations of the soil<br />

system that were even more pronounced than the<br />

long-term effect of chestnut on soil quality.<br />

Geoderma, 2007, V141, N1-2, SEP 15, pp<br />

119-129.<br />

08.1-193<br />

Importance of dispersal for the expansion of a<br />

Eurasian lynx Lynx lynx population in a fragmented<br />

landscape<br />

Zimmermann F, Breitenmoser Wursten C, Breitenmoser<br />

U<br />

Switzerland<br />

Zoology , Ecology , Biodiversity<br />

Dispersal allows recolonization of previous areas<br />

of habitat following severe depression of a population<br />

but the significance of this is not clear in<br />

felids. <strong>The</strong>re is little evidence to support the general<br />

belief that subadult felids will colonize new<br />

areas, although this is a crucial assumption in reintroduction<br />

or recovery projects. Eurasian lynx<br />

Lynx lynx were reintroduced into the <strong>Swiss</strong> Alps<br />

and have subsequently spread over part of their<br />

potential range but the expansion halted in the<br />

mid 1980s. We postulated that high lynx densities<br />

would lead to an expansion of the population,<br />

and to assess the potential of this population to<br />

expand we compared the dispersal characteristics<br />

of 22 subadults from the northwest <strong>Swiss</strong> Alps,<br />

where an increase in lynx abundance occurred<br />

from 1995 onwards, to 17 individuals from the<br />

Jura Mountains, an area with a lower lynx density.<br />

Dispersal data came mainly from radio-telemetry.<br />

Dispersal rates and distances for subadults that<br />

completed dispersal were lower in the north-west<br />

<strong>Swiss</strong> Alps than in the Jura Mountains. In general,<br />

subadults exhibited little ability to cross major<br />

barriers such as highways. <strong>The</strong> hypothesis that<br />

high density alone will foster the expansion of<br />

the population was therefore not confirmed. This<br />

has consequences for the reintroduction and recovery<br />

of carnivores in fragmented landscapes. To<br />

establish only one strong source population may<br />

not be an optimal strategy, and population nuclei<br />

should therefore be founded in several neighbouring<br />

patches.<br />

Oryx, 2007, V41, N3, JUL, pp 358-368.<br />

08.1-194<br />

Remote sensing-based predictors improve<br />

distribution models of rare, early successional<br />

and broadleaf tree species in Utah<br />

Zimmermann N E, Edwards T C, Moisen G G,<br />

Frescino T S, Blackard J A<br />

Switzerland, USA<br />

Ecology , Remote Sensing , Modelling , Plant Sciences<br />

, Forestry<br />

1. Compared to bioclimatic variables, remote<br />

sensing predictors are rarely used for predictive<br />

species modelling. When used, the predictors represent<br />

typically habitat classifications or filters<br />

rather than gradual spectral, surface or biophysical<br />

properties. Consequently, the full potential<br />

of remotely sensed predictors for modelling the<br />

spatial distribution of species remains unexplored.<br />

Here we analysed the partial contributions<br />

of remotely sensed and climatic predictor<br />

sets to explain and predict the distribution of 19<br />

tree species in Utah. We also tested how these partial<br />

contributions were related to characteristics<br />

such as successional types or species traits. 2. We<br />

developed two spatial predictor sets of remotely<br />

sensed and topo-climatic variables to explain the<br />

distribution of tree species. We used variation partitioning<br />

techniques applied to generalized linear<br />

models to explore the combined and partial<br />

predictive powers of the two predictor sets. Nonparametric<br />

tests were used to explore the relationships<br />

between the partial model contributions of<br />

both predictor sets and species characteristics. 3.<br />

More than 60% of the variation explained by the<br />

models represented contributions by one of the


112<br />

two partial predictor sets alone, with topo-climatic<br />

variables outperforming the remotely sensed<br />

predictors. However, the partial models derived<br />

from only remotely sensed predictors still provided<br />

high model accuracies, indicating a significant<br />

correlation between climate and remote sensing<br />

variables. <strong>The</strong> overall accuracy of the models was<br />

high, but small sample sizes had a strong effect<br />

on cross-validated accuracies for rare species. 4.<br />

Models of early successional and broadleaf species<br />

benefited significantly more from adding remotely<br />

sensed predictors than did late seral and<br />

needleleaf species. <strong>The</strong> core-satellite species types<br />

differed significantly with respect to overall model<br />

accuracies. Models of satellite and urban species,<br />

both with low prevalence, benefited more from<br />

use of remotely sensed predictors than did the<br />

more frequent core species. 5. Synthesis and applications.<br />

If carefully prepared, remotely sensed<br />

variables are useful additional predictors for the<br />

spatial distribution of trees. Major improvements<br />

resulted for deciduous, early successional, satellite<br />

and rare species. <strong>The</strong> ability to improve model<br />

accuracy for species having markedly different<br />

life history strategies is a crucial step for assessing<br />

effects of global change.<br />

Journal of Applied Ecology, 2007, V44, N5, OCT, pp<br />

1057-1067.<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Terrestrial Ecosystems<br />

08.1-195<br />

Stomatal regulation by microclimate and tree<br />

water relations: interpreting ecophysiological<br />

field data with a hydraulic plant model<br />

Zweifel R, Steppe K, Sterck F J<br />

Switzerland, Belgium, Netherlands<br />

Meteorology & Atmospheric Sciences , Plant Sciences<br />

, Forestry , Modelling<br />

Dynamics in microclimate and physiological<br />

plant traits were studied for Pubescent oak and<br />

Scots pine in a dry inner-alpine valley in Switzerland,<br />

at a 10 min resolution for three consecutive<br />

years (2001-2003). As expected, stomata tended<br />

to close with increasing drought in air and soil.<br />

However, stomatal aperture in oak was smaller<br />

than in pine under relatively wet conditions, but<br />

larger under dry conditions. To explore underlying<br />

mechanisms, a model was applied that (i)<br />

quantifies water relations within trees from physical<br />

principles (mechanistic part) and (ii) assumes<br />

that signals from light, stomatal aperture, crown<br />

water potential, and tree water deficit in storage<br />

pools control stomata (systemic part). <strong>The</strong> stomata<br />

of pine showed a more sensitive response to increasing<br />

drought because both factors, the slowly<br />

changing tree water deficit and the rapidly changing<br />

crown water potential, closed the stomata. By<br />

contrast, the stomata of oak became less droughtsensitive<br />

as the closing signal of crown water potential<br />

was opposed by the opening signal of tree<br />

water deficit. Moreover, parameter optimization<br />

suggests that oak withdrew more water from the<br />

storage pools and reduced leaf water potentials<br />

to lower levels, without risking serious damage<br />

by cavitation. <strong>The</strong> new model thus suggests how<br />

the hydraulic water flow and storage system determines<br />

the responses in stomatal aperture and<br />

transpiration to drought at time scales ranging<br />

from hours to multiple years, and why pine and<br />

oak might differ in such responses. <strong>The</strong>se differences<br />

explain why oaks are more efficient competitors<br />

during drought periods, although this<br />

was not the case in the extremely dry year 2003,<br />

which provoked massive leaf loss and, from July<br />

onwards, physiological activity almost ceased.<br />

Journal of Experimental Botany, 2007, V58, N8, pp<br />

2113-2131.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Soil and Lithosphere 113<br />

1.3 Soil and Lithosphere<br />

08.1-196<br />

Quantification of soil erosion rates related to<br />

ancient Maya deforestation<br />

Anselmetti F S, Hodell D A, Ariztegui D, Brenner M,<br />

Rosenmeier M F<br />

Switzerland, USA<br />

Geomorphology , Agriculture, Soil Sciences , Paleontology<br />

, Geology<br />

We used seismic and sediment core data to quantify<br />

soil erosion rates for the past similar to 6000<br />

yr in the closed catchment of Lake Salpeten, in the<br />

tropical lowlands of northern Guatemala. <strong>The</strong> region<br />

was affected by ancient Maya land use from<br />

before ca. 1000 B.C. to A.D. 900. This period of<br />

human impact coincided with deposition in the<br />

lake of a detrital unit (Maya Clay) as much as 7<br />

m thick that contrasts sharply with the relatively<br />

organic-rich gyttja deposited both before and after<br />

Maya occupation of the watershed. <strong>The</strong> greatest<br />

soil loss, with mean sustained values of similar<br />

to 1000 t/km(2)yr (-1), occurred in the Middle<br />

and Late Preclassic Periods (700 B.C. to A.D. 250),<br />

associated with relatively low Maya population<br />

densities. Soil erosion slowed during the period<br />

of maximum population density in the Late Classic<br />

Period (A.D. 550-830), indicating a decoupling<br />

between human population density and soil erosion<br />

rate. <strong>The</strong> most rapid soil loss occurred early<br />

during initial land clearance, suggesting that<br />

even low numbers of people can have profound<br />

impacts on lowland tropical karst landscapes.<br />

Geology, 2007, V35, N10, OCT, pp 915-918.<br />

08.1-197<br />

Soil biogeochemical processes within the Critical<br />

Zone<br />

Chorover J, Kretzschmar R, Garcia Pichel F, Sparks<br />

D L<br />

USA, Switzerland<br />

Agriculture, Soil Sciences , Toxicology , Geochemistry<br />

& Geophysics<br />

Many processes that affect soil and water quality<br />

occur at the water wetted interface of weathering<br />

products such as clays, oxides, and organic matter.<br />

Especially near the sunlit surface of the Critical<br />

Zone, these interfaces associate with plant<br />

roots and soil organism to form porous, aggregated<br />

structures. Soil aggregates and intervening<br />

pore networks give rise to a patchwork of interconnected<br />

microenvironments. <strong>The</strong> ensuing steep<br />

geochemical gradients affect weathering processes,<br />

fuel the activities of microbes, and drive interfacial<br />

reactions that retain and transform rock- or<br />

ecosystem- derived chemicals and anthropogenic<br />

pollutants.<br />

Elements, 2007, V3, N5, OCT, pp 321-326.<br />

08.1-198<br />

Scale-dependent relationships between soil<br />

organic carbon and urease activity<br />

Corstanje R, Schulin R, Lark R M<br />

England, Switzerland<br />

Modelling , Agriculture, Soil Sciences<br />

Many soil properties and processes vary at different<br />

spatial scales. As a result, relationships between<br />

soil properties often depend on scale. In this<br />

paper we show this for two soil properties of biological<br />

importance, by means of a nested analysis<br />

of covariance. <strong>The</strong> variables were urease activity<br />

(UA) and soil organic carbon (SOC) , sampled on an<br />

unbalanced nested design at three sites with different<br />

land uses (arable, forest and pasture). <strong>The</strong><br />

objective of this study was to investigate the scaledependent<br />

relationships of UA and SOC at these<br />

three sites to exemplify the phenomenon of scale-<br />

dependency in the covariation of biogeochemical<br />

variables. At each site the variables showed different<br />

scale dependencies, expressed in their correlations<br />

at different scales. At the pasture site,<br />

UA and SOC were uncorrelated at all scales in the<br />

sampling design (0.2 m, 1 m, 6 m and >= 15 m),<br />

and the overall product moment correlation was<br />

0.10. A significant positive scale dependent correlation<br />

(0.65) was found at the 1-m scale for the<br />

forested site. <strong>The</strong> soil properties were not spatially<br />

correlated at any of the other scales and the associated<br />

product moment correlation for this site<br />

was 0.14. Urease activity and soil organic C were<br />

found not to be correlated at the shorter scales in<br />

the arable site. However, significant positive correlation<br />

coefficients of 0.89 and 0.82 were obtained<br />

at the longer scales of 6 and >= 15-m respectively<br />

for the arable site. <strong>The</strong> product moment correlation<br />

at this site was 0.65. At both the arable and<br />

forest site, we found that correlations at particular<br />

scales were stronger than the overall product<br />

moment correlation. This approach allowed us to<br />

identify significant relationships between urease<br />

activity and soil organic carbon and the scales at<br />

which these relationships occur and to draw conclusions<br />

about the spatial scales, which must be<br />

resolved in further studies of these variables in<br />

these contrasting environments. This study highlights<br />

the pervasive effect of scale in soil biogeochemistry<br />

and shows that scale-dependence must<br />

not be disregarded by soil scientists in their investigations<br />

of biogeochemical processes.<br />

European Journal of Soil Science, 2007, V58, N5,<br />

OCT, pp 1087-1095.


114<br />

08.1-199<br />

Effect of climate and vegetation on soil<br />

organic carbon, humus fractions, allophanes,<br />

imogolite, kaolinite, and oxyhydroxides in<br />

volcanic soils of Etna (Sicily)<br />

Egli M, Alioth L, Mirabella A, Raimondi S, Nater M,<br />

Verel R<br />

Switzerland, Italy<br />

Agriculture, Soil Sciences , Geology , Geochemistry<br />

& Geophysics<br />

A soil sequence along an elevational gradient ranging<br />

from to subalpine climate zones in the Etna region<br />

(Sicily, southern Italy) investigated with respect<br />

to organic C, kaolinite, and crystalline noncrystalline<br />

Al and Fe phases. Special emphasis was given<br />

to stabilization of soil organic carbon (SOC) and its<br />

interaction with inorganic phases. <strong>The</strong> soils were<br />

variations of Vitric Andosols developed on a trachybasaltic<br />

lava flow with an age of 15,000 years. main<br />

vegetation systems dominated the sites: at the lower<br />

sites, it mainly maquis vegetation and, at the higher<br />

elevated sites, predominantly coniferous forest. <strong>The</strong><br />

concentration of SOC in the topsoil, SOC stocks in<br />

the profiles, the humus fractions such as humic<br />

and acids, functional groups and substances of organic<br />

matter, type materials (ITM), and oxyhydroxides<br />

were found to be related to elevation and, thus,<br />

climate (precipitation and temperature) and vegetation.<br />

<strong>The</strong> C/N ratio in the topsoil was especially<br />

indicative the vegetation type. <strong>The</strong> amount of SOC,<br />

ITM, and crystalline oxyhydroxides decreased with<br />

increasing altitude. Weathering, as to the proportion<br />

of crystalline Fe-oxyhydroxides or the kaolinite<br />

centration in the clay fraction, seemed to be greater<br />

at the lower sites. At these sites, maquis vegetation<br />

led to a higher accumulation SOC as compared with<br />

the coniferous trees at the higher sites. activity, as<br />

indicated by aromatic compounds in the humic<br />

acids and the presence of charcoal in the soil, has<br />

most probably influenced important soil processes.<br />

<strong>The</strong> identification and radiocarbon dating charcoal<br />

revealed evidence that repeated bush fires had<br />

played a significant role in soil formation. <strong>The</strong> better<br />

stabilization of SOC at altitudes might be due to<br />

the specific climatic conditions with a pronounced<br />

change in periods of humidity alternating with periods<br />

droughts and resultant fire activity. <strong>The</strong> positive<br />

correlation mean annual temperature and SOC<br />

content supports such a hypothesis. <strong>The</strong> climate-<br />

and vegetation-dependent stabilization of organic<br />

matter the soil can be ascribed to the proportion<br />

of aromatics in the humic acids, to the presence<br />

of noncrystalline Al and Fe phases, to the kaolinite<br />

concentration, to the amount of clay, and to a lesser<br />

extent to the fraction.<br />

Soil Science, 2007, V172, N9, SEP, pp 673-691.<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Soil and Lithosphere<br />

08.1-200<br />

Soil moisture - Atmosphere interactions during<br />

the 2003 European summer heat wave<br />

Fischer E M, Seneviratne S I, Vidale P L, Lüthi D,<br />

Schär C<br />

Switzerland, England<br />

Modelling , Meteorology & Atmospheric Sciences ,<br />

Agriculture, Soil Sciences<br />

<strong>The</strong> role of land surface-related processes and feedbacks<br />

during the record-breaking 2003 European<br />

summer heat wave is explored with a regional climate<br />

model. All simulations are driven by lateral<br />

boundary conditions and sea surface temperatures<br />

from the ECMWF operational analysis and 40-yr<br />

ECMWF Re-Analysis (ERA-40), thereby prescribing<br />

the large-scale circulation. In particular, the<br />

contribution of soil moisture anomalies and their<br />

interactions with the atmosphere through latent<br />

and sensible heat fluxes is investigated. Sensitivity<br />

experiments are performed by perturbing spring<br />

soil moisture in order to determine its influence<br />

on the formation of the heat wave. A multiyear<br />

regional climate simulation for 1970-2000 using a<br />

fixed model setup is used as the reference period.<br />

A large precipitation deficit together with early<br />

vegetation green-up and strong positive radiative<br />

anomalies in the months preceding the extreme<br />

summer event contributed to an early and rapid<br />

loss of soil moisture, which exceeded the multiyear<br />

average by far. <strong>The</strong> exceptionally high temperature<br />

anomalies, most pronounced in June and August<br />

2003, were initiated by persistent anticyclonic circulation<br />

anomalies that enabled a dominance of<br />

the local heat balance. In this experiment the hottest<br />

phase in early August is realistically simulated<br />

despite the absence of an anomaly in total surface<br />

net radiation. This indicates an important role<br />

of the partitioning of net radiation in latent and<br />

sensible heat fluxes, which is to a large extent controlled<br />

by soil moisture. <strong>The</strong> lack of soil moisture<br />

strongly reduced latent cooling and thereby amplified<br />

the surface temperature anomalies. <strong>The</strong> evaluation<br />

of the experiments with perturbed spring<br />

soil moisture shows that this quantity is an important<br />

parameter for the evolution of European heat<br />

waves. Simulations indicate that without soil moisture<br />

anomalies the summer heat anomalies could<br />

have been reduced by around 40% in some regions.<br />

Moreover, drought conditions are revealed to influence<br />

the tropospheric circulation by producing<br />

a surface heat low and enhanced ridging in the<br />

midtroposphere. This suggests a positive feedback<br />

mechanism between soil moisture, continentalscale<br />

circulation, and temperature.<br />

Journal of Climate, 2007, V20, N20, OCT 15, pp<br />

5081-5099.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Soil and Lithosphere 115<br />

08.1-201<br />

Numerical modelling of the hydrogeological<br />

and geomechanical behaviour of a large slope<br />

movement: the Triesenberg landslide (Liechtenstein)<br />

Francois B, Tacher L, Bonnard Ch, Laloui L,<br />

Triguero V<br />

Switzerland<br />

Modelling , Geomorphology , Geology<br />

Using advanced hydrogeological and geomechanical<br />

finite element modelling, it has been possible<br />

to model the mechanical behaviour of a large<br />

slope movement, the Triesenberg landslide. This<br />

slope is located along the Rhine valley in the<br />

Principality of Liechtenstein and covers an area<br />

of around 5 km(2), which includes two villages.<br />

Pore-water pressure fields calculated by the hydrogeological<br />

model were used as input for the geomechanical<br />

model. <strong>The</strong> results obtained through<br />

numerical simulation agree fairly well with field<br />

measurements of peak velocity, spatial and temporal<br />

distribution of velocity, and total displacements.<br />

Such results were obtained using a modified<br />

Cam-Clay elastoplastic constitutive model for<br />

which the required material parameters were obtained<br />

through careful geotechnical tests. <strong>The</strong>se<br />

finite element models were carried out in two and<br />

three dimensions to gradually improve the understanding<br />

of the physical phenomena governing<br />

the hydrogeological conditions and the movements<br />

of the slope.<br />

Canadian Geotechnical Journal, 2007, V44, N7,<br />

JUL, pp 840-857.<br />

08.1-202<br />

Formation of hydrozincite, Zn layered double<br />

hydroxide and Zn phyllosilicates in contaminated<br />

calcareous soils<br />

Jacquat O, Vögelin A, Kretzschmar R<br />

Switzerland<br />

Agriculture, Soil Sciences , Geochemistry &<br />

Geophysics , Toxicology<br />

Geochimica et Cosmochimica Acta, 2007, V71, N15,<br />

AUG, SS, p A437.<br />

08.1-203<br />

<strong>The</strong> impact of Fe isotope fractionation by<br />

plants on the isotopic signature of soils<br />

Kiczka M, Wiederhold J G, Krämer S M, Bourdon B,<br />

Kretzschmar R<br />

Switzerland, Austria<br />

Plant Sciences , Agriculture, Soil Sciences , Geochemistry<br />

& Geophysics<br />

Geochimica et Cosmochimica Acta, 2007, V71, N15,<br />

AUG, SS, p A482.<br />

08.1-204<br />

Sulphur behaviour in forest soils near the largest<br />

SO 2 emitter in northern Europe<br />

Koptsik G, Alewell C<br />

Russia, Switzerland<br />

Forestry , Agriculture, Soil Sciences , Geochemistry<br />

& Geophysics , Toxicology , Ecology<br />

<strong>The</strong> impact of 60 a of SO 2 emissions from a Ni-<br />

Cu plant in the Kola Peninsula (Russia) on soil S<br />

contents was assessed in podzols under pine forests.<br />

Sulphate desorption and the possible delay<br />

of acidification reversal was investigated, because<br />

the plant will be reconstructed in 2006 with an<br />

expected emission reduction of 90%. Sites were<br />

sampled along a pollution gradient in the prevailing<br />

wind direction from 1 to 66 km. <strong>The</strong> investigated<br />

podzols stored S mostly in the organic<br />

form. <strong>The</strong> concentrations of total and organic S<br />

in soil organic horizons tended to be higher near<br />

the smelter but were only weakly correlated with<br />

S deposition. No relationship between distance to<br />

smelter and S contents was found for the mineral<br />

horizons. Sulphate content and desorption behavior<br />

were highly variable due to natural variations<br />

of texture and extractable Al and Fe contents of<br />

the soils. <strong>The</strong> lack of a clear strong trend with distance<br />

from the smelter except in the organic layer<br />

indicated that long range transport and diffuse<br />

input of SO 4 played a major role rather than point<br />

source impact. It was concluded that biological<br />

turnover is most likely the regulating process in<br />

these soils and thus low to medium release of SO 4<br />

is expected under decreasing deposition scenarios<br />

because organic S was the dominant fraction of<br />

total S in all soils.<br />

Applied Geochemistry, 2007, V22, N6, JUN, pp<br />

1095-1104.<br />

08.1-205<br />

Evidence for in situ degradation of mono-and<br />

polyaromatic hydrocarbons in alluvial sediments<br />

based on microcosm experiments with<br />

C-13-labeled contaminants<br />

Morasch B, Höhener P, Hunkeler D<br />

Switzerland, France<br />

Microbiology , Geochemistry & Geophysics , Geology<br />

A microcosm study was conducted to investigate<br />

the degradation of mono- and polyaromatic hydrocarbons<br />

under in situ-like conditions using<br />

alluvial sediments from the site of a former cokery.<br />

Benzene, naphthalene, or acenaphthene were<br />

added to the sediments as C-13- labeled substrates.<br />

Based on the evolution of C-13-CO 2 determined by<br />

gas chromatography isotope-ratio mass spectrometry<br />

(GC-IRMS) it was possible to prove mineraliza-


116<br />

tion of the compound of interest in the presence<br />

of other unknown organic substances of the sediment<br />

material. This new approach was suitable to<br />

give evidence for the intrinsic biodegradation of<br />

benzene, naphthalene, and acenaphthene under<br />

oxic and also under anoxic conditions, due to the<br />

high sensitivity and reproducibility of C-13/C-12<br />

stable isotope analysis. This semi-quantitative<br />

method can be used to screen for biodegradation<br />

of any slowly degrading, strongly sorbing compound<br />

in long-term experiments.<br />

Environmental Pollution, 2007, V148, N3, AUG, pp<br />

739-748.<br />

08.1-206<br />

Acidification and recovery of soil at a heavily<br />

impacted forest catchment (Lysina, Czech<br />

Republic) - SAFE modeling and field results<br />

Navratil T, Kurz D, Kram P, Hofmeister J, Hruska J<br />

Czech Republic, Switzerland<br />

Agriculture, Soil Sciences , Geochemistry & Geophysics<br />

, Modelling , Forestry , Plant Sciences<br />

Soil and soil solution chemistry were simulated<br />

using the dynamic multi-layer soil chemistry<br />

model SAFE for the Lysina catchment, located<br />

in the western part of the Czech Republic. Modeled<br />

soil solution chemistry and properties were<br />

compared to a 10-year-long time series of monthly<br />

measurements of soil solution data at 5,15, 20<br />

and 80 cm depths. Historically high deposition of<br />

S and N compounds caused a significant decrease<br />

in soil base saturation and caused severe changes<br />

in the soil solution chemistry. Since year 1990<br />

deposition of S and N compounds decreased substantially<br />

due to improved control on S emissions.<br />

SAFE predicted an increase in base saturation at<br />

Lysina in the Oi + Oe and Oa layers, from 36% and<br />

18% in 1994 to 50% and 22% in 2004, respectively.<br />

on the other hand, base saturation of the deeper<br />

soil horizons B and C, which represent the main<br />

mass of the soil at the Lysina catchment, has decreased<br />

even further (in B horizon from 4% in 1994<br />

to 3% in 2004 and from 4% to 2% in horizon C).<br />

<strong>The</strong> measured values of base saturation from year<br />

2004 fit the modeled results of base saturation<br />

development at the Lysina catchment. if atmospheric<br />

deposition remains at the 2006 level, the<br />

predicted base saturation in the B and C horizons<br />

for the year 2100 will increase by approximately<br />

2%, to reach only 4.6% and 3.8%, respectively. <strong>The</strong><br />

increasing molar ratio Bc/Al ((Ca + Mg + K)/All in<br />

soil solution of Oi + Oe, Oa and E horizons during<br />

the first half of the 21st century represents recovery<br />

in the top 20 cm of the soil profile, only This<br />

change may have a positive effect on the health<br />

status of shallow rooting spruce trees. <strong>The</strong> Bc/Al<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Soil and Lithosphere<br />

ratio in soil solutions in the main mass of the soil<br />

(horizons B and C), however, will remain below<br />

the critical value (


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Soil and Lithosphere 117<br />

08.1-208<br />

Bioavailability of pollutants and soil remediation<br />

Ortega Calvo J J, Ball W P, Schulin R, Semple K T,<br />

Wick L Y<br />

Spain, USA, Switzerland, England, Germany<br />

Agriculture, Soil Sciences , Toxicology<br />

Journal of Environmental Quality, 2007, V36, N5,<br />

SEP-OCT, pp 1383-1384.<br />

08.1-209<br />

New method for in situ characterization of<br />

loose material for landslide mapping purpose<br />

Pantet A, Parriaux A, <strong>The</strong>lin P<br />

Switzerland<br />

Geomorphology , Geology , Instruments & Instrumentation<br />

<strong>The</strong> assessment of grain size distribution and<br />

plasticity of loose geological material, during in<br />

situ geological investigations, is not obvious. Visual<br />

appreciation allows an approximative quantification<br />

of the coarse granulometric fractions,<br />

but not of the fine ones. Field soils determination<br />

methods suggested until now, are visual and tactile<br />

tests leading to a very rough estimate, which<br />

is only qualitative and not very reproducible. <strong>The</strong><br />

new proposed field test (GEOLEP method) allows a<br />

quick quantification of the fine fraction of loose<br />

material. It allows the determination of the sand<br />

fraction (fine and medium grained sands) as well<br />

as the methylene blue value of the samples. <strong>The</strong><br />

necessary equipment to perform this test is light<br />

and compact and the time needed to analyze one<br />

sample is approximately 15 min. Thus it is also<br />

possible to carry out numerous measurements in<br />

one day. <strong>The</strong> calibrations were carried out on a selection<br />

of 13 natural samples, chosen for their representativeness<br />

of the typical alpine quaternary<br />

deposits. <strong>The</strong> results obtained with GEOLEP method<br />

are relevant compared with standardized laboratory<br />

tests; the obtained correlation indexes are<br />

of 73% for the comparison with laboratory stain<br />

test results and of 89% with a laboratory method<br />

using a similar procedure than the field test. <strong>The</strong><br />

correlation we performed with Atterberg’s limits<br />

tests shows that a rough approximation of plasticity<br />

index can also be obtained (R-2 = 75%). This<br />

method thus brings a new tool which should allow<br />

taking into account the lithological factor (by<br />

some quantitative and representative variables) in<br />

a reliable way for the evaluation of landslide hazards.<br />

(C) 2007 Elsevier B.V. All rights reserved.<br />

Engineering Geology, 2007, V94, N3-4, NOV 2, pp<br />

166-179.<br />

08.1-210<br />

Poplar for the phytomanagement of boron<br />

contaminated sites<br />

Robinson B H, Green S R, Chancerel B, Mills T M,<br />

Clothier B E<br />

Switzerland, New Zealand<br />

Toxicology , Agriculture, Soil Sciences , Plant Sciences<br />

Boron (B) is a widespread environmental contaminant<br />

that is mobile relative to other trace<br />

elements. We investigated the potential of hybrid<br />

poplar (Populus sp.) for B phytomanagement using<br />

a lysimeter experiment and a field trial on<br />

B-contaminated wood-waste. In both studies, poplars<br />

enhanced evapotranspiration from the woodwaste,<br />

reduced B leaching, and accumulated Bin<br />

the aerial portions of the tree. When grown in<br />

a substrate containing 30 mg/kg B, poplar leaves<br />

had an average B concentration of 845 mg/kg,<br />

while the stems contained 21 mg/kg B. Leaf B<br />

concentrations increased linearly with leaf age. A<br />

decomposition experiment revealed that abscised<br />

leaves released 14% of their B during the winter<br />

months. Fertiliser application enhanced tree<br />

growth without decreasing the leaf B concentrations.<br />

Harvesting alternate rows of trees on a contaminated<br />

site would reduce leaching from the<br />

site while removing B. Harvested plant material<br />

may provide bioenergy, stock fodder, or an amendment<br />

for B-deficient soils.<br />

Environmental Pollution, 2007, V150, N2, NOV, pp<br />

225-233.<br />

08.1-211<br />

<strong>Change</strong>s in the macro-pore structure of<br />

restored soil caused by compaction beneath<br />

heavy agricultural machinery: a morphometric<br />

study<br />

Schäffer B, Stauber M, Müller R, Schulin R<br />

Switzerland<br />

Agriculture, Soil Sciences<br />

Compaction can seriously degrade soil in modern<br />

agriculture. Soil that has been temporarily removed<br />

and stored is particularly sensitive to compaction<br />

when restored, although little is known<br />

about the structural changes in such soils under<br />

mechanical loads. We investigated the structural<br />

changes in a restored soil that had been gently cultivated<br />

for several years and then was trafficked<br />

by a heavy combine harvester, analysing the macro-pore<br />

structure by quantitative morphometry of<br />

three-dimensional microcomputed tomography<br />

images. Increased trafficking caused decreases in<br />

both the porosity and connectivity of the macropores.<br />

<strong>The</strong> fraction of spherical pores (and thus the<br />

convexity of the pore space) and the mean pore


118<br />

separation were increased. Trafficking had no<br />

clear effect on the orientation of pores. While the<br />

mean pore diameter tended to decrease, biopores<br />

were more stable than interaggregate pores originating<br />

from the packing of soil aggregates. This<br />

is relevant for the development of structural stability<br />

in restored soils, as the macro-pores consist<br />

mainly of interaggregate pores initially, whereas<br />

biopores develop and increase in proportion only<br />

gradually over time. Quantitative morphometry<br />

provides valuable morphological indices for the<br />

objective assessment of the macro-pore structure<br />

and changes induced by compaction.<br />

European Journal of Soil Science, 2007, V58, N5,<br />

OCT, pp 1062-1073.<br />

08.1-212<br />

Reducing phosphorus losses from over-fertilized<br />

grassland soils proves difficult in the<br />

short term<br />

Schärer M, Stamm C, Vollmer T, Frossard E, Oberson<br />

A, Flühler H, Sinaj S<br />

Switzerland<br />

Water Resources , Agriculture, Soil Sciences , Toxicology<br />

, Hydrology<br />

Phosphorus (P) losses from many agricultural<br />

soils are driven by fast transport processes, such<br />

as surface runoff, shallow interflow and macropore<br />

flow. Close interaction of rain with topsoil layers<br />

(0-5 cm), rich in available P, results in high P<br />

concentrations in these rapid runoff pathways.<br />

This is particularly pronounced in permanent<br />

grassland soils typically characterized by a P enrichment<br />

of the topsoil. One option to mitigate P<br />

losses from grassland is therefore to reduce soil<br />

P content, particularly available P, in this critical<br />

surface layer. Omitting application of P fertilizer<br />

will reduce soil P in the long term but more drastic<br />

methods may be necessary to achieve P loss<br />

reductions in shorter time-scales. In this study,<br />

three management options to reduce P in runoff<br />

from grassland soils were evaluated in a field experiment<br />

lasting 2 years on two grassland sites: (i)<br />

no P inputs, (ii) no P inputs plus soil tillage and<br />

(iii) no P inputs plus tillage combined with application<br />

of a P sorbing soil amendment (iron oxide).<br />

Withholding P inputs did not decrease either the<br />

available P in the soil or the P concentrations in<br />

runoff from sprinkler experiments over a 2-year<br />

period. Both the treatments which included tillage<br />

caused immediate reductions in both soil<br />

available P and runoff P, with Fe/OH amendment<br />

being more effective. However, in the second year<br />

the effects of both tillage treatments were less apparent<br />

and only the Fe/OH treatment significantly<br />

decreased runoff P. <strong>The</strong> results indicate that the<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Soil and Lithosphere<br />

long-term enrichment of soils due to P application<br />

in excess of plant needs is unlikely to be remedied<br />

by short-term treatments. However, further<br />

work is required to assess the applicability of our<br />

conclusion to other sites.<br />

Soil Use and Management, 2007, V23, SEP, S1, pp<br />

154-164.<br />

08.1-213<br />

Heavy metal contamination along a soil<br />

transect in the vicinity of the iron smelter of<br />

Kremikovtzi (Bulgaria)<br />

Schulin R, Curchod F, Mondeshka M, Daskalova A,<br />

Keller A<br />

Switzerland, Bulgaria<br />

Agriculture, Soil Sciences , Toxicology , Geochemistry<br />

& Geophysics<br />

Based on previous preliminary survey results,<br />

elevated heavy metal concentrations of the agricultural<br />

soils of the villages of the Kremikovtzi<br />

region east of the Bulgarian capital Sofia were<br />

attributed to pollution from dusts emitted by<br />

the iron smelter in the centre of the region. Additional<br />

sampling in a test area indicated that<br />

high metal concentrations in this area could also<br />

be of geogenic origin. In order to test this hypothesis,<br />

we sampled a sequence of 14 soil profiles at<br />

increasing distance from the smelter along a 2<br />

km transect through agricultural land outside<br />

the metallurgical complex of Kremikovtzi. <strong>The</strong><br />

transect extended through two different units of<br />

soil types: Chromic Luvisols and Alluvial Fluvisols.<br />

Samples of the fine earth fraction (


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Soil and Lithosphere 119<br />

important it can be in identifying the origin of<br />

soil pollution not only to look into areal distribution<br />

patterns of suspected contaminants, but also<br />

to investigate their depth profiles as well as that<br />

of other elements and to account for pedological<br />

factors and their variability.<br />

Geoderma, 2007, V140, N1-2, JUN 15, pp 52-61.<br />

08.1-214<br />

Slip rates variability and sediment mobilization<br />

on a shallow landslide in the northern<br />

<strong>Swiss</strong> Alps<br />

Schwab M, Läderach C, Rieke Zapp D,<br />

Schlunegger F<br />

Switzerland<br />

Geology , Geomorphology<br />

Geomorphic and morphometric data imply that<br />

process rates of the Schimbrig landslide, located<br />

in the Entle watershed (Central Switzerland), are<br />

still limited by the elevation of the LGM base level.<br />

At present, the Entle watershed is in a stage of adjusting<br />

to the lowered post-glacial base level as indicated<br />

by knick zones in the trunk stream. Some<br />

thousands of years later when these knick zones<br />

will reach the Schimbrig site, we anticipate a substantial<br />

increase in process rates and sediment<br />

flux for the landslide. <strong>The</strong> pattern of slip rates<br />

was measured on the Schimbrig landslide over<br />

a 14-months period. We propose that a Bingham<br />

plastic model explains much of how measured<br />

slip rates are linked to the observed topography,<br />

climatic variations and thickness variability of<br />

the landslide mass. This model explains why slip<br />

rates have been highest where the thickness of the<br />

material is substantially higher. It also explains<br />

why slip rates are highest in late summer/autumn<br />

and early spring. It appears then that snow melt<br />

in spring and decreasing temperatures in late<br />

summer/autumn potentially result in a high retention<br />

of the pore water and thus in a low viscosity<br />

of the material, which, in turns, promotes<br />

slip rates. Interestingly, an extreme rainstorm like<br />

the one of August 2005 only had a local impact<br />

on the landslide mass by triggering small scale<br />

earth flows and debris flows. This implies that the<br />

earth slide material does not directly respond to<br />

an episodic pattern of rainfall. Such precipitation<br />

events, however, superimpose a smaller-scale imprint<br />

on the landslide relief.<br />

<strong>Swiss</strong> Journal of Geosciences, 2007, V100, N2, SEP,<br />

pp 281-292.<br />

08.1-215<br />

Dry-end surface soil moisture variability during<br />

NAFE’06<br />

Teuling A J, Uijlenhoet R, Hurkmans R, Merlin O,<br />

Panciera R, Walker J P, Troch P A<br />

Switzerland, Netherlands, Australia, USA<br />

Hydrology , Agriculture, Soil Sciences<br />

Characterization of the space-time variability of<br />

soil moisture is important for land surface and<br />

climate studies. Here we develop an analytical<br />

model to investigate how, at the dry-end of the<br />

soil moisture range, the main characteristics of<br />

the soil moisture field (spatial mean and variability,<br />

steady state distribution) depend on the intermittent<br />

character of low intensity rain storms.<br />

Our model is in good agreement with data from<br />

the recent National Airborne Field Experiment<br />

(NAFE’06) held in the semiarid Australian Murrumbidgee<br />

catchment. We find a positive linear<br />

relationship between mean soil moisture and its<br />

associated variability, and a strong dependency<br />

of the temporal soil moisture distribution to the<br />

amount and structure of precipitation.<br />

Geophysical Research Letters, 2007, V34, N17, SEP<br />

13 ARTN: L17402.<br />

08.1-216<br />

Dynamics of soil organic matter turnover and<br />

soil respired CO 2 in a temperate grassland<br />

labelled with C-13<br />

<strong>The</strong>is D E, Jäggi M, Aeschlimann D, Blum H,<br />

Frossard E, Siegwolf R T W<br />

Switzerland<br />

Plant Sciences , Ecology , Agriculture, Soil Sciences<br />

, Geochemistry & Geophysics<br />

<strong>The</strong> fate of carbon (C) in grassland soils is of particular<br />

interest since the vast majority in grassland<br />

ecosystems is stored below ground and respiratory<br />

C-release from soils is a major component of the<br />

global C balance. <strong>The</strong> use of C-13-depleted CO 2 in a<br />

10-year free- air carbon dioxide enrichment (FACE)<br />

experiment, gave a unique opportunity to study<br />

the turnover of the C sequestered during this experiment.<br />

Soil organic matter (SOM), soil air and<br />

plant material were analysed for delta C-13 and C<br />

contents in the last year of the FACE experiment<br />

(2002) and in the two following growing seasons.<br />

After 10 years of exposure to CO 2 enrichment at<br />

600 ppmv, no significant differences in SOM C<br />

content could be detected between fumigated<br />

and non-fumigated plots. A C-13 depletion of 3.4<br />

parts per thousand was found in SOM (0-12 cm) of<br />

the fumigated soils in comparison with the control<br />

soils and a rapid decrease of this difference<br />

was observed after the end of fumigation. Within<br />

2 years, 49% of the C in this SOM (0-12 cm) was


120 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Soil and Lithosphere<br />

exchanged with fresh C, with the limitation that<br />

this exchange cannot be further dissected into respiratory<br />

decay of old C and freshly sequestered<br />

new C. By analysing the mechanistic effects of a<br />

drought on the plant-soil system it was shown<br />

that rhizosphere respiration is the dominant factor<br />

in soil respiration. Consideration of ecophysiological<br />

factors that drive plant activity is therefore<br />

important when soil respiration is to be investigated<br />

or modelled.<br />

European Journal of Soil Science, 2007, V58, N6,<br />

DEC, pp 1364-1372.<br />

08.1-217<br />

Methanotrophic activity in a diffusive methane/oxygen<br />

counter- gradient in an unsaturated<br />

porous medium<br />

Urmann K, Norina E S, Schroth M H, Zeyer J<br />

Switzerland<br />

Toxicology , Geochemistry & Geophysics , Agriculture,<br />

Soil Sciences , Water Resources<br />

Microbial methane (CH 4) oxidation is a main control<br />

on emissions of this important greenhouse<br />

gas from ecosystems such as contaminated aquifers<br />

or wetlands under aerobic conditions. Due to<br />

a lack of suitable model systems, we designed a<br />

laboratory column to study this process in diffusional<br />

CH 4/O-2 counter-gradients in unsaturated<br />

porous media. Analysis and simulations of the<br />

steady-state CH 4, CO 2 and O-2 gas profiles showed<br />

that in a 15-cm-deep active zone, CH 4 oxidation<br />

followed first-order kinetics with respect to CH 4<br />

with a high apparent first-order rate constant of<br />

similar to 30 h(-1). Total cell counts obtained using<br />

DAPI-staining suggested growth of methanotrophic<br />

bacteria, resulting in a high capacity<br />

for CH 4 oxidation. This together with apparent<br />

tolerance to anoxic conditions enabled a rapid<br />

response of the methanotrophic community to<br />

changing substrate availability, which was induced<br />

by changes in O-2 concentrations at the top<br />

of the column. Microbial oxidation was confirmed<br />

by a similar to 7 parts per thousand enrichment<br />

in CH 4 stable carbon isotope ratios along profiles.<br />

Using a fractionation factor of 1.025 +/- 0.0005 for<br />

microbial oxidation estimated from this shift and<br />

the fractionation factor for diffusion, simulations<br />

of isotope profiles agreed well with measured data<br />

confirming large fractionation associated with<br />

microbial oxidation. <strong>The</strong> designed column should<br />

be valuable for investigating response of methanotrophic<br />

bacteria to environmental parameters<br />

in future studies.<br />

Journal of Contaminant Hydrology, 2007, V94,<br />

N1-2, OCT 30, pp 126-138.<br />

08.1-218<br />

Release of C and N from roots of peas and oats<br />

and their availability to soil microorganisms<br />

Wichern F, Mayer J, Joergensen R G, Müller T<br />

Germany, Switzerland<br />

Plant Sciences , Agriculture, Soil Sciences , Geochemistry<br />

& Geophysics<br />

Nutrient mobilisation in the rhizosphere is driven<br />

by soil microorganisms and controlled by the<br />

release of available C compounds from roots. It is<br />

not known how the quality of release influences<br />

this process in situ. <strong>The</strong>refore, the present study<br />

was conducted to investigate the amount and<br />

turnover of rhizodeposition, in this study defined<br />

as root-derived C or N present in the soil after<br />

removal of roots and root fragments, released at<br />

different growth stages of peas (Pisum sativum L.)<br />

and oats (Avena sativa L.). Plants were grown in<br />

soil columns placed in a raised bed under outdoor<br />

conditions and simultaneously pulse labelled in<br />

situ with a C-13-glucose-N-15-urea solution using a<br />

stem feeding method. After harvest, C-13 and N-15<br />

was recovered in plant parts and soil pools, including<br />

the microbial biomass. Net rhizodeposition of<br />

C and N as a percentage of total plant C and N was<br />

higher in peas than in oats. Moreover, the C-to-N<br />

ratio of the rhizodeposits was lower in peas, and<br />

a higher proportion of the microbial biomass and<br />

inorganic N was derived from rhizodeposition.<br />

<strong>The</strong>se results suggest a positive plant-soil feedback<br />

shaping nutrient mobilisation. This process<br />

is driven by the C and N supply of roots, which has<br />

a higher availability in peas than in oats.<br />

Soil Biology Biochemistry, 2007, V39, N11, NOV, pp<br />

2829-2839.<br />

08.1-219<br />

Coupled mobilization of dissolved organic<br />

matter and metals (Cu and Zn) in soil columns<br />

Zhao L Y L, Schulin R, Weng L, Nowack B<br />

Switzerland, Netherlands<br />

Modelling , Agriculture, Soil Sciences , Forestry ,<br />

Geochemistry & Geophysics<br />

Dissolved organic carbon (DOC) is a key component<br />

involved in metal displacement in soils. In<br />

this study, we investigated the concentration<br />

profiles of soil-borne DOC, Cu and Zn at various<br />

irrigation rates with synthetic rain water under<br />

quasi steady-state conditions, using repacked soil<br />

columns with a metal-polluted topsoil and two<br />

unpolluted subsoils. Soil solution was collected<br />

using suction cups installed at centimeter intervals<br />

over depth. In the topsoil the concentrations<br />

of DOC, dissolved metals (Zn and Cu), major cations<br />

(Ca2+ and Mg2+) and anions (NO 3- and SO 4 2-)<br />

increased with depth. In the subsoil, the Cu and


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Soil and Lithosphere | Cryosphere<br />

Zn concentrations dropped to background levels<br />

within 2 cm. All compounds were much faster<br />

mobilized in the first 4 cm than in the rest of the<br />

topsoil. DOC and Cu concentrations were higher<br />

at higher flow rates for a given depth, whereas<br />

the concentrations of the other ions decreased<br />

with increasing flow rate. <strong>The</strong> decomposition of<br />

soil organic matter resulted in the formation of<br />

DOC, SO 4 2-, and NO 3- and was the main driver of<br />

the system. Regression analysis indicated that<br />

1.4 Cryosphere<br />

08.1-220<br />

ADEOS-II/GLI snow/ice products - Part II: Validation<br />

results using GLI and MODIS data<br />

Aoki T, Hori M, Motoyoshi H, Tanikawa T, Hachikubo<br />

A, Sugiura K, Yasunari T J, Storvold R, Eide H A,<br />

Stamnes K, Li W, Nieke J, Nakajima Y, Takahashi F<br />

Japan, Norway, Switzerland<br />

Modelling , Remote Sensing , Cryology / Glaciology<br />

For the validation of snow/ice products of the<br />

Advanced Earth Observing Satellite-II/<strong>Global</strong> Imager<br />

(ADEOS-II/GLI), several field campaigns were<br />

performed for various types of snow conditions<br />

with the Moderate Resolution Imaging Spectroradiometer<br />

(MODIS) and GLI overpasses at four sites<br />

in Alaska and eastern Hokkaido, Japan from 2001<br />

to 2005. <strong>The</strong> target satellite-derived snow parameters<br />

are snow surface temperature, mass fraction<br />

of soot, and two types of snow grain size retrieved<br />

from different spectral channels. <strong>The</strong> retrieved satellite<br />

products were compared with in-situ measured<br />

snow parameters based on snow pit work<br />

and snow sampling. <strong>The</strong> satellite- derived snow<br />

surface temperatures agreed well with in-situ<br />

measured values with a correlation coefficient<br />

(R-c) of 0.900 and a root-mean- square error (RMSE)<br />

of 1.1 K. <strong>The</strong> satellite-derived mass fractions of<br />

soot were close to in-situ measured mass fractions<br />

of snow impurities for the snow layer between the<br />

surface and down to 7 or 10 cm rather than between<br />

0 and 2 cm, while the satellite-derived absolute<br />

values were lower than the in-situ measured<br />

ones (R-c=0.506 and RMSE=5.0 parts per million by<br />

weight (ppmw)). This discrepancy is due primarily<br />

to the difference in the composition of snow impurities<br />

assumed in the satellite algorithm (soot)<br />

and measured in-situ (mineral dust) suggesting<br />

that the satellite retrieval of soot is not producing<br />

soot concentrations in many cases but rather<br />

dust. Snow grain sizes retrieved from two satellite<br />

121<br />

Cu mobilization was governed by DOC, whereas<br />

Zn mobilization was primarily determined by Ca<br />

and to a lesser extent by DOC. Labile Zn and Cu2+<br />

concentrations were well predicted by the NICA-<br />

Donnan model. <strong>The</strong> results highlight the value of<br />

high-resolution in-situ measurements of DOC and<br />

metal mobilization in soil profiles.<br />

Geochimica et Cosmochimica Acta, 2007, V71,<br />

N14, JUL 15, pp 3407-3418.<br />

channels lambda = 0.460 and 0.865 pm had better<br />

accuracy (R-c =0.840 and RMSE = 125 µm) than<br />

those from a satellite channel at lambda = 1.64<br />

µm (R-c=0.524 and RMSE = 123 µm) from the comparison<br />

with simply depth-averaged snow grain<br />

size. When similar comparisons are made with<br />

the depth-averaged measured grain size by a 1/e<br />

weighting using flux transmittance, the results<br />

for R-c and RMSE are not improved due to some<br />

difficulties in calculating the depth-averaging by<br />

a 1/e weighting. For all our satellite products, the<br />

possible causes of errors are (1) satellite sensor<br />

calibration and (2) the bidirectional reflectance<br />

model (directional emissivity model for surface<br />

temperature) used in the algorithm together with<br />

the atmospheric correction. Two ways to improve<br />

the in-situ measurements are (1) the representativeness<br />

of the measured values and (2) the measuring<br />

methods. Field measurements also indicated<br />

that the increased reflectance due to “sun<br />

crust” observed at wet snow surfaces under clear<br />

sky could cause an underestimation of satellitederived<br />

snow grain size. This problem will be<br />

more severe for the grain size retrieved from the<br />

channel at lambda = 1.64 µm.<br />

Remote Sensing of Environment, 2007, V111,<br />

N2-3, NOV 30, pp 274-290.<br />

08.1-221<br />

Current status of Andean glaciers<br />

Casassa G, Rivera A, Haeberli W, Jones G, Käser G,<br />

Ribstein P, Rivera A, Schneider C<br />

Chile, Switzerland, Canada, Austria, France, Germany<br />

Cryology / Glaciology , Meteorology & Atmospheric<br />

Sciences<br />

<strong>Global</strong> and Planetary <strong>Change</strong>, 2007, V59, N1-4,<br />

OCT, pp 1-9.


122 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Cryosphere<br />

08.1-222<br />

Diurnal production of gaseous mercury in the<br />

alpine snowpack before snowmelt<br />

Fain X, Grangeon S, Bahlmann E, Fritsche J, Obrist<br />

D, Dommergue A, Ferrari C P, Cairns W, Ebinghaus<br />

R, Barbante C, Cescon P, Boutron C<br />

France, Italy, Germany, Switzerland, USA<br />

Meteorology & Atmospheric Sciences , Cryology /<br />

Glaciology<br />

(1) In March 2005, an extensive mercury study was<br />

performed just before snowmelt at Col de Porte,<br />

an alpine site close to Grenoble, France. Total<br />

mercury concentration in the snowpack ranged<br />

from 80 + /- 08 to 160 +/- 15 ng l(-1), while reactive<br />

mercury was below detection limit (0.2 ng l(-1)).<br />

We observed simultaneously a production of gaseous<br />

elemental mercury (GEM) in the top layer<br />

of the snowpack and an emission flux from the<br />

snow surface to the atmosphere. Both phenomena<br />

were well correlated with solar irradiation,<br />

indicating photo-induced reactions in the snow<br />

interstitial air (SIA). <strong>The</strong> mean daily flux of GEM<br />

from the snowpack was estimated at similar to<br />

9 ng m(-2) d(-1). No depletion of GEM concentrations<br />

was observed in the SIA, suggesting no occurrence<br />

of oxidation processes. <strong>The</strong> presence of<br />

liquid water in the snowpack clearly enhanced<br />

GEM production in the SIA. Laboratory flux chamber<br />

measurements enabled us to confirm that<br />

GEM production from this alpine snowpack was<br />

first driven by solar radiation (especially UVA and<br />

UVB radiation), and then by liquid water in the<br />

snowpack. Finally, a large GEM emission from the<br />

snow surface occurred during snowmelt, and we<br />

report total mercury concentrations in meltwater<br />

of about 72 ng l(-1).<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND21, NOV 13 ARTN: D21311.<br />

08.1-223<br />

Validation of operational AVHRR subpixel<br />

snow retrievals over the European Alps based<br />

on ASTER data<br />

Foppa N, Hauser A, Oesch D, Wunderle S,<br />

Meister R<br />

Switzerland<br />

Remote Sensing , Cryology / Glaciology<br />

Snow is of great economic and social importance<br />

for the European Alps. Accurate monitoring of the<br />

alpine snow cover is a key component in studying<br />

regional climate change as well as in daily weather<br />

forecasting and snowmelt runoff modelling.<br />

<strong>The</strong>se applications require snow cover information<br />

on a high temporal resolution in near-real<br />

time. For the European Alps, operational snow<br />

cover fraction maps are generated on a daily basis<br />

using data from the Advanced Very High Resolution<br />

Radiometer (AVHRR) on board the National<br />

Oceanic and Atmospheric Administration (NOAA)<br />

platforms. Snow cover distribution is inherently<br />

discontinuous and heterogeneous in this mountainous<br />

region. We have therefore implemented a<br />

straightforward multiple endmember unmixing<br />

approach to estimate fractional snow cover. Subpixel<br />

proportions are difficult to validate because<br />

similar products are not available and appropriate<br />

ground-based observations do not exist. In this<br />

study, we validate AVHRR subpixel snow retrievals<br />

using binary classified data sets from the Advanced<br />

Spaceborne <strong>The</strong>rmal Emission and Reflection Radiometer<br />

(ASTER) to establish absolute errors of<br />

our operational approach at three test sites. Our<br />

analysis indicates that the AVHRR subpixel maps<br />

compare well with the aggregated ASTER data,<br />

showing an overall correlation of 0.78 and providing<br />

subpixel estimates with a mean absolute error<br />

of 10.4% fractional snow cover. Discrepancies between<br />

AVHRR and ASTER snow fraction maps can<br />

be attributed to varying snow conditions, terrain<br />

effects and density in forest cover.<br />

International Journal of Remote Sensing, 2007,<br />

V28, N21, pp 4841-4865.<br />

08.1-224<br />

An overview of snow photochemistry: evidence,<br />

mechanisms and impacts<br />

Grannas A M, Jones A E, Dibb J, Ammann M,<br />

Anastasio C, Beine H J, Bergin M, Bottenheim J,<br />

Boxe C S, Carver G, Chen G, Crawford J H, Domine<br />

F, Frey M M, Guzman M I, Heard D E, Helmig D,<br />

Hoffmann M R, Honrath R E, Huey L G, Hutterli M,<br />

Jacobi H W, Klan P, Lefer B, Mc Connell J, Plane J,<br />

Sander R, Savarino J, Shepson P B, Simpson W R,<br />

Sodeau J R, von Glasow R, Weller R, Wolff E W,<br />

Zhu T<br />

USA, England, Switzerland, Italy, Canada, France,<br />

Germany, Czech Republic, Ireland, Peoples R China<br />

Cryology / Glaciology , Meteorology & Atmospheric<br />

Sciences<br />

It has been shown that sunlit snow and ice plays<br />

an important role in processing atmospheric species.<br />

Photochemical production of a variety of<br />

chemicals has recently been reported to occur in<br />

snow/ice and the release of these photochemically<br />

generated species may significantly impact the<br />

chemistry of the overlying atmosphere. Nitrogen<br />

oxide and oxidant precursor fluxes have been measured<br />

in a number of snow covered environments,<br />

where in some cases the emissions significantly<br />

impact the overlying boundary layer. For example,<br />

photochemical ozone production (such as that<br />

occurring in polluted mid-latitudes) of 3-4 ppbv/


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Cryosphere<br />

day has been observed at South Pole, due to high<br />

OH and NO levels present in a relatively shallow<br />

boundary layer. Field and laboratory experiments<br />

have determined that the origin of the observed<br />

NOx flux is the photochemistry of nitrate within<br />

the snowpack, however some details of the mechanism<br />

have not yet been elucidated. A variety of<br />

low molecular weight organic compounds have<br />

been shown to be emitted from sunlit snowpacks,<br />

the source of which has been proposed to be either<br />

direct or indirect photo-oxidation of natural<br />

organic materials present in the snow. Although<br />

myriad studies have observed active processing<br />

of species within irradiated snowpacks, the fundamental<br />

chemistry occurring remains poorly<br />

understood. Here we consider the nature of snow<br />

at a fundamental, physical level; photochemical<br />

processes within snow and the caveats needed for<br />

comparison to atmospheric photochemistry; our<br />

current understanding of nitrogen, oxidant, halogen<br />

and organic photochemistry within snow; the<br />

current limitations faced by the field and implications<br />

for the future.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N16, pp 4329-4373.<br />

08.1-225<br />

Snow avalanche hazard modelling of large<br />

areas using shallow water numerical methods<br />

and GIS<br />

Gruber U, Bartelt P<br />

Switzerland<br />

Cryology / Glaciology , Modelling , Instruments &<br />

Instrumentation<br />

Snow avalanches threaten settlements and roads<br />

in steep mountainous areas. Hazard mitigation<br />

strategies apply numerical models in combination<br />

with GIS-based methods to determine run out distances<br />

and pressure maps of snow avalanches in<br />

three-dimensional terrain. <strong>The</strong> snow avalanche<br />

modelling system is usually applied to study<br />

single avalanche tracks. In this paper we investigate<br />

the application of a numerical modelling<br />

system for large area hazard analysis. We begin by<br />

briefly presenting the depth-averaged equations<br />

governing avalanche flow. <strong>The</strong>n, we describe the<br />

statistical and GIS-based methods that are applied<br />

to define the initial fracture depths and release<br />

areas for snow avalanche modelling. We discuss<br />

the calibration of the avalanche model friction<br />

coefficients for extreme avalanches in function<br />

of altitude, avalanche size and topography. Seven<br />

test sites with areas between 100 and 350 km(2),<br />

that are well distributed over the different snow<br />

climates and elevation ranges of Switzerland,<br />

were used to calibrate the model by comparing<br />

123<br />

the simulation results with historic avalanche<br />

events and existing avalanche hazard maps. We<br />

then show how the avalanche modelling system<br />

was applied over the mountainous region of Switzerland<br />

(25,000 km(2)) to delineate forests with<br />

protective function against avalanches.<br />

Environmental Modelling Software, 2007, V22,<br />

N10, OCT, pp 1472-1481.<br />

08.1-226<br />

Retreat scenarios of Unteraargletscher, Switzerland,<br />

using a combined ice-flow mass-balance<br />

model<br />

Huss M, Sugiyama S, Bauder A, Funk M<br />

Switzerland, Japan<br />

Modelling , Meteorology & Atmospheric Sciences ,<br />

Cryology / Glaciology<br />

<strong>The</strong> future evolution of Unteraargletscher, a large<br />

valley glacier in the <strong>Swiss</strong> Alps, is assessed for the<br />

period 2005 to 2050 using a flowline model. Detailed<br />

measurements of surface velocity from the<br />

last decade allow us to relate ice flux to glacier<br />

thickness and width. Mass balance is calculated<br />

using a distributed temperature- index model<br />

calibrated with ice volume changes derived independently<br />

from comparison of repeated digital<br />

elevation models. <strong>The</strong> model was validated for the<br />

period 1961 to 2005 and showed good agreement<br />

between the simulated and observed evolution<br />

of surface geometry. Regional climate scenarios<br />

with seasonal resolution were used to investigate<br />

the anticipated response of Unteraargletscher to<br />

future climate changes. Three mass balance scenarios<br />

were defined, corresponding to 2.5%, 50%,<br />

and 97.5% quantiles of a statistical analysis of 16<br />

different climate model results. We present a forecast<br />

of the future extent of Unteraargletscher in<br />

the next five decades and analyze relevant parameters<br />

with respect to the past. <strong>The</strong> model predicts<br />

a retreat of the glacier terminus of 800-1025 in by<br />

2035, and of 1250-2300 in by 2050. <strong>The</strong> debris coverage<br />

of the glacier tongue reduces the retreat rate<br />

by a factor of three. <strong>The</strong> thinning, rate increased<br />

by 50-183% by 2050 depending on the scenario applied,<br />

compared to the period 1997 to 2005.<br />

Arctic Antarctic and Alpine Research, 2007, V39,<br />

N3, AUG, pp 422-431.


124 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Cryosphere<br />

08.1-227<br />

Hazard assessment of potential periglacial<br />

debris flows based on GIS- based spatial modelling<br />

and geophysical field surveys: A case<br />

study in the <strong>Swiss</strong> Alps<br />

Kneisel C, Rothenbühler C, Keller F, Haeberli W<br />

Germany, Switzerland<br />

Cryology / Glaciology , Modelling , Geomorphology<br />

Geology<br />

Combined geomorphological and geophysical approaches<br />

were used to perforrn a hazard assessment<br />

of potential periglacial debris flow. Possible<br />

debris flow initiation zones were identified within<br />

a GIS- based model and located based on geomorphic<br />

attributes which contribute the most to this<br />

type of instability. In permafrost- affected alpine<br />

environments, these include the extent and location<br />

of ground ice and permafrost. In a potential<br />

debris flow-starting zone in the Upper Engadine<br />

(moraine/debris rock glacier complex Boval) twodimensional<br />

electrical resistivity surveys were<br />

used to detect the presence/absence of permafrost<br />

and to estimate active- layer depth. <strong>The</strong> results<br />

show that the moraine complex represents<br />

a periglacial debris reservoir which consists of<br />

frozen and unfrozen debris. <strong>The</strong> ice-bonded part<br />

of the moraine is largely protected from sudden<br />

destabilisation and retrogressive erosion can be<br />

assumed to be limited. However, future degradation<br />

or loss of permafrost in the lower parts of the<br />

debris rock glacier would increase the amount of<br />

erodible debris and generally reduce mechanical<br />

stability.<br />

Permafrost and Periglacial Processes, 2007, V18,<br />

N3, JUL-SEP, pp 259-268.<br />

08.1-228<br />

Tracing glacier wastage in the Northern Tien<br />

Shan (Kyrgyzstan/Central Asia) over the last<br />

40 years<br />

Niederer P, Bilenko V, Ershova N, Hurni H, Yerokhin<br />

S, Maselli D<br />

Switzerland, Kyrgyzstan<br />

Cryology / Glaciology , Meteorology & Atmospheric<br />

Sciences<br />

<strong>The</strong> status and dynamics of glaciers are crucial<br />

for agriculture in semiarid parts of Central Asia,<br />

since river flow is characterized by major runoff in<br />

spring and summer, supplied by glacier- and snowmelt.<br />

Ideally, this coincides with the critical period<br />

of water demand for irrigation. <strong>The</strong> present study<br />

shows a clear trend in glacier retreat between 1963<br />

and 2000 in the Sokoluk watershed, a catchment of<br />

the Northern Tien Shan mountain range in Kyrgyzstan.<br />

<strong>The</strong> overall area loss of 28% observed for the<br />

period 1963-2000, and a clear acceleration of wast-<br />

age since the 1980s, correlate with the results of<br />

previous studies in other regions of the Tien Shan<br />

as well as the Alps. In particular, glaciers smaller<br />

than 0.5 km(2) have exhibited this phenomenon<br />

most starkly. While they registered a medium decrease<br />

of only 9.1% for 1963-1986, they lost 41.5% of<br />

their surface area between 1986 and 2000. Furthermore,<br />

a general increase in the minimum glacier<br />

elevation of 78 m has been observed over the last<br />

three decades. This corresponds to about one-third<br />

of the entire retreat of the minimum glacier elevation<br />

in the Northern Tien Shan since the Little Ice<br />

Age maximum.<br />

Climatic <strong>Change</strong>, 2008, V86, N1-2, JAN, pp<br />

227-234.<br />

08.1-229<br />

Validation of the SNOWPACK model in five different<br />

snow zones in Finland<br />

Rasmus S, Gronholm T, Lehning M, Rasmus K,<br />

Kulmala M<br />

Finland, Switzerland<br />

Cryology / Glaciology , Modelling<br />

<strong>The</strong> performance of a snow pack structure model<br />

SNOWPACK was studied in five locations around<br />

Finland during two winters. Reasonable agreement<br />

between modelled and observed snow depth<br />

and snow pack structure evolution was found<br />

in all other locations except in coastal Santala.<br />

Agreement grew when going towards the north;<br />

better agreements were obtained during the early<br />

winter than during the melting period. Several<br />

test runs with changed input data were done for<br />

Hyytiala. Water equivalent, temperature, grain<br />

form and grain size were the most sensitive of the<br />

model output quantities to changes in the input<br />

data. <strong>The</strong> use of measured precipitation instead<br />

of snow depth for driving the mass balance or the<br />

use of different radiation schemes had relatively<br />

large effects on the model output. Model sensitivity<br />

was high when many phase changes were involved<br />

such as during the melting phase in spring<br />

or in temperate climate zones.<br />

Boreal Environment Research, 2007, V12, N4, AUG<br />

27, pp 467-488.<br />

08.1-230<br />

Rockglacier activity studies on a regional scale:<br />

comparison of geomorphological mapping and<br />

photogrammetric monitoring<br />

Roer I, Nyenhuis M<br />

Switzerland, Germany<br />

Geomorphology , Geology , Instruments & Instrumentation<br />

, Cryology / Glaciology<br />

In their spatial distribution as well as in their<br />

different states of activity, rockglaciers imply


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Cryosphere<br />

important information on former and recent<br />

permafrost conditions. Two different methods<br />

were applied in one study area (Turtmann Valley,<br />

<strong>Swiss</strong> Alps) in order to compare their suitability<br />

in assessing rockglacier activity. <strong>The</strong> comparison<br />

of geomorphological mapping and photogrammetric<br />

monitoring demonstrated a good accordance,<br />

especially on a regional scale. On a local<br />

scale, some differences in delimitation of the<br />

landforms as well as in the degree of activity were<br />

found. One reason for the observed differences<br />

is the qualitative character of geomorphological<br />

mapping resulting from the variable suitability<br />

of single parameters and combinations thereof in<br />

the determination of rockglacier activity. Based<br />

on these results, geomorphological mapping of<br />

rockglaciers can be improved by data from photogrammetric<br />

monitoring. <strong>The</strong>refore, at best the<br />

two methods are combined when analysing former<br />

and present permafrost distribution.<br />

Earth Surface Processes and Landforms, 2007, V32,<br />

N12, OCT 30, pp 1747-1758.<br />

08.1-231<br />

Influence of different digital terrain models<br />

(DTMs)on alpine permafrost modeling<br />

Salzmann N, Gruber S, Hugentobler M, Hölzle M<br />

Switzerland<br />

Modelling , Cryology / Glaciology , Instruments &<br />

Instrumentation<br />

<strong>The</strong> thawing of alpine permafrost due to changes<br />

in atmospheric conditions can have a severe impact,<br />

e.g., on the stability of rock walls. <strong>The</strong> energy<br />

balance model, PERMEBAL, was developed<br />

in order to simulate the changes and distribution<br />

of ground surface temperature (GST) in complex<br />

high-mountain topography. In such environments,<br />

the occurrence of permafrost depends greatly on<br />

the topography, and thus, the digital terrain model<br />

(DTM) is an important input of PERMEBAL. This<br />

study investigates the influence of the DTM on the<br />

modeling of the GST. For this purpose, PERMEBAL<br />

was run with six different DTMs. Five of the six<br />

DTMs are based on the same base data, but were<br />

generated using different interpolators. To ensure<br />

that only the topographic effect on the GST is calculated,<br />

the snow module was turned off and uniform<br />

conditions were assumed for the whole test<br />

area. <strong>The</strong> analyses showed that the majority of the<br />

deviations between the different model outputs<br />

related to a reference DTM had only small differences<br />

of up to 1 K, and only a few pixels deviated<br />

more than 1 K. However, we also observed that the<br />

use of different interpolators for the generation of<br />

a DTM can result in large deviations of the model<br />

output. <strong>The</strong>se deviations were mainly found at<br />

125<br />

topographically complex locations such as ridges<br />

and foot of slopes.<br />

Environmental Modeling Assessment, 2007, V12,<br />

N4, NOV, pp 303-313.<br />

08.1-232<br />

Modeling the effect of snow and ice on the<br />

global environmental fate and long-range<br />

transport potential of semivolatile organic<br />

compounds<br />

Stocker J, Scheringer M, Wegmann F,<br />

Hungerbühler K<br />

Switzerland<br />

Modelling , Cryology / Glaciology , Geochemistry &<br />

Geophysics<br />

Snow and ice have been implemented in a global<br />

multimedia box model to investigate the influence<br />

of these media on the environmental fate and longrange<br />

transport (LRT) of sernivolatile organic compounds<br />

(SOCs). Investigated compounds include<br />

HCB, PC1328, PCB180, PBDE47, PBDE209, alpha-<br />

HCH, and dacthal. In low latitudes, snow acts as a<br />

transfer medium taking up chemicals from air and<br />

releasing them to water or soil during snowmelt. In<br />

high latitudes, snow and ice shield water, soil, and<br />

vegetation from chemical deposition. In the model<br />

version including snow and ice (scenario 2), the mass<br />

of chemicals in soil in high latitudes is between 27%<br />

(HCB) and 97% (alpha-HCH) of the mass calculated<br />

with the model version without snow and ice (scenario<br />

1). Amounts in Arctic seawater in scenario 2<br />

are 8% (alpha- HCH) to 21% (dacthal) of the amounts<br />

obtained in scenario 1. For all investigated chemicals<br />

except alpha-HCH, presence of snow and ice in the<br />

model increases the concentration in air by a factor<br />

of 2(HCB)to 10(PBDE209). Because of reduced net deposition<br />

to snow-covered surfaces in high latitudes,<br />

LRT to the Arctic is reduced for most chemicals<br />

whereas transport to the south is more pronounced<br />

than in scenario 1 (“southward shift”). <strong>The</strong> presence<br />

of snow and ice thus considerably changes the environmental<br />

fate of SOCs.<br />

Environmental Science Technology, 2007, V41,<br />

N17, SEP 1, pp 6192-6198.<br />

08.1-233<br />

Climate warming revealed by englacial temperatures<br />

at Col du Dome (4250 m, Mont Blanc<br />

area)<br />

Vincent C, Le Meur E, Six D, Possenti P, Lefebvre E,<br />

Funk M<br />

France, Switzerland<br />

Meteorology & Atmospheric Sciences , Cryology /<br />

Glaciology<br />

Temperatures were measured in two deep boreholes<br />

drilled at the same location in the ice at Col


126 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Cryosphere | Oceans and Fresh Water<br />

du Dome (4250 m) in 1994 and 2005, providing<br />

clear evidence of atmospheric warming. <strong>The</strong> 1994<br />

temperature profile was already far from steady<br />

state conditions. Results from a heat transfer<br />

model reveal that the englacial temperature increase<br />

cannot be explained solely by atmospheric<br />

temperature rise. <strong>The</strong> latent heat produced by the<br />

refreezing of surface meltwater below the surface<br />

also contributes to the englacial temperature increase.<br />

Although surface melting is normally very<br />

low at this altitude, this contribution became significant<br />

after 1980 for temperatures at the top of<br />

the borehole. Simulations for different climatic<br />

scenarios show that glaciated areas located between<br />

3500 and 4250 m could become temperate<br />

in the future. This warming could have a major<br />

impact on the stability of hanging glaciers frozen<br />

to their beds if the melting point is reached.<br />

Geophysical Research Letters, 2007, V34, N16,<br />

AUG 18 ARTN: L16502.<br />

08.1-235<br />

Impact of monsoonal rains on spatial scaling<br />

patterns in water chemistry of a semiarid river<br />

network<br />

Acuna V, Dahm C N<br />

Switzerland, USA<br />

Hydrology , Geochemistry & Geophysics<br />

<strong>The</strong> chemical composition of surface waters of<br />

nine streams with drainage sizes ranging from<br />

44 to 8900 km(2) within a semiarid catchment<br />

in the southwestern United States was examined<br />

over the monsoonal season of 2006. Primary goals<br />

were to determine the impact of monsoonal rains<br />

on linkages between landscape cover features<br />

and water chemistry in a semiarid river network<br />

and to identify whether drainage size influences<br />

the temporal variability in water chemistry of<br />

streams. Landscape cover features (geology, soil,<br />

and vegetation types) were quantified for the subcatchment<br />

upstream of each study site and the<br />

riparian ecotone. Processes of binary mixing, dilution,<br />

and concentration were identified by end<br />

member mixing analysis (EMMA). Results showed<br />

that most chemical constituents corresponded<br />

to geological features at the basin scale, but<br />

other constituents (TSS and PO 4 3-) corresponded<br />

more closely to riparian features. Importantly,<br />

statistical relationships between land cover and<br />

water chemistry differed between baseflow and<br />

08.1-234<br />

Introduction to special section: Permafrost and<br />

seasonally frozen ground under a changing<br />

climate<br />

Zhang T, Nelson F E, Gruber S<br />

USA, Switzerland<br />

Cryology / Glaciology , Meteorology & Atmospheric<br />

Sciences<br />

Journal of Geophysical Research Earth Surface,<br />

2007, V112, NF2, JUN 28 ARTN: F02S01.<br />

1.5 Oceans and Fresh Water Systems<br />

monsoonal conditions, suggesting that seasonal<br />

changes in hydrologic routing and water sources<br />

(e. g., overland flow versus groundwater sources)<br />

have important consequences for stream chemistry.<br />

In contrast with mesic drainages, temporal<br />

variability in water chemistry increased with spatial<br />

scale. <strong>The</strong> variety of contributing water sources<br />

and the relative effect of dilution and concentration<br />

in each spatial scale may be underlying<br />

processes that explain differences across spatial<br />

scales. Observed patterns in the Gila basin suggest<br />

that climate variability interacts with hydrologic<br />

routing to influence spatial patterns of stream water<br />

chemistry in arid basins. Observations made<br />

here may be similar to other systems with strongly<br />

seasonal climate patterns, and the underlying<br />

determinants of stream chemistry change with<br />

drainage size.<br />

Journal of Geophysical Research Biogeosciences,<br />

2007, V112, NG4, DEC 1 ARTN: G04009.<br />

08.1-236<br />

<strong>The</strong> tracing of riverine U in Arctic seawater<br />

with very precise U-234 /U-238 measurements<br />

Andersen M B, Stirling C H, Porcelli D, Halliday A N,<br />

Andersson P S, Baskaran M<br />

England, Switzerland, New Zealand, USA<br />

Geochemistry & Geophysics , Oceanography ,<br />

Hydrology


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

<strong>The</strong> riverine flux of U that enters the deep oceans<br />

is not well constrained since the net losses during<br />

estuarine mixing are difficult to quantify. Riverine-dissolved<br />

U normally has a higher U-234/(238)<br />

U activity ratio (U-234/U-238(ar)) than the uniform<br />

value that characterizes open ocean seawater and<br />

could be used as a tracer of riverine inputs if one<br />

could resolve subtle variations in seawater composition.<br />

Using new mass spectrometry techniques<br />

we achieve a long-term reproducibility +/- 0.3<br />

parts per thousand on U-234/U-238 (ar) which permits<br />

the tracing of riverine U in seawater samples<br />

from the Arctic - a partially restricted basin that is<br />

ideal for such a study. We find that surface waters<br />

from the Arctic basins carry elevated U-234/(238)<br />

Uar when compared with deep ocean seawater.<br />

Samples from the Canada Basin have a significant<br />

freshwater component and provide evidence that<br />

the Mackenzie River loses similar to 65% of its U<br />

in the Mackenzie shelf/estuary zone before entering<br />

the deeper basin. This is in contrast to samples<br />

from the Makarov Basin, which provide evidence<br />

that all of the freshwater input is derived from<br />

the major Yenisey River alone, despite the proximity<br />

of the Lena and Ob Rivers. <strong>The</strong> differing behaviour<br />

of U between the Mackenzie and Yenisey<br />

Rivers is most likely a consequence of the strong<br />

binding of U to dissolved organic matter (DOC) or<br />

secondary phases in these rivers. <strong>The</strong> Yenisey River<br />

appears to transport the majority of the DOC<br />

through the shelf and into the Makarov Basin. In<br />

contrast, the Mackenzie River appears to lose a<br />

significant amount of DOC (> 50%) in the estuary/<br />

shelf zone, which may lead to loss of associated<br />

U. <strong>The</strong>se findings offer a more detailed picture of<br />

the fresh riverine water flow patterns in the Arctic<br />

Ocean when compared to other geochemical proxies.<br />

<strong>The</strong> non-conservative behaviour of U in the<br />

Mackenzie River through the shelf/estuaries has<br />

important implications for U input into oceans<br />

and the total marine budget.<br />

Earth and Planetary Science Letters, 2007, V259,<br />

N1-2, JUL 15, pp 171-185.<br />

08.1-237<br />

Effects of Alpine hydropower dams on particle<br />

transport and lacustrine sedimentation<br />

Anselmetti F S, Bühler R, Finger D, Girardclos S,<br />

Lancini A, Rellstab C, Sturm M<br />

Switzerland<br />

Hydrology , Limnology , Geomorphology , Water<br />

Resources<br />

<strong>The</strong> effects of high-alpine hydropower damming<br />

on lacustrine sedimentation and transport of<br />

solid particles were investigated in the glaciated<br />

Grimsel area and in downstream Lake Brienz,<br />

127<br />

providing quantitative denudation rates and sediment<br />

yield on a source-sink basis. A total of 271<br />

kt/yr of solid particles entered the Grimsel reservoirs<br />

on average in the last 71 years, mostly by<br />

turbiditic underflows that focused sedimentation<br />

in depocenters upstream of obstacles such as bedrock<br />

ridges, submerged moraines, or dams. This<br />

is equivalent to a sediment yield of 2430 t/(km(2)<br />

yr) in the catchment (111.5 km(2)) or a denudation<br />

rate of 0.94 mm/yr. A total of 39 kt/yr of the fine<br />

fraction (


128 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

experiment, biomass production appeared to be<br />

co-limited by N and P, while N fertilisation dramatically<br />

reduced plant species richness; these<br />

effects became weaker subsequently. Following<br />

two extreme winter floods in 1993-94 and 1994-95<br />

and a drought in spring 1996, the effects of fertilisation<br />

disappeared between 1998 and 2001 and<br />

then appeared again. Flooding caused an overall<br />

reduction in species richness (from c. 24 to 15 species<br />

m(-2)) and an increase in biomass production,<br />

which were only partly reversed after ten years.<br />

Conclusions: Long time series are necessary to<br />

understand vegetation dynamics and nutrient<br />

limitation in river floodplains, since they are influenced<br />

by occasional flood and drought events,<br />

whose effects may persist for more than ten years.<br />

A future increase in flooding frequency might<br />

be detrimental to species richness in floodplain<br />

grasslands.<br />

Journal of Vegetation Science, 2007, V18, N5, OCT,<br />

pp 625-634.<br />

08.1-239<br />

Large-scale climatic signatures in lakes across<br />

Europe: a meta- analysis<br />

Blenckner T, Adrian R, Livingstone D M, Jennings<br />

E, Weyhenmeyer G A, George D G, Jankowski T,<br />

Jarvinen M, Aonghusa Caitriona N, Noges T, Straile<br />

D, Teubner K<br />

Sweden, Germany, Switzerland, Ireland, England,<br />

Finland, Estonia, Austria<br />

Zoology , Meteorology & Atmospheric Sciences ,<br />

Limnology , Marine & Freshwater Biology , Ecology<br />

Recent studies have highlighted the impact of the<br />

winter North Atlantic Oscillation (NAO) on water<br />

temperature, ice conditions, and spring plankton<br />

phenology in specific lakes and regions in Europe.<br />

Here, we use meta-analysis techniques to test<br />

whether 18 lakes in northern, western, and central<br />

Europe respond coherently to winter climate<br />

forcing, and to assess the persistence of the winter<br />

climate signal in physical, chemical, and biological<br />

variables during the year. A meta-analysis<br />

approach was chosen because we wished to emphasize<br />

the overall coherence pattern rather than<br />

individual lake responses. A particular strength<br />

of our approach is that time-series from each of<br />

the 18 lakes were subjected to the same robust<br />

statistical analysis covering the same 23-year period.<br />

Although the strongest overall coherence in<br />

response to the winter NAO was exhibited by lake<br />

water temperatures, a strong, coherent response<br />

was also exhibited by concentrations of soluble<br />

reactive phosphorus and soluble reactive silicate,<br />

most likely as a result of the coherent response<br />

exhibited by the spring phytoplankton bloom.<br />

Lake nitrate concentrations showed significant<br />

coherence in winter. With the exception of the<br />

cyanobacterial biomass in summer, phytoplankton<br />

biomass in all seasons was unrelated to the<br />

winter NAO. A strong coherence in the abundance<br />

of daphnids during spring can most likely be attributed<br />

to coherence in daphnid phenology. A<br />

strong coherence in the summer abundance of<br />

the cyclopoid copepods may have been related to<br />

a coherent change in their emergence from resting<br />

stages. We discuss the complex nature of the<br />

potential mechanisms that drive the observed<br />

changes.<br />

<strong>Global</strong> <strong>Change</strong> Biology, 2007, V13, N7, JUL, pp<br />

1314-1326.<br />

08.1-240<br />

<strong>The</strong> ecology of European ponds: defining<br />

the characteristics of a neglected freshwater<br />

habitat<br />

Cereghino R, Biggs J, Oertli B, Declerck S<br />

France, England, Switzerland, Belgium<br />

Marine & Freshwater Biology , Biodiversity , Ecology<br />

<strong>The</strong>re is growing awareness in Europe of the importance<br />

of ponds, and increasing understanding<br />

of the contribution they make to aquatic biodiversity<br />

and catchment functions. Collectively, they<br />

support considerably more species, and specifically<br />

more scarce species, than other freshwater waterbody<br />

types. Ponds create links (or stepping stones)<br />

between existing aquatic habitats, but also provide<br />

ecosystem services such as nutrient interception,<br />

hydrological regulation, etc. In addition, ponds are<br />

powerful model systems for studies in ecology, evolutionary<br />

biology and conservation biology, and<br />

can be used as sentinel systems in the monitoring<br />

of global change. Ponds have begun to receive<br />

greater protection, particularly in the Mediterranean<br />

regions of Europe, as a result of the identification<br />

of Mediterranean temporary ponds as a priority<br />

in the EU Habitats Directive. Despite this, they<br />

remain excluded from the provisions of the Water<br />

Framework Directive, even though this is intended<br />

to ensure the good status of all waters. <strong>The</strong>re is now<br />

a need to strengthen, develop and coordinate existing<br />

initiatives, and to build a common framework<br />

in order to establish a sound scientific and practical<br />

basis for pond conservation in Europe. <strong>The</strong> articles<br />

presented in this issue are intended to explore<br />

scientific problems to be solved in order to increase<br />

the understanding and the protection of ponds, to<br />

highlight those aspects of pond ecology that are<br />

relevant to freshwater science, and to bring out research<br />

areas which are likely to prove fruitful for<br />

further investigation.<br />

Hydrobiologia, 2008, V597, FEB, pp 1-6.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

08.1-241<br />

Biodiversity and distribution patterns of freshwater<br />

invertebrates in farm ponds of a southwestern<br />

French agricultural landscape<br />

Cereghino R, Ruggiero A, Marty P, Angelibert S<br />

France, Switzerland<br />

Biodiversity , Marine & Freshwater Biology , Agriculture,<br />

Soil Sciences , Ecology , Zoology<br />

We assessed the importance for biodiversity of<br />

man-made farm ponds in an agricultural landscape<br />

in SW France lacking natural wetlands.<br />

<strong>The</strong> ponds were originally created to provide a<br />

variety of societal services (irrigation, visual amenity,<br />

water for cattle, etc.). We also assessed the<br />

environmental factors influencing invertebrate<br />

assemblages in these ponds. Only 18 invertebrate<br />

taxa out of 114 taxa occurring in the study area<br />

were common to ponds and rivers indicating that<br />

the contribution of farm ponds to freshwater biodiversity<br />

was potentially high. A Self-Organizing<br />

Map (SOM, neural network) was used to classify 36<br />

farm ponds in terms of the 52 invertebrate families<br />

and genera they supported, and to specify<br />

the influence of environmental variables related<br />

to land-use and to pond characteristics on the<br />

assemblage patterns. <strong>The</strong> SOM trained with taxa<br />

occurrences showed five clusters of ponds, most<br />

taxa occurring only in 1-2 clusters of ponds. Abandoned<br />

ponds tended to support higher numbers<br />

of taxa, probably because they were allowed to<br />

undergo a natural succession. Nevertheless, abandoned<br />

ponds were also amongst the largest, so<br />

that it remained difficult to separate the effects of<br />

pond size and abandonment, although both factors<br />

were likely to interact to favour higher taxon<br />

richness. <strong>The</strong> invertebrate communities in the<br />

ponds appeared to be influenced mainly by widely<br />

acting environmental factors (e.g. area, regionalization<br />

of assemblages) with little evidence that<br />

pond use (e.g. cattle watering, amenity) generally<br />

influenced assemblage composition. Our results<br />

support the idea that agricultural landscapes<br />

containing man- made ponds make a significant<br />

contribution to freshwater biodiversity indicating<br />

that protection of farm ponds from threats such<br />

as in- filling and pollution can make a positive<br />

contribution to the maintenance of aquatic biodiversity.<br />

This added value for biodiversity should<br />

be considered when calculating the economic<br />

costs and benefits of constructing water bodies<br />

for human activities.<br />

Hydrobiologia, 2008, V597, FEB, pp 43-51.<br />

129<br />

08.1-242<br />

<strong>The</strong> Mar Menor lagoon (SE Spain): A singular<br />

natural ecosystem threatened by human<br />

activities<br />

Conesa H M, Jimenez Carceles F J<br />

Switzerland, Spain<br />

Ecology , Agriculture, Soil Sciences , Marine &<br />

Freshwater Biology<br />

<strong>The</strong> Mar Menor lagoon is one of the most important<br />

ecological singularities in the Mediterranean<br />

area. At the same time, it is an area where many<br />

economic and industrial activities meet. <strong>The</strong> sum<br />

of the impacts of mining, agriculture and urban<br />

development in the surroundings to the lagoon<br />

during the last decades has affected its ecosystem.<br />

In this paper, we have reviewed the studies done<br />

by researchers over two decades regarding the<br />

impacts of human activities in the lagoon, reporting<br />

data of contamination levels and the effects<br />

generated in the ecosystem of the lagoon. <strong>The</strong><br />

discharge of enriched nutrient waters seems to be<br />

the most important input in the lagoon. <strong>Change</strong>s<br />

to more friendly agricultural techniques in the<br />

surrounding areas are therefore necessary. After<br />

our review, we can conclude that it is necessary<br />

to have higher efforts from the public administrations<br />

and stricter environmental regulations in<br />

order to preserve, on one hand, the important ecological<br />

values of the lagoon, and on other hand,<br />

public health.<br />

Marine Pollution Bulletin, 2007, V54, N7, JUL, pp<br />

839-849.<br />

08.1-243<br />

Earth Observation for wetland inventory, assessment<br />

and monitoring<br />

Davidson N C, Finlayson C M<br />

Switzerland, Sri Lanka<br />

Marine & Freshwater Biology , Instruments & Instrumentation<br />

, Remote Sensing , Ecology<br />

1. Wetland inventory, assessment and monitoring<br />

are widely recognized as essential tools for a<br />

range of purposes that underpin sound decisionmaking<br />

and the management of wetlands so as to<br />

maintain their ecological character, including the<br />

critical services they provide to people worldwide.<br />

2. In recognition of this, the Ramsar Convention<br />

on Wetlands has adopted a suite of tools designed<br />

for: (i) describing the ecological character of wetlands;<br />

(ii) assessing the pressures and associated<br />

risks of adverse change; and (iii) monitoring the<br />

extent of any change that occurs as a consequence<br />

of management actions. 3. As a prelude to considering<br />

the application of Earth Observation techniques<br />

to wetlands a review of the needs and purposes<br />

of inventory, assessment and monitoring is


130 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

provided and linked with the wetlands ‘toolkit’<br />

that the Convention has developed. In particular<br />

the usefulness of Earth Observation for undertaking<br />

such work more widely, and making its results<br />

more accessible to users, is considered. 4. As<br />

the wide typological, geographical and temporal<br />

variability of wetlands poses major challenges for<br />

inventory and assessment there have been many<br />

calls for the effective application of Earth Observation.<br />

In response a number of remote-sensing<br />

techniques have been developed or are being considered,<br />

such as the application of satellite-based<br />

radar, with more recent attention given to the<br />

application of long-wavelength (L-band) synthetic<br />

aperture radar. Copyright (c) 2007 John Wiley &<br />

Sons, Ltd.<br />

Aquatic Conservation Marine and Freshwater Ecosystems,<br />

2007, V17, N3, MAY, pp 219-228.<br />

08.1-244<br />

Biodegradation and environmental behavior<br />

of biodiesel mixtures in the sea: An initial<br />

study<br />

Demello J A, Carmichael C A, Peacock E E, Nelson R<br />

K, Arey J S, Reddy C M<br />

USA, Switzerland<br />

Toxicology , Marine & Freshwater Biology , Ecology<br />

Biodiesel, a mixture of fatty acid methyl esters<br />

(FAMEs) derived from animal fats or vegetable<br />

oils, is rapidly moving towards the mainstream<br />

as an alternative source of energy. However, the<br />

behavior of biodiesel, or blends of biodiesel with<br />

fossil diesel, in the marine environment have yet<br />

to be fully understood. Hence, we performed a series<br />

of initial laboratory experiments and simple<br />

calculations to evaluate the microbial and environmental<br />

fate of FAMEs. Aerobic seawater microcosms<br />

spiked with biodiesel or mixtures of biodiesel<br />

and fossil diesel revealed that the FAMEs were<br />

degraded at roughly the same rate as n-alkanes,<br />

and more rapidly than other hydrocarbon components.<br />

<strong>The</strong> residues extracted from these different<br />

microcosms became indistinguishable within<br />

weeks. Preliminary results from physical-chemical<br />

calculations suggest that FAMEs in biodiesel<br />

mixtures will not affect the evaporation rates of<br />

spilled petroleum hydrocarbons but may stabilize<br />

oil droplets in the water column and thereby facilitate<br />

transport. (c) 2007 Elsevier Ltd. All rights<br />

reserved.<br />

Marine Pollution Bulletin, 2007, V54, N7, JUL, pp<br />

894-904.<br />

08.1-245<br />

Effect of water-table fluctuation on dissolution<br />

and biodegradation of a multi-component,<br />

light nonaqueous-phase liquid<br />

Dobson R, Schroth M H, Zeyer J<br />

Switzerland<br />

Geochemistry & Geophysics , Water Resources ,<br />

Marine & Freshwater Biology<br />

Light nonaqueous-phase liquids (LNAPLs) such as<br />

gasoline and diesel fuel are among the most common<br />

causes of soil and groundwater contamination.<br />

Dissolution and subsequent advective transport<br />

of LNAPL components can negatively impact<br />

water supplies, while biodegradation is thought<br />

to be an important sink for this class of contaminants.<br />

We present a laboratory investigation of<br />

the effect of a water-table fluctuation on dissolution<br />

and biodegradation of a multi-component<br />

LNAPL (85% hexadecane, 5% toluene, 5% ethylbenzene,<br />

and 5% 2-methylnapthalene on a molar<br />

basis) in a pair of similar model aquifers (80 cm<br />

x 50 cm x 3 cm), one of which was subjected to<br />

a water-table fluctuation. Water-table fluctuation<br />

resulted in LNAPL and air entrapment below the<br />

water table, an increase in the vertical extent of<br />

the LNAPL source zone (by factor 6.7), and an increase<br />

in the volume of water passing through<br />

the source zone (by factor similar to 18). Effluent<br />

concentrations of dissolved LNAPL components<br />

were substantially higher and those of dissolved<br />

nitrate lower in the model aquifer where a fluctuation<br />

had been induced. Thus, water-table fluctuation<br />

led to enhanced biodegradation activity<br />

(28.3 mmol of nitrate consumed compared to 16.3<br />

mmol in the model without fluctuation) as well<br />

as enhanced dissolution of LNAPL components.<br />

Despite the increased biodegradation, fluctuation<br />

led to increased elution of dissolved LNAPL components<br />

from the system (by factors 10-20). Hence,<br />

water-table fluctuations in LNAPL-contaminated<br />

aquifers might be expected to result in increased<br />

exposure of downgradient receptors to LNAPL<br />

components. Accordingly, water-table fluctuations<br />

in contaminated aquifers are probably undesirable<br />

unless the LNAPL is of minimal solubility<br />

or the dissolved-phase plume is not expected to<br />

reach a receptor due to distance or the presence of<br />

some form of containment.<br />

Journal of Contaminant Hydrology, 2007, V94,<br />

N3-4, DEC 7, pp 235-248.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

08.1-246<br />

Ecosystem expansion and contraction dynamics<br />

along a large Alpine alluvial corridor<br />

(Tagliamento River, Northeast Italy)<br />

Doering M, Uehlinger U, Rotach A, Schlaepfer D R,<br />

Tockner K<br />

Switzerland<br />

Hydrology , Ecology , Geomorphology<br />

Riverine floodplains are pulsing ecosystems that<br />

expand and contract with changing flow. In this<br />

study we quantified large-scale expansion and<br />

contraction dynamics of surface waters along<br />

a 41.5 km braided section of the last remaining<br />

semi-natural large Alpine gravel-bed river (Tagliamento<br />

River; NE Italy). To assess surface-subsurface<br />

exchange patterns We measured discharge and<br />

vertical hydraulic gradients at multiple locations<br />

along the corridor. We identified two river sections<br />

delineated by distinct geomorphic knickpoints. In<br />

the upper 29 km, Section I (losing zone), surface<br />

flow decreased on average by 2.5 +/- 0.8 m(3) s(-1)<br />

per river-km. In the downstream 12.5 km, Section<br />

II (gaining zone), surface How increased on average<br />

by 0.3 +/- 0.1 m(3)s(-1) per river-km. <strong>The</strong> losing<br />

zone experienced frequent and extensive drying<br />

and rewetting cycles. <strong>The</strong> length of the dry river<br />

section was measured over a 1.5 year period using<br />

differential GPS. Up to 23 km of Section I fell dry<br />

at the surface. Frequent and irregular flow pulses<br />

led to rapid expansions of the wetted channel at<br />

velocities of up to 3 km h(-1), while the subsequent<br />

contraction velocities were less than 0-5 km h(-1).<br />

Water level was linearly regressed against the total<br />

length of the dry river section (r(2) = 0.74; p<br />

< 0.0001). This relationship, in combination with<br />

a continuous stage record, was used to evaluate<br />

expansion and contraction dynamics over a 4 year<br />

period. Timing, frequency, magnitude (spatial extent)<br />

and duration of expansion and contraction<br />

dynamics reflected the flashy flow regime of the<br />

Tagliamento River, including a high intra- and<br />

inter-annual variability of surface drying and rewetting.<br />

Our study emphasizes that even small<br />

changes in How can cause major increases or<br />

decreases of ecosystem size, thereby creating a<br />

highly dynamic and harsh environment for both<br />

terrestrial and aquatic organisms.<br />

Earth Surface Processes and Landforms, 2007, V32,<br />

N11, OCT 15, pp 1693-1704.<br />

131<br />

08.1-247<br />

Field evidence of a dynamic leakage coefficient<br />

for modelling river- aquifer interactions<br />

Doppler T, Franssen H J H, Kaiser H P, Kuhlman U,<br />

Stauffer F<br />

Switzerland<br />

Modelling , Water Resources , Hydrology<br />

In groundwater flow modelling, the interaction<br />

between rivers and aquifers is usually modelled<br />

with spatially and temporally constant leakage<br />

coefficients. We used conventional model calibration<br />

techniques to investigate the time-varying<br />

river-aquifer interactions in the sandy gravel<br />

aquifer of the upper Limmat valley in Zürich<br />

(Switzerland). <strong>The</strong> aim of the study was to determine<br />

whether the leakage coefficients have to be<br />

treated as time-dependent in order to adequately<br />

model the dynamics of the groundwater flow. A<br />

transient horizontal two-dimensional groundwater<br />

flow model was established together with a<br />

one-dimensional hydraulic model for river flow,<br />

as well as a scheme calculating groundwater recharge<br />

and lateral inflow from meteorological<br />

data and a soil water balance model. <strong>The</strong> groundwater<br />

flow model was calibrated using hydraulic<br />

head data from May and June 2004 and July and<br />

August 2005. <strong>The</strong> verification period covered 13<br />

years using hydraulic head data from 90 piezometers.<br />

<strong>The</strong> comparison of the model results with<br />

the measurements in the verification period revealed<br />

three phenomena concerning river-aquifer<br />

interaction which all showed up as systematic deviations<br />

between model and observations. (1) <strong>The</strong><br />

major flood event in May 1999 had a significant<br />

and persistent influence on the river-aquifer interaction.<br />

In an impounded river section upstream<br />

of a weir, the infiltration of river water was enhanced<br />

by the flooding probably due to erosion<br />

processes. (2) Seasonal river water temperature<br />

fluctuations influenced the infiltration rate, due<br />

to the temperature dependence of hydraulic<br />

conductivity of the river bed. (3) Depending on<br />

geometry and hydraulic characteristics of the riverbanks<br />

the leakage coefficient can be a function<br />

of the river stage. With higher water levels, additional<br />

areas can contribute to the infiltration of<br />

river water. <strong>The</strong>refore, in modelling groundwater<br />

flow with strong river-aquifer interactions, it can<br />

become necessary to consider dynamic leakage<br />

coefficients and to recalibrate periodically.<br />

Journal of Hydrology, 2007, V347, N1-2, DEC 15,<br />

pp 177-187.


132 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

08.1-248<br />

<strong>The</strong> GLOWA Jordan river project: Integrated<br />

research for sustainable water management<br />

Drexler C, Tielbörger K<br />

Switzerland, Germany<br />

Water Resources , Hydrology<br />

Mountain Research and Development, 2007, V27,<br />

N3, AUG, pp 274-275.<br />

08.1-249<br />

Hydropower production and river rehabilitation:<br />

A case study on an alpine river<br />

Fette M, Weber C, Peter A, Wehrli B<br />

Switzerland<br />

Hydrology , Marine & Freshwater Biology , Ecology<br />

Despite the numerous benefits of hydropower production,<br />

this renewable energy source can have serious<br />

negative consequences on the environment.<br />

For example, dams act as barriers for the longitudinal<br />

migration of organisms and transport of<br />

particulate matter. Accelerated siltation processes<br />

in the receiving river reduce the vertical connectivity<br />

between river and groundwater. Hydropeaks,<br />

caused by short-term changes in hydropower<br />

operation, result in a negative impact on both<br />

habitat and organisms, especially during winter<br />

months when natural discharge is low and almost<br />

constant. In this study, we report the current deficits<br />

present in the River Rhone from two different<br />

scientific perspectives - fish ecology and hydrology.<br />

Potential rehabilitation solutions in synergy<br />

with flood protection measures are discussed. We<br />

focus on the effects of hydropeaking in relation to<br />

longitudinal and vertical dimensions and discuss<br />

local river widening as a potential rehabilitation<br />

tool. <strong>The</strong> fish fauna in the Rhone is characterized<br />

by a highly unnatural structure (low diversity,<br />

impaired age distribution). A high correlation between<br />

fish biomass and monotonous morphology<br />

(poor cover availability) was established. Tracer<br />

hydrology provided further details about the reduced<br />

permeability of the riverbank, revealing a<br />

high degree of siltation with K values of about 4.7<br />

x 10 (-6) m s(-1). Improving the hydrologic situation<br />

is therefore essential for the successful rehabilitation<br />

of the Rhone River. To this end, hydropeaks<br />

in the river reaches must be attenuated. This<br />

can be realized by a combination of different hard<br />

technical and soft operational measures such as<br />

retention reservoirs or slower up and down ramping<br />

of turbines.<br />

Environmental Modeling Assessment, 2007, V12,<br />

N4, NOV, pp 257-267.<br />

08.1-250<br />

Effects of alpine hydropower operations on<br />

primary production in a downstream lake<br />

Finger D, Bossard P, Schmid M, Jaun L, Müller B,<br />

Steiner D, Schäffer E, Zeh M, Wüest A<br />

Switzerland<br />

Limnology , Hydrology , Marine & Freshwater Biology<br />

, Ecology , Water Resources<br />

During the past century, the construction of hydropower<br />

dams in the watershed of Lake Brienz<br />

has significantly altered the dynamics of turbidity,<br />

which has important implications for lake<br />

productivity. To assess these effects, we measured<br />

in situ carbon assimilation rates and ambient<br />

light intensities over 18 months. Based on experimental<br />

data, a numerical model was developed<br />

to assess gross primary production under present<br />

light conditions and those under a hypothetical<br />

case without upstream dams. Light conditions<br />

for the hypothetical ‘no-dam’ situation were estimated<br />

from pre-dam Secchi depths and simulated<br />

‘no-dam’ particle concentrations. Current gross<br />

primary production is low (similar to 66 gC m(-2)<br />

yr(-1)), and could increase similar to 44% if the lake<br />

was less turbid. Disregarding nutrient retention<br />

in reservoirs, we estimate gross primary production<br />

would be similar to 35% lower in summer and<br />

similar to 23% higher in winter in the absence of<br />

reservoirs. <strong>The</strong> annual primary production (similar<br />

to 58 gC m(-2)yr(-1)) would decrease similar to<br />

12% compared to the current primary production<br />

with dams. According to model calculations, hydropower<br />

operations have significantly altered<br />

the seasonal dynamics, but have little effect on<br />

annual primary production in Lake Brienz.<br />

Aquatic Sciences, 2007, V69, N2, JUN, pp 240-256.<br />

08.1-251<br />

Comparing effects of oligotrophication and<br />

upstream hydropower dams on plankton and<br />

productivity in perialpine lakes<br />

Finger D, Schmid M, Wüest A<br />

Switzerland<br />

Modelling , Hydrology , Water Resources , Marine<br />

& Freshwater Biology<br />

In recent decades, many perialpine lakes have<br />

been affected by oligotrophication due to efficient<br />

sewage treatment and by altered water turbidity<br />

due to upstream hydropower operations. Such<br />

simultaneous environmental changes often lead<br />

to public debate on the actual causes of observed<br />

productivity reductions. We evaluate the effects<br />

of those two changes by a combined approach<br />

of modeling and data interpretation for a case<br />

study on Lake Brienz (Switzerland), a typical oligotrophic<br />

perialpine lake, located downstream


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

of several hydropower reservoirs. A physical kepsilon<br />

scheme and a biogeochemical advectiondiffusion-reaction<br />

model were implemented and<br />

applied for several hypothetical scenarios with different<br />

nutrient loads and different particle input<br />

dynamics. <strong>The</strong> simulation results are compared to<br />

long-term biotic data collected from 1999 to 2004.<br />

<strong>The</strong> analysis shows that enhanced nutrient supply<br />

increases the nutritious value of algae, stimulating<br />

zooplankton growth, while phytoplankton<br />

growth is limited by stronger top-down control.<br />

Annually integrated productivity is only slightly<br />

influenced by altered turbidity, as phosphorous<br />

limitation prevails. Simulations indicate that the<br />

spring production peak is delayed because of increased<br />

turbidity in winter caused by upstream<br />

hydropower operation. As a consequence, the entire<br />

nutrient cycle is seasonally delayed, creating<br />

an additional stress for zooplankton and fish in<br />

the downstream lake.<br />

Water Resources Research, 2007, V43, N12, DEC<br />

11 ARTN: W12404.<br />

08.1-252<br />

Characterizing water circulation and contaminant<br />

transport in Lake Geneva using bacteriophage<br />

tracer experiments and limnological<br />

methods<br />

Goldscheider N, Haller L, Pote J, Wildi W, Zopfi J<br />

Switzerland<br />

Limnology , Microbiology , Marine & Freshwater<br />

Biology<br />

Multi-tracer tests with three types of marine bacteriophages<br />

(H4/4, H6/1, and H40/1), together with<br />

various limnological methods, including physicochemical<br />

depth profiling, surface drifters, deep<br />

current measurements, and fecal indicator bacteria<br />

analyses, have been applied to characterize<br />

water circulation and pathogen transport in the<br />

Bay of Vidy (Lake Geneva, Switzerland). <strong>The</strong> experimental<br />

program was carried out twice, first in November<br />

2005, when the lake was stratified, and a<br />

second time during holomixis in February 2006.<br />

<strong>The</strong> bacteriophages were injected at three points<br />

at different depths, where contaminated waters<br />

enter the lake, including the outlet pipe of a wastewater<br />

treatment plant, a river, and a stormwater<br />

outlet. <strong>The</strong>reafter, water samples were collected<br />

in the lake at 2 m depth during a 48 h sampling<br />

campaign. <strong>The</strong> results demonstrate that (i) contaminated<br />

river water spreads rapidly in the bay; (ii) a<br />

well- developed thermocline is highly effective in<br />

preventing contamination from the depth to rise<br />

up to the surface; (iii) rapid vertical mixing and<br />

pathogen transport occur under thermally homogeneous<br />

conditions; and (iv) repeated multi-tracer<br />

133<br />

tests with bacteriophages are a powerful technique<br />

to assess water circulation and contaminant transport<br />

in lakes where high dilution occurs.<br />

Environmental Science Technology, 2007, V41,<br />

N15, AUG 1, pp 5252-5258.<br />

08.1-253<br />

Bubble gas-exchange in an artificially aerated<br />

lake traced using noble gases<br />

Holzner C P, Graser N, Kipfer R<br />

Switzerland<br />

Limnology , Geochemistry & Geophysics<br />

Geochimica et Cosmochimica Acta, 2007, V71, N15,<br />

AUG, SS, p A413.<br />

08.1-254<br />

Accumulation of cyanobacterial toxins in<br />

freshwater “seafood” and its consequences for<br />

public health: A review<br />

Ibelings B W, Chorus I<br />

Switzerland, Netherlands, Germany<br />

Marine & Freshwater Biology , Toxicology , Human<br />

& Public Health<br />

This review summarizes and discusses the current<br />

understanding of human exposure to cyanobacterial<br />

toxins in “seafood” collected from<br />

freshwater and coastal areas. <strong>The</strong> review consists<br />

of three parts: (a) the existing literature on concentrations<br />

of cyanobacterial toxins in seafood is<br />

reviewed, and the likelihood of bioaccumulation<br />

discussed; (b) we derive cyanotoxin doses likely<br />

to occur through seafood consumption and propose<br />

guideline values for seafood and compare<br />

these to guidelines for drinking water; and (c) we<br />

discuss means to assess, control or mitigate the<br />

risks of exposure to cyanotoxins through seafood<br />

consumption. This is discussed in the context of<br />

two specific procedures, the food specific HACCPapproach<br />

and the water- specific Water Safety<br />

Plan approach by the WHO. Risks of exposure to<br />

cyanotoxins in food are sometimes underestimated.<br />

Risk assessments should acknowledge this and<br />

investigate the partitioning of exposure between<br />

drinking-water and food, which may vary depending<br />

on local circumstances.<br />

Environmental Pollution, 2007, V150, N1, NOV, pp<br />

177-192.<br />

08.1-255<br />

Effects of upstream hydropower operation<br />

and oligotrophication on the light regime of a<br />

turbid peri-alpine lake<br />

Jaun L, Finger D, Zeh M, Schurter M, Wüest A<br />

Switzerland<br />

Hydrology , Limnology , Marine & Freshwater Biology<br />

, Ecology , Water Resources


134 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

Anthropogenic activities in catchments can alter<br />

the light regimes in downstream natural waters,<br />

affecting light attenuation and the perceived optical<br />

properties of the waters. We analyzed the<br />

effects of upstream hydropower operation and<br />

oligotrophication on light attenuation and reflectance<br />

in Lake Brienz (Switzerland). For this<br />

purpose, we reconstructed its light regime for the<br />

pre-dam condition and for periods of 4-fold increased<br />

primary productivity, based on direct observations<br />

of light and beam attenuation as well<br />

as concentrations of optically active compounds,<br />

especially observed and simulated mineral particle<br />

concentrations. Based on our assessment, light<br />

attenuation before the construction of upstream<br />

dams was double the current value during summer<br />

and nearly half in winter. This result is consistent<br />

with pre-dam measurements of Secchi depths<br />

in the early 1920s. Using a simple optical model, a<br />

significant increase in reflectance since the 1970s<br />

was estimated, assuming a 4-fold decrease of optical<br />

active organic compounds within the lake. As<br />

reflectance is perceived by human eyes as turbidity,<br />

this may explain subjective reports by local<br />

residents of increasing turbidity in recent years.<br />

Aquatic Sciences, 2007, V69, N2, JUN, pp 212-226.<br />

08.1-256<br />

Decadal water mass variations along 20 degrees<br />

W in the Northeastern Atlantic Ocean<br />

Johnson G C, Gruber N<br />

USA, Switzerland<br />

Oceanography<br />

Water mass variations in the northeastern Atlantic<br />

Ocean along 20 degrees W are analyzed with<br />

pentadal resolution over the past 15 years using<br />

data from four repeat occupations of a meridional<br />

hydrographic section running south from Iceland.<br />

<strong>The</strong> section was sampled in 1988, 1993, 1998, and<br />

2003. <strong>The</strong> results are interpreted in the context of<br />

changes in air-sea forcing, ocean circulation, and<br />

water properties associated with the North Atlantic<br />

Oscillation (NAO) . <strong>The</strong> NAO index oscillated around<br />

zero from 1984 to 1988, was strongly positive from<br />

1989 to 1995, after which it shifted to lower positive,<br />

and occasionally negative values from 1996 to 2003.<br />

Previously published studies suggest that after the<br />

1995-1996 shift of the NAO, the subpolar gyre largely<br />

retreated to the northwest in the northeastern Atlantic<br />

Ocean, resulting in an increasingly southeastern<br />

character of local water masses with time. Water<br />

property changes extending from the Subpolar<br />

Mode Water (SPMW) just below the seasonal pycnocline<br />

through the density range shared by Mediterranean<br />

Outflow Water and SubArctic Intermediate<br />

Water (SAIW) along 20 degrees W are consistent<br />

with changes in wind-driven ocean circulation and<br />

air-sea heat flux associated with shifts in the NAO,<br />

especially after accounting for ocean memory. After<br />

periods of lower NAO index the SPMW is warmer,<br />

saltier, and lighter. At these same times, large increases<br />

of apparent oxygen utilization (AOU) and<br />

potential vorticity are found at the SPMW base, consistent<br />

with SPMW ventilation to lighter densities<br />

during lower NAO index periods. Deeper and denser<br />

in the water column, the cold, fresh, and dense<br />

SAIW signature within the permanent pycnocline<br />

that was most strongly present in 1993, near the culmination<br />

of a period of high NAO index, is much<br />

reduced in 1988 and 1998. In 2003, after a prolonged<br />

period of lower NAO index, increasing influence of<br />

warmer, saltier subtropical waters is clear within<br />

the permanent pycnocline. <strong>The</strong> deep penetration of<br />

the changes implies that they are caused primarily<br />

by circulation changes resulting from NAO-associated<br />

wind shifts, but changes in air-sea heat flux could<br />

also have played a role.<br />

Progress in Oceanography, 2007, V73, N3-4, pp<br />

277-295.<br />

08.1-257<br />

Relationships among recent Alpine Cladocera<br />

remains and their environment: Implications<br />

for climate-change studies<br />

Kamenik C, Szeroczynska K, Schmidt R<br />

Switzerland, Poland, Austria<br />

Limnology , Marine & Freshwater Biology , Meteorology<br />

& Atmospheric Sciences , Ecology<br />

Our objective was to assess the potential of Cladocera<br />

from mountain lakes for climate reconstruction.<br />

We related Cladocera from surface sediments<br />

of Alpine lakes (1,502-2,309 m asl) to 29 abiotic environmental<br />

variables using statistical methods. <strong>The</strong><br />

environmental dataset included water chemistry,<br />

lake depth, and bi-hourly water- temperature logs,<br />

which were used to assess mean monthly water<br />

temperatures, dates of freezing and breakup, spring<br />

and autumn mixing. We found 14 different Cladocera<br />

of the families Bosminidae, Daphniidae, and<br />

Chydoridae. Lakes without Cladocera (eight lakes)<br />

were cold and/or ultra-oligotrophic, whereas lakes<br />

with planktonic and littoral Cladocera (19 lakes)<br />

were warmer and/or less oligotrophic. Lakes with<br />

only littoral Cladocera (18 lakes) had intermediate<br />

water temperatures/trophy. <strong>Change</strong>s in Cladocera<br />

assemblages were related to changes in climate,<br />

nutrients, and/or alkalinity. We found a climate<br />

threshold at which Bosminidae disappeared in<br />

95% of the lakes. For climate-change research, we<br />

propose studying Cladocera along transects that<br />

include climatic thresholds.<br />

Hydrobiologia, 2007, V594, DEC, pp 33-46.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

08.1-258<br />

Implementation of a process-based catchment<br />

model in a poorly gauged, highly glacierized<br />

Himalayan headwater<br />

Konz M, Uhlenbrook S, Braun L, Shrestha A, Demuth<br />

S<br />

Switzerland, Netherlands, Germany, Nepal<br />

Modelling , Hydrology<br />

<strong>The</strong> paper presents a catchment modeling approach<br />

for remote glacierized Himalayan catchments.<br />

<strong>The</strong> distributed catchment model TAC<br />

(D), which is widely based on the HBV model, was<br />

further developed for the application in highly<br />

glacierized catchments on a daily timestep and<br />

applied to the Nepalese Himalayan headwater<br />

Langtang Khola (360 km(2)). Low laying reference<br />

stations are taken for temperature extrapolation<br />

applying a second order polynomial function.<br />

Probability based statistical methods enable<br />

bridging data gaps in daily precipitation<br />

time series and the redistribution of cumulated<br />

precipitation sums over the previous days. Snow<br />

and ice melt was calculated in a distributed way<br />

based on the temperature- index method employing<br />

calculated daily potential sunshine durations.<br />

Different melting conditions of snow and ice and<br />

melting of ice under debris layers were considered.<br />

<strong>The</strong> spatial delineation of hydrological response<br />

units was achieved by taking topographic<br />

and physiographic information from maps and<br />

satellite images into account, and enabled to<br />

incorporate process knowledge into the model.<br />

Simulation results demonstrated that the model<br />

is able to simulate daily discharge for a period of<br />

10 years and point glacier mass balances observed<br />

in the research area with an adequate reliability.<br />

<strong>The</strong> simple but robust data pre-processing and<br />

modeling approach enables the determination of<br />

the components of the water balance of a remote,<br />

data scarce catchment with a minimum of input<br />

data.<br />

Hydrology and Earth System Sciences, 2007, V11,<br />

N4, pp 1323-1339.<br />

08.1-259<br />

Effects of impoundment on nutrient availability<br />

and productivity in lakes<br />

Matzinger A, Pieters R, Ashley K I, Lawrence G A,<br />

Wüest A<br />

Switzerland, Canada<br />

Modelling , Limnology , Marine & Freshwater Biology<br />

, Geochemistry & Geophysics<br />

We investigate the hydraulic alteration and the<br />

effect on primary productivity of the Hugh Keenleyside<br />

Dam built at the outlet of the Arrow Lakes<br />

(British Columbia, Canada) in 1967. Three dam-<br />

135<br />

induced hydraulic changes have been identified<br />

as relevant: (1) water level increase, (2) leveling of<br />

the seasonal outflow, and (3) subsurface release of<br />

water from the dam. <strong>The</strong> potential effect of these<br />

alterations on primary productivity were tested<br />

with a numerical model supported by field observations.<br />

Hydraulic modifications can reduce lake<br />

productivity by up to 40%, primarily as a result<br />

of altered flow path and allowing nutrients to<br />

pass through the reservoir without entering the<br />

productive zone near the surface. This productivity<br />

loss is comparable to the reduction caused<br />

by nutrient retention behind dams constructed<br />

upstream of the Arrow Lakes Reservoir. <strong>The</strong> combined<br />

productivity loss from both of these two<br />

mechanisms is significant and may well be responsible<br />

for the dramatic decline of kokanee (Oncorhynchus<br />

nerka) observed in the Arrow Lakes<br />

Reservoir in the 1990s.<br />

Limnology and Oceanography, 2007, V52, N6,<br />

NOV, pp 2629-2640.<br />

08.1-260<br />

Eutrophication: are mayflies (Ephemeroptera)<br />

good bioindicators for ponds?<br />

Menetrey N, Oertli B, Sartori M, Wagner A, Lachavanne<br />

J B<br />

Switzerland<br />

Zoology , Marine & Freshwater Biology , Water<br />

Resources , Biodiversity<br />

Ephemeroptera larvae are recognized worldwide<br />

for their sensitivity to oxygen depletion in running<br />

waters, and are therefore commonly used as<br />

bioindicators in many monitoring programmes.<br />

Mayflies inhabiting lentic waters, like lakes and<br />

ponds, in contrary have been poorly prospected<br />

in biomonitoring. For this purpose, a better understanding<br />

of their distribution in lentic habitats<br />

and of the relations of species presence with<br />

environmental conditions are needed. Within<br />

this framework, 104 ponds were sampled in Switzerland.<br />

<strong>The</strong> Ephemeroptera are found to be an<br />

insect order particularly well represented in the<br />

ponds studied here (93% of the lowland ponds).<br />

Nevertheless, in terms of diversity, they are relatively<br />

poorly represented (mean species number<br />

= 1.9). Two species dominated: Cloeon dipterum<br />

(Baetidae) and Caenis horaria (Caenidae). <strong>The</strong> investigations<br />

contributed to the updating of the<br />

geographical distribution of the species in Switzerland,<br />

as many of the observations appear to<br />

be from new localities. <strong>The</strong> trophic state of ponds<br />

appears here to be important for Ephemeroptera<br />

communities. First, there is a negative relationship<br />

between total phosphorus (TP) concentrations<br />

and species richness. Second, the presence of


136 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

Caenis horaria or Cloeon dipterum is dependent<br />

on the trophic state. Caenis horaria is most closely<br />

associated with low levels of TP concentrations,<br />

while Cloeon dipterum appears to be less sensitive,<br />

and is most frequently found in hypertrophic<br />

conditions. A probable consequence of these relations,<br />

is that Baetidae are always present when<br />

Caenidae are also present. Contrastingly, Baetidae<br />

is observed as the only mayflies family present in<br />

several ponds.<br />

Hydrobiologia, 2008, V597, FEB, pp 125-135.<br />

08.1-261<br />

Inorganic carbon fixation by sulfate-reducing<br />

bacteria in the Black Sea water column<br />

Neretin L N, Abed R M M, Schippers A, Schubert C<br />

J, Kohls K, Kuypers M M M<br />

Germany, Switzerland<br />

Microbiology , Marine & Freshwater Biology , Geochemistry<br />

& Geophysics<br />

<strong>The</strong> Black Sea is the largest anoxic water basin on<br />

Earth and its stratified water column comprises<br />

an upper oxic, middle suboxic and a lower permanently<br />

anoxic, sulfidic zone. <strong>The</strong> abundance<br />

of sulfate- reducing bacteria (SRB) in water samples<br />

was determined by quantifying the copy<br />

number of the dsrA gene coding for the alpha<br />

subunit of the dissimilatory (bi)sulfite reductase<br />

using real-time polymerase chain reaction. <strong>The</strong><br />

dsrA gene was detected throughout the whole<br />

suboxic and anoxic zones. <strong>The</strong> maximum dsrA<br />

copy numbers were 5 x 10(2) and 6.3 x 10(2) copies<br />

ml(-1) at 95 m in the suboxic and at 150 m in<br />

the upper anoxic zone, respectively. <strong>The</strong> proportion<br />

of SRB to total Bacteria was 0.1% in the oxic,<br />

0.8-1.9% in the suboxic and 1.2-4.7% in the anoxic<br />

zone. A phylogenetic analysis of 16S rDNA clones<br />

showed that most clones from the anoxic zone<br />

formed a coherent cluster within the Desulfonema-Desulfosarcina<br />

group. A similar depth profile<br />

as for dsrA copy numbers was obtained for the<br />

concentration of non-isoprenoidal dialkyl glycerol<br />

diethers (DGDs), which are most likely SRBspecific<br />

lipid biomarkers. Three different DGDs<br />

were found to be major components of the total<br />

lipid fractions from the anoxic zone. <strong>The</strong> DGDs<br />

were depleted in C-13 relative to the delta C-13<br />

values of dissolved CO 2 (delta C-13(CO 2)) by 14-19<br />

parts per thousand. <strong>The</strong>ir delta C-13 values (delta<br />

C-13(DGD(II-III))) co-varied with depth showing<br />

the least C-13-depleted values in the top of the<br />

sulfidic, anoxic zone and the most C-13-depleted<br />

values in the deep anoxic waters at 1500 m. This<br />

co-variation provides evidence for CO 2 incorporation<br />

by the DGD(II-III)-producing SRB, while<br />

the 1:2 relationship between delta C-13(CO 2) and<br />

delta C-13(DGD(II-III)) indicates the use of an additional<br />

organic carbon source.<br />

Environmental Microbiology, 2007, V9, N12, DEC,<br />

pp 3019-3024.<br />

08.1-262<br />

Impacts of environmental change on water<br />

resources in the Mt. Kenya region<br />

Notter B, Macmillan L, Viviroli D, Weingartner R,<br />

Liniger H P<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , Water Resources<br />

, Modelling<br />

Water resources are becoming increasingly scarce<br />

in the Mt. Kenya region. Land use and climate<br />

change may pose additional challenges to water<br />

management in the future. In order to assess<br />

the impacts of environmental change, the NRM3<br />

Streamflow Model, a simple, semi- distributed,<br />

grid-based water balance model, is evaluated as<br />

a too(for discharge prediction in six meso-scale<br />

catchments on the western slopes of Mt. Kenya,<br />

and used to analyse the impact of Land use and<br />

climate change scenarios on water resources. <strong>The</strong><br />

calibration and validation results show an acceptable<br />

performance of the NRM3 Streamflow Model<br />

in simulating discharge. Input data represent the<br />

main (imitation. Rainfall patterns in the mountainous<br />

catchments are very heterogeneous and<br />

difficult to capture with the monitoring network.<br />

River water abstractions make up 80-100% of naturalized<br />

dry season discharge, but amounts can<br />

only be approximately estimated. Under the scenarios<br />

of (and use and climate change examined,<br />

the total amount as well as the variability of discharge<br />

wilt increase: Conversion of the forest area<br />

to crop- or grassland wilt increase annual runoff<br />

by 11% or 59%, respectively, by mainly increasing<br />

flood flows and, under cropland, slightly reducing<br />

Low flows. Climate change as projected by the<br />

IPCC Task Group on Scenarios for Impact Assessment<br />

(IPCC-TCGIA, 1999. Guidelines in the use of<br />

data for climate impact and adaptation assessment.<br />

Version 1. Prepared by Carter, T.R., Hulme,<br />

M.., Lal, M., Intergovernmental Panel on Climate<br />

<strong>Change</strong>, Task Group on Scenarios for Climate Impact<br />

Assessment.) will result in an increase of annual<br />

runoff by 26%, with a severe increase in flood<br />

flows, and a reduction of the lowest flows to about<br />

a tenth of the current value.<br />

Journal of Hydrology, 2007, V343, N3-4, SEP 20,<br />

pp 266-278.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

08.1-263<br />

Influence of temperature and high acetate<br />

concentrations on methanogenensis in lake<br />

sediment slurries<br />

Nozhevnikova A N, Nekrasova V, Ammann A,<br />

Zehnder A J B, Wehrli B, Holliger C<br />

Switzerland, Russia<br />

Limnology , Microbiology , Geochemistry & Geophysics<br />

, Marine & Freshwater Biology<br />

Methanogenesis from main methane precursors<br />

H-2/CO 2 and acetate was investigated in a temperature<br />

range of 2-70 degrees C using sediments from<br />

Lake Baldegg, Switzerland. Psychrophilic, psychrotrophic,<br />

mesophilic, and thermophilic methanogenic<br />

microbial communities were enriched<br />

by incubations for 1-3 months of nonamended<br />

sediment slurries at 5, 15, 30, and 50 degrees<br />

C. Isotope experiments with slurries amended<br />

with C-14-labeled bicarbonate and C-14-2-acetate<br />

showed that in the psychrophilic community<br />

(enriched at 5 degrees C), about 95% of methane<br />

originated from acetate, in contrast to the thermophilic<br />

community (50 degrees C) where up to<br />

98% of methane was formed from bicarbonate. In<br />

the mesophilic community (30 degrees C), acetate<br />

was the precursor of about 80% of the methane<br />

produced. When the hydrogen-carbon dioxide<br />

mixture (H-2/CO 2) was used as a substrate, it was<br />

directly converted to methane under thermophilic<br />

conditions (70 and 50 degrees C). Under<br />

mesophilic conditions (30 degrees C), both pathways,<br />

hydrogenotrophic and acetoclastic, were<br />

observed. At low temperatures (5 and 15 degrees<br />

C), H-2/CO 2 was converted into methane by a twostep<br />

process; first acetate was formed, followed by<br />

methane production from acetate. When slurries<br />

were incubated at high partial pressures of H-2/<br />

CO 2, the high concentrations of acetate produced<br />

of more than 20 mM inhibited acetoclastic methanogenesis<br />

at a temperature below 15 degrees C.<br />

However, slow adaptation of the psychrophilic<br />

microbial community to high acetate concentrations<br />

was observed.<br />

Fems Microbiology Ecology, 2007, V62, N3, DEC,<br />

pp 336-344.<br />

08.1-264<br />

Macroinvertebrate assemblages in 25 high alpine<br />

ponds of the <strong>Swiss</strong> National Park (Cirque<br />

of Macun) and relation to environmental<br />

variables<br />

Oertli B, Indermühle N, Angelibert S, Hinden H,<br />

Stoll A<br />

Switzerland<br />

Zoology , Biodiversity , Marine & Freshwater<br />

Biology , Ecology<br />

137<br />

High-altitude freshwater ecosystems and their biocoenosis<br />

are ideal sentinel systems to detect global<br />

change. In particular, pond communities are likely<br />

to be highly responsive to climate warming. For this<br />

reason, the <strong>Swiss</strong> National Park has included ponds<br />

as part of a long-term monitoring programme of<br />

the high-alpine Macun cirque. This cirque covers 3.6<br />

km(2), has a mean altitude of 2,660 m a.s.l., and includes<br />

a hydrographic system composed of a stream<br />

network and more than 35 temporary and permanent<br />

ponds. <strong>The</strong> first two steps in the programme<br />

were to (i) make an inventory of the macroinvertebrates<br />

of the waterbodies in the Macun cirque,<br />

and (ii) relate the assemblages to local or regional<br />

environmental variables. Sampling was conducted<br />

in 25 ponds between 2002 and 2004. <strong>The</strong> number of<br />

taxa characterising the region (Macun cirque) was<br />

low, represented by 47 lentic taxa. None of them<br />

was endemic to the Alps, although several species<br />

were cold stenothermal. Average pond richness<br />

was low (11.3 taxa). Assemblages were dominated<br />

by Chironomidae (Diptera), and Coleoptera and Oligochaeta<br />

were also relatively well represented. Other<br />

groups, which are frequent in lowland ponds,<br />

had particularly poor species richness (Trichoptera,<br />

Heteroptera) or were absent (Gastropoda, Odonata,<br />

Ephemeroptera). Macroinvertebrate assemblages<br />

(composition, richness) were only weakly influenced<br />

by local environmental variables. <strong>The</strong> main<br />

structuring processes were those operating at regional<br />

level and, namely, the connectivity between<br />

ponds, i.e. the presence of a physical connection<br />

(tributary) and/or small geographical distance between<br />

ponds. <strong>The</strong> results suggest that during the<br />

long-term monitoring of the Macun ponds (started<br />

in 2005), two kinds of change will affect macroinvertebrate<br />

assemblages. <strong>The</strong> first change is related<br />

to the natural dynamics, with high local- scale turnover,<br />

involving the metapopulations characterising<br />

the Macun cirque. <strong>The</strong> second change is related to<br />

global warming, leading to higher local and regional<br />

richness through an increase in the number of<br />

colonisation events resulting from the upward shift<br />

of geographical ranges of species. At the same time<br />

the cold stenothermal species from Macun will be<br />

subject to extinction.<br />

Hydrobiologia, 2008, V597, FEB, pp 29-41.<br />

08.1-265<br />

Aquatic macroinvertebrate response along a<br />

gradient of lateral connectivity in river floodplain<br />

channels<br />

Paillex A, Castella E, Carron G<br />

Switzerland<br />

Marine & Freshwater Biology, Ecology, Biodiversity,<br />

Zoology


138 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

Large river floodplains potentially include the<br />

full range of freshwater ecosystems from permanently<br />

flowing channels to temporary pools and<br />

springs. Attempts to restore such complex systems<br />

require tools adapted to assess restoration success.<br />

In an analysis of invertebrate assemblages in the<br />

Rhone River floodplain (France), taxonomic-based<br />

indices (rarefied richness and assemblage composition)<br />

were compared with functional metrics<br />

using trait-based ratios as surrogates of ecosystem<br />

processes. <strong>The</strong>ir ability to respond to a gradient<br />

of hydrological connectivity was assessed in 7<br />

cut-off channels. <strong>The</strong> sampling design included<br />

2 sites/channel (upstream and downstream), 4<br />

randomly chosen sampling points (0.5 x 0.5-m<br />

quadrats) /site, and 2 sampling seasons (spring<br />

and summer). Water physicochemical and habitat<br />

variables were recorded when invertebrates were<br />

sampled. Environmental variables, including water<br />

conductance, (NH 3-N), submerged vegetation<br />

cover, diversity of sediment grain size, and organic<br />

matter content of the sediment, were used to<br />

construct a synthetic variable describing the hydrological<br />

connectivity of each site with the main<br />

river channel. A quadratic regression of rarefied<br />

taxonomic richness and the connectivity gradient<br />

was not quite significant, but assemblage composition<br />

was strongly related to the gradient. Four<br />

of 8 trait-based metrics; were correlated with the<br />

connectivity gradient. Values of metrics that are<br />

surrogates for top-down control of assemblage<br />

structure and habitat stability (based on functional<br />

feeding groups) declined along the gradient<br />

from disconnected sites to more connected sites.<br />

Values of metrics that are surrogates for voltinism<br />

and food supply for water- column-feeding fish increased<br />

with connectivity. Top-down control and<br />

voltinism surrogates suggested a decline in predator-prey<br />

relationships and lower habitat stability,<br />

respectively, in the more connected sites. Assemblage<br />

composition and some of the trait-based<br />

metrics were sensitive to a flood that occurred before<br />

one of the sampling dates. Some of the traitbased<br />

metrics showed potential for explaining<br />

floodplain invertebrate assemblages and for monitoring<br />

postrestoration conditions in floodplain<br />

water bodies. However, the metrics were developed<br />

initially for studies of lotic systems and their<br />

use in heterogeneous floodplain water bodies will<br />

require further investigation, e.g., delineation of<br />

reference conditions for trait-based metrics.<br />

Journal of the North American Benthological Society,<br />

2007, V26, N4, DEC, pp 779-796.<br />

08.1-266<br />

Bipolar gene flow in deep-sea benthic foraminifera<br />

Pawlowski J, Fahrni J, Lecroq B, Longet D, Cornelius<br />

N, Excoffier L, Cedhagen T, Gooday A J<br />

Switzerland, England, Denmark<br />

Biodiversity , Ecology , Marine & Freshwater Biology<br />

Despite its often featureless appearance, the deepocean<br />

floor includes some of the most diverse<br />

habitats on Earth. However, the accurate assessment<br />

of global deep-sea diversity is impeded by<br />

a paucity of data on the geographical ranges of<br />

bottom-dwelling species, particularly at the genetic<br />

level. Here, we present molecular evidence<br />

for exceptionally wide distribution of benthic<br />

foraminifera, which constitute the major part of<br />

deep-sea meiofauna. Our analyses of nuclear ribosomal<br />

RNA genes revealed high genetic similarity<br />

between Arctic and Antarctic populations of three<br />

common deep-sea foraminiferal species (Epistominella<br />

exigua, Cibicides wuellerstorfi and Oridorsalis<br />

umbonatus), separated by distances of up to<br />

17 000 km. Our results contrast with the substantial<br />

level of cryptic diversity usually revealed by<br />

molecular studies, of shallow- water benthic and<br />

planktonic marine organisms. <strong>The</strong> very broad<br />

ranges of the deep-sea foraminifera that we examined<br />

support the hypothesis of global distribution<br />

of small eukaryotes and suggest that deep-sea<br />

biodiversity may be more modest at global scales<br />

than present estimates suggest.<br />

Molecular Ecology, 2007, V16, N19, OCT, pp<br />

4089-4096.<br />

08.1-267<br />

Earlier onset of the spring phytoplankton<br />

bloom in lakes of the temperate zone in a<br />

warmer climate<br />

Peeters F, Straile D, Lorke A, Livingstone D M<br />

Germany, Switzerland<br />

Marine & Freshwater Biology , Meteorology &<br />

Atmospheric Sciences , Oceanography , Biodiversity<br />

Ecology<br />

<strong>The</strong> decoupling of trophic interactions is potentially<br />

one of the most severe consequences of climate<br />

warming. In lakes and oceans the timing<br />

of phytoplankton blooms affects competition<br />

within the plankton community as well as foodweb<br />

interactions with zooplankton and fish. Using<br />

Upper Lake Constance as an example, we present<br />

a model-based analysis that predicts that in<br />

a future warmer climate, the onset of the spring<br />

phytoplankton bloom will occur earlier in the<br />

year than it does at present. This is a result of the<br />

earlier occurrence of the transition from strong<br />

to weak vertical mixing in spring, and of the as-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

sociated earlier onset of stratification. According<br />

to our simulations a shift in the timing of phytoplankton<br />

growth resulting from a consistently<br />

warmer climate will exceed that resulting from a<br />

single unusually warm year. <strong>The</strong> numerical simulations<br />

are complemented by a statistical analysis<br />

of long-term data from Upper Lake Constance<br />

which demonstrates that oligotrophication has a<br />

negligible effect on the timing of phytoplankton<br />

growth in spring and that an early onset of the<br />

spring phytoplankton bloom is associated with<br />

high air temperatures and low wind speeds.<br />

<strong>Global</strong> <strong>Change</strong> Biology, 2007, V13, N9, SEP, pp<br />

1898-1909.<br />

08.1-268<br />

Water level fluctuations and dynamics of amphibious<br />

plants at Lake Constance: Long-term<br />

study and simulation<br />

Peintinger M, Prati D, Winkler E<br />

Germany, Switzerland<br />

Plant Sciences , Modelling , Limnology , Marine &<br />

Freshwater Biology<br />

Inundations of lakeshores are classical examples<br />

of how disturbance can influence community diversity<br />

and composition. As the occurrence and<br />

intensity of flooding are predicted to change dramatically<br />

as a result of climate change, predicting<br />

the consequences of such changes has become a<br />

major task for community ecology. Here we present<br />

abundance data of five species that comprise a<br />

species-poor community of high conservation value<br />

at lakeshores of Lake Constance over 17 years,<br />

during which one of the longest flood periods<br />

and the lowest water levels since 1890 occurred.<br />

We used simple regression models and increasingly<br />

sophisticated Markov chain models plus<br />

non-linear parameter estimation to put down<br />

abundance changes to direct effects of flooding<br />

on population-dynamic parameters and to indirect<br />

effects of flooding through modification of<br />

interspecific competition. We found a negative effect<br />

of flood duration on abundance changes for<br />

the non-specialist species Agrostis stolonifera and<br />

Phalaris arundinacea, but no effect on Carex acuta.<br />

<strong>The</strong> specialist species, Ranunculus reptans but<br />

not Littorella uniflora showed a positive effect of<br />

flooding. Data analysis revealed an unambiguous<br />

competitive hierarchy with the two graminoid<br />

species (C acuta, P. arundinacea) being superior,<br />

and the habitat specialists being most sensitive<br />

to interspecific competition. We used estimated<br />

parameters to project the community dynamics<br />

under different flooding regimes. Long-term projection<br />

showed that the original community is<br />

threatened by two non-specialist species (C acuta<br />

139<br />

and P. arundinacea). Even if this forecast was influenced<br />

by various model limitations, it may indicate<br />

irreversible changes in soil fertility during<br />

the phase of high eutrophication between 1950<br />

and 1980. Our study demonstrated that long-term<br />

abundance releves combined with Markov modelling<br />

and predictive simulations are an important<br />

counterpart to detailed short-term studies. <strong>The</strong><br />

combination of empirical and theoretical methods<br />

elucidates the interaction of biotic and abiotic<br />

factors in community change.<br />

Perspectives in Plant Ecology Evolution and Systematics,<br />

2007, V8, N4, pp 179-196.<br />

08.1-269<br />

Phytoplankton blooms in the Ross Sea, Antarctica:<br />

Interannual variability in magnitude,<br />

temporal patterns, and composition<br />

Peloquin J A, Smith W O Jr<br />

USA, Switzerland<br />

Oceanography , Marine & Freshwater Biology<br />

<strong>The</strong> continental shelf of the Ross Sea, Antarctica,<br />

is a unique region within the Southern Ocean.<br />

Phytoplankton growth is believed to be seasonally<br />

limited, first in austral spring by irradiance, and<br />

then in summer by biologically available iron. It<br />

also is historically known to have taxonomically<br />

distinct regimes: the south-central portion is<br />

dominated by Phaeocystis antarctica and to the<br />

west diatoms are abundant. We measured photochemical<br />

yield to interpret the health of the phytoplankton<br />

assemblage from 2001-2004 and interfaced<br />

these measurements with satellite remote<br />

sensing of pigments. <strong>The</strong> bloom of 2001-2002 was<br />

similar in both temporal and spatial distributions<br />

to the climatological mean of the Ross Sea, with a<br />

peak in biomass being observed in mid-December<br />

within the Ross Sea polynyas; F-v/F-m values averaged<br />

0.43. We found high (0.50-0.65) F-v/F-m for<br />

most of the seasonal phytoplankton bloom for<br />

2002-2003, suggesting that it was not seasonally<br />

iron limited. An unusual, large bloom occurred<br />

during 2003-2004, with an initial bloom of P. antarctica<br />

during austral spring followed by an extensive<br />

diatom bloom in summer that may have<br />

been enhanced by an intrusion of modified circumpolar<br />

deep water. On the basis of an analysis<br />

of the historical SeaWiFS records, accumulation<br />

of phytoplankton biomass in February may occur<br />

approximately every 2-4 years, potentially being<br />

a significant source of carbon on the continental<br />

shelf.<br />

Journal of Geophysical Research Oceans, 2007,<br />

V112, NC8, AUG 23 ARTN: C08013.


140 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

08.1-270<br />

One-year survey of a single Micronesian reef<br />

reveals extraordinarily rich diversity of Symbiodinium<br />

types in soritid foraminifera<br />

Pochon X, Garcia Cuetos L, Baker A C, Castella E,<br />

Pawlowski J<br />

USA, Switzerland<br />

Marine & Freshwater Biology , Biodiversity , Ecology<br />

Recent molecular studies of symbiotic dinoflagellates<br />

(genus Symbiodinium) from a wide array<br />

of invertebrate hosts have revealed exceptional<br />

fine-scale symbiont diversity whose distribution<br />

among hosts, regions and environments exhibits<br />

significant biogeographic, ecological and evolutionary<br />

patterns. Here, similar molecular approaches<br />

using the internal transcribed spacer-2<br />

(ITS-2) region were applied to investigate cryptic<br />

diversity in Symbiodinium inhabiting soritid foraminifera.<br />

Approximately 1,000 soritid specimens<br />

were collected and examined during a 12-month<br />

period over a 40 m depth gradient from a single<br />

reef in Guam, Micronesia. Out of 61 ITS-2 types<br />

distinguished, 46 were novel. Most types found<br />

are specific for soritid hosts, except for three types<br />

(Cl, C15 and C19) that are common in metazoan<br />

hosts. <strong>The</strong> distribution of these symbionts was<br />

compared with the phylotype of their foraminifera<br />

hosts, based on soritid small subunit ribosomal<br />

DNA sequences, and three new phylotypes<br />

of soritid hosts were identified based on these<br />

sequences. Phylogenetic analyses of 645 host-symbiont<br />

pairings revealed that most Symbiodinium<br />

types associated specifically with a particular<br />

foraminiferal host genus or species, and that the<br />

genetic diversity of these symbiont types was positively<br />

correlated with the genetic diversity found<br />

within each of the three host genera. Compared<br />

to previous molecular studies of Symbiodinium<br />

from other locations worldwide, the diversity reported<br />

here is exceptional and suggests that Micronesian<br />

coral reefs are home to a remarkably<br />

large Symbiodinium assemblage.<br />

Coral Reefs, 2007, V26, N4, DEC, pp 867-882.<br />

08.1-271<br />

Continuous measurement of sediment transport<br />

in the Erlenbach stream using piezoelectric<br />

bedload impact sensors<br />

Rickenmann D, Mcardell B W<br />

Switzerland<br />

Hydrology , Geomorphology<br />

We report on bedload transport observations using<br />

piezoelectric bedload impact sensors (PBIS),<br />

an indirect method of estimating the volume of<br />

bedload transport of coarse sediment. <strong>The</strong> PBIS<br />

device registers vibrations produced by bedload<br />

(particle diameter >similar to 20 mm) and records<br />

the signal as a sum of the number of impulses per<br />

time. Sediment transport at the Erlenbacb stream<br />

has been continuously monitored with a PBIS array<br />

starting in 1986. <strong>The</strong> sensor array spans the<br />

width of an entire cross-section and is mounted<br />

Hush with the surface of a check dam immediately<br />

upstream of a sediment retention basin. We<br />

compare PBIS data with long-term sedimentation<br />

records obtained from repeated surveys of<br />

material stored in the sediment retention basin,<br />

with artificial sediment input under controlled<br />

conditions in the field, and also with laboratory<br />

experiments. <strong>The</strong> rate of bedload transport is proportional<br />

to the number of impacts on the sensor<br />

per unit time. <strong>The</strong> reliability of the calibration relationship<br />

increases with the length of the observation<br />

period, e.g. for higher numbers of impacts<br />

and larger bedload volumes. Sediment volumes<br />

for individual flood events estimated with the<br />

PBIS method are in agreement with volumes estimated<br />

using an independent empirical method<br />

based on the effective runoff volume of water, the<br />

peak water discharge, and the critical discharge<br />

for the onset of sediment transport. Copyright (c)<br />

2007 John Wiley & Sons, Ltd.<br />

Earth Surface Processes and Landforms, 2007, V32,<br />

N9, AUG, pp 1362-1378.<br />

08.1-272<br />

Cadmium isotope fractionation in seawater - A<br />

signature of biological activity<br />

Ripperger S, Rehkamper M, Porcelli D, Halliday A N<br />

Switzerland, England<br />

Oceanography , Geochemistry & Geophysics , Marine<br />

& Freshwater Biology<br />

Investigations of cadmium isotope variations in<br />

the oceans may provide new insights into the factors<br />

that control the marine distribution and cycling<br />

of this element. Here we present the results<br />

of Cd isotope and concentration analyses for 22<br />

seawater samples from the Atlantic, Southern, Pacific,<br />

and Arctic Oceans. <strong>The</strong> results reveal, for the<br />

first time, large and well resolved Cd isotope fractionations<br />

in the marine environment. <strong>The</strong> majority<br />

of the seawater samples display an inverse<br />

relationship between dissolved Cd contents and<br />

isotope compositions, which range from epsilon<br />

Cd-114 /110 approximate to +3 +/- 0.5 for Cd-rich<br />

waters (0.8-1.0 nmol/kg) to epsilon Cd-114/110 approximate<br />

to 38 +/- 6 for surface water with a Cd<br />

concentration of only 0.003 nmol/kg (all epsilon<br />

Cd-114/110 data are reported relative to the JMC<br />

Cd Munster standard). This suggests that the Cd<br />

isotope variations reflect kinetic isotope effects<br />

that are generated during closed system uptake


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

of dissolved seawater Cd by phytoplankton. A<br />

few samples do not follow this trend, as they exhibit<br />

extremely low Cd contents (= 900 in depth, despite of Cd concentrations<br />

that display the expected increase along<br />

the global deep-water pathway from the Atlantic<br />

(similar to 0.3 nmol/kg) to the Pacific Ocean (similar<br />

to 0.9 nmol /kg). This indicates that the biomass,<br />

which is remineralized in the deeper ocean,<br />

is also characterized by a very constant Cd isotope<br />

composition. This observation is in accord with<br />

the interpretation that the Cd distribution in<br />

surface waters is primarily governed by Rayleigh<br />

fractionation during near-quantitative uptake of<br />

dissolved seawater Cd.<br />

Earth and Planetary Science Letters, 2007, V261,<br />

N3-4, SEP 30, pp 670-684.<br />

08.1-273<br />

Density-dependent life history differences in<br />

a stream mayfly (Deleatidium) inhabiting permanent<br />

and intermittent stream reaches<br />

Robinson C T, Buser T<br />

Switzerland<br />

Marine & Freshwater Biology , Ecology , Zoology<br />

A life-history response by the mayfly Deleatidium<br />

(Ephemeroptera: Leptophlebiidae) from a permanent-fl<br />

owing and an intermittent- flowing reach<br />

of the Selwyn River, New Zealand, to failing water<br />

conditions was examined using field populations<br />

and laboratory experiments in January 2006.<br />

Field populations had similar densities under<br />

flowing water conditions, but size distributions<br />

were skewed towards larger larvae in the intermittent<br />

reach relative to the permanent reach. Under<br />

field conditions of falling water at the intermittent<br />

reach, more larvae were caught in the drift<br />

during the day and more adults at dusk at the<br />

intermittent than at the permanent reach. A desiccation<br />

study in the laboratory showed that larvae<br />

survived up to 3 days under moist conditions,<br />

whereas larvae died within 3 h under dry conditions.<br />

Another laboratory experiment revealed<br />

that both populations increased emergence under<br />

falling water in the high density treatment<br />

but not in the ambient density treatment. We<br />

conclude that a density increase caused by falling<br />

water cues late instar larvae to hasten emergence,<br />

141<br />

an adaptive trait that may reduce population<br />

mortality from stream drying.<br />

New Zealand Journal of Marine and Freshwater<br />

Research, 2007, V41, N3, SEP, pp 265-271.<br />

08.1-274<br />

Macroinvertebrate assemblages of a high elevation<br />

stream/lake network with an emphasis<br />

on the Chironomidae<br />

Robinson C T, Hieber M, Wenzelides V, Lods Crozet B<br />

Switzerland<br />

Limnology , Marine & Freshwater Biology ,<br />

Hydrology , Zoology<br />

Macroinvertebrate assemblages of inlet and outlet<br />

streams were examined in a high elevation cirque<br />

comprising two basins in the <strong>Swiss</strong> Alps. Average<br />

taxon richness, with chironomids included as a<br />

single taxon, was < 8 at most sites. Chironomids<br />

represented between 26 and 85 % of the individuals<br />

and at least 50 % of the species collected at the<br />

different sites with over 22 chironomid species<br />

identified in total. No differences in the relative<br />

abundance of common macroinvertebrate taxa<br />

were found between inlet and outlet streams,<br />

but composition differed between the north and<br />

south basin of the cirque. <strong>The</strong> north basin was<br />

mostly fed by groundwater and snowmelt, whereas<br />

the south basin was dominated by glacier-melt<br />

from rock glaciers. Chironomids were 26 % more<br />

abundant and had more species in south basin<br />

than north basin streams, whereas the simuliid<br />

Prosimulium latimucro was 24 % more abundant<br />

in north basin streams. Other common taxa, e.g.,<br />

Nemoura sp., Dicranota sp., Crenobia alpina and<br />

Pseudopsilopteryx zimmeri, also showed substantial<br />

differences in abundance between the two<br />

basins. Diamesinae and Orthocladiinae were the<br />

most common chironomid subfamilies collected<br />

with Diamesa zernyilcinerella, Pseudodianiesa<br />

branickii, Pseudodiamesa arctica, Corynoneura<br />

scutellata, and Tvetenia calvescens together representing<br />

on average > 10 % of the assemblage at<br />

most sites. Chironomid abundance typically was<br />

higher in outlets than inlets. An exception was Diamesa<br />

zernyilcinerella, which had greater relative<br />

abundances in inlets (24 %) than outlets (6 %). <strong>The</strong><br />

results suggest that alpine macroinvertebrates,<br />

chironomids in particular, are sensitive to subtle<br />

differences in habitat conditions and may thus<br />

make good sentinels of environmental change to<br />

alpine waters.<br />

Fundamental and Applied Limnology, 2007, V169,<br />

N1, pp 25-36.


142 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

08.1-275<br />

Hydrological heterogeneity of an alpine<br />

stream-lake network in Switzerland<br />

Robinson C T, Matthaei S<br />

Switzerland<br />

Limnology , Water Resources , Hydrology<br />

Water source and lake landscape position can<br />

strongly influence the physico-chemical characteristics<br />

of flowing waters over space and time. We<br />

examined the physico-chemical heterogeneity in<br />

surface waters of an alpine stream-lake network<br />

(>2600 m a.s.l.) in Switzerland. <strong>The</strong> catchment comprises<br />

two basins interspersed with 26 cirque lakes.<br />

<strong>The</strong> larger lakes in each basin are interconnected<br />

by streams that converge in a lowermost lake<br />

with an outlet stream. <strong>The</strong> north basin is primarily<br />

fed by precipitation and groundwater, whereas<br />

the south basin is fed mostly by glacial melt from<br />

rock glaciers. Surface flow of the entire channel<br />

network contracted by similar to 60% in early autumn,<br />

when snowmelt runoff ceased and cold temperatures<br />

reduced glacial outputs, particularly in<br />

the south basin. Average water temperatures were<br />

similar to 4 degrees C cooler in the south basin,<br />

and temperatures increased by about 4-6 degrees C<br />

along the longitudinal gradient within each basin.<br />

Although overall water conductivity was low (300 µg<br />

1(-1) (nitrite + nitrate-nitrogen), whereas particulate<br />

nitrogen was approximately nine times greater in<br />

the north basin (seasonal average: 97 µg 1(-1)) than<br />

in the south basin (seasonal average: 12 µg 1(-1)).<br />

Total inorganic carbon was low (usually


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

hydrological soil information is not available at a<br />

European scale, we reclassified the Soil Geographical<br />

Database of Europe (SGDBE) at 1:1 million in a<br />

hydrological manner by adopting the Hydrology Of<br />

Soil Types (HOST) system developed in the UK. <strong>The</strong><br />

HOST classification describes dominant pathways<br />

of water movement through soil and was related to<br />

the base flow index (BFI) of a catchment (the longterm<br />

proportion of base flow on total stream flow).<br />

In the original UK study, a linear regression of the<br />

coverage of HOST classes in a catchment explained<br />

79% of BFI variability. We found that a hydrological<br />

soil classification can be built based on the information<br />

present in the SGDBE. <strong>The</strong> reclassified SGDBE<br />

and the regression coefficients from the original UK<br />

study were used to predict BFIs for 103 catchments<br />

spread throughout Europe. <strong>The</strong> predicted BFI explained<br />

around 65% of the variability in measured<br />

BFI in catchments in Northern Europe, but the explained<br />

variance decreased from North to South.<br />

We therefore estimated new regression coefficients<br />

from the European discharge data and found that<br />

these were qualitatively similar to the original estimates<br />

from the UK. This suggests little variation<br />

across Europe in the hydrological effect of particular<br />

HOST classes, but decreasing influence of soil<br />

on BFI towards Southern Europe. Our preliminary<br />

study showed that pedological information is useful<br />

for characterising soil hydrology within Europe and<br />

the long-term discharge regime of catchments in<br />

Northern Europe. Based on these results, we draft a<br />

roadmap for a refined hydrological classification of<br />

European soils.<br />

Hydrology and Earth System Sciences, 2007, V11,<br />

N4, pp 1501-1513.<br />

08.1-278<br />

Selecting scenarios to assess exposure of surface<br />

waters to veterinary medicines in Europe<br />

Schneider M K, Stamm C, Fenner K<br />

Switzerland<br />

Water Resources , Agriculture, Soil Sciences<br />

Registering a veterinary medicinal product (VMP) in<br />

the European Union requires assessing its potential<br />

to contaminate surface waters (SW) on a European<br />

scale. VMP are spread to land in manure or excreted<br />

during grazing and may enter SW through runoff,<br />

erosion, or leaching. Since the factors driving these<br />

processes vary largely across Europe, it is necessary<br />

to identify characteristic conditions, so-called scenarios,<br />

un(er which VMP enter SW. <strong>The</strong>se scenarios<br />

may guide the parameterization of mechanistic fate<br />

models to predict environmental concentrations for<br />

environmental risk assessment. A number of such<br />

scenarios for pesticides and VMP have been developed<br />

rather pragmatically. Here, we describe how a<br />

143<br />

geo-referenced European database of driving factors<br />

was used to divide the European environment into<br />

groups with similar conditions for SW contamination<br />

by VMP. Out of these groups, relevant exposure<br />

scenarios in Europe were selected by a simple scoring<br />

system. Comparing these to the existing scenarios<br />

showed that a number of situations are not well<br />

covered. <strong>The</strong> newly identified scenarios are primarily<br />

located in hilly areas of Central Europe and the<br />

Mediterranean, and in Eastern European plains with<br />

a continental climate. We recommend that they are<br />

included in the technical guidelines for higher-tier<br />

assessment of VMP.<br />

Environmental Science Technology, 2007, V41,<br />

N13, JUL 1, pp 4669-4676.<br />

08.1-279<br />

Assessing iron-mediated oxidation of toluene<br />

and reduction of nitroaromatic contaminants<br />

in anoxic environments using compound- specific<br />

isotope analysis<br />

Tobler N B, Hofstetter T B, Schwarzenbach R P<br />

Switzerland<br />

Geochemistry & Geophysics , Microbiology , Marine<br />

& Freshwater Biology<br />

We evaluated compound-specific isotope analysis<br />

(CSIA) as a tool to assess the coupling of microbial<br />

toluene oxidation by Fe(III)- reducing<br />

bacteria and abiotic reduction of nitroaromatic<br />

contaminants by biogenic mineral-bound Fe(II)<br />

species. Examination of the two processes in<br />

isolated systems revealed a reproducible carbon<br />

isotope fractionation for toluene oxidation by<br />

Geobacter metallireducens with a solid Fe(111)<br />

phase as terminal electron acceptor. We found a<br />

carbon isotope enrichment factor, epsilon(C), of<br />

-1.0 +/- 0.1%o, which corresponds to an apparent<br />

kinetic isotope effect (AKIE(C)) of 1.0073 +/- 0.0009<br />

for the oxidative cleavage of a C-H bond. Nitrogen<br />

isotope fractionation of the reduction of nitroaromatic<br />

compounds (NAC) by mineral-bound Fe(11)<br />

species yielded a nitrogen isotope enrichment factor,<br />

EN, of -39.7 +/- 3.4%o for the reduction of an<br />

aromatic NO 2-group (AKIE(N) = 1.0413 +/- 0.0037)<br />

that was constant for variable experimental conditions.<br />

Finally, AKIE values for C and N observed<br />

in coupled experiments, where reactive Fe(11) was<br />

generated through microbial activity, were identical<br />

to those obtained in the isolated experiments.<br />

This study provides new evidence on isotope fractionation<br />

behavior during contaminant transformation<br />

and promotes the use of CSIA for-the elucidation<br />

of complex contaminant transformation<br />

pathways in the environment.<br />

Environmental Science Technology, 2007, V41,<br />

N22, NOV 15, pp 7773-7780.


144 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

08.1-280<br />

Iron-mediated microbial oxidation and abiotic<br />

reduction of organic contaminants under anoxic<br />

conditions<br />

Tobler N B, Hofstetter T B, Straub K L, Fontana D,<br />

Schwarzenbach R P<br />

Switzerland, Austria<br />

Microbiology , Geochemistry & Geophysics , Marine<br />

& Freshwater Biology<br />

In anoxic environments, the oxidation of organic<br />

compounds, such as BTEX fuel components, by<br />

dissimilatory Fe(III) reduction can generate reactive<br />

mineral-bound Fe(II) species, which in turn<br />

are able to reduce other classes of organic and inorganic<br />

groundwater contaminants. In this study,<br />

we designed and evaluated an anaerobic batch reactor<br />

that mimicks iron-reducing conditions to investigate<br />

the factors that favor the coupling of microbial<br />

toluene oxidation and abiotic reduction of<br />

nitroaromatic contaminants . We investigated the<br />

influence of different Fe(III)-bearing minerals and<br />

combinations thereof on the coupling of these two<br />

processes. Results from laboratory model systems<br />

show that complete oxidation of toluene to CO 2<br />

by Geobacter metallireducens in the presence of<br />

Fe(III)-bearing minerals leads to the formation of<br />

mineral-bound Fe(II) species capable of the reduction<br />

of 4-nitroacetophenone. Whereas significant<br />

microbial toluene oxidation was only observed in<br />

the presence of amorphous Fe(III) phases, reduction<br />

of nitroaromatic compounds only proceeded<br />

with Fe(II) species bound to crystalline Fe(III) oxides.<br />

Our results suggest that in anoxic soils and<br />

sediments containing amorphous and crystalline<br />

iron phases simultaneously, coupling of microbial<br />

oxidation and abiotic reduction of organic<br />

compounds may allow for concurrent natural attenuation<br />

of different contaminant classes.<br />

Environmental Science Technology, 2007, V41,<br />

N22, NOV 15, pp 7765-7772.<br />

08.1-281<br />

Probabilistic flood forecasting with a limitedarea<br />

ensemble prediction system: Selected<br />

case studies<br />

Verbunt M, Walser A, Gurtz J, Montani A, Schär C<br />

Switzerland, Italy<br />

Modelling , Hydrology , Meteorology & Atmospheric<br />

Sciences<br />

A high-resolution atmospheric ensemble forecasting<br />

system is coupled to a hydrologic model to<br />

investigate probabilistic runoff forecasts for the<br />

alpine tributaries of the Rhine River basin (34 550<br />

km(2)). Five-day ensemble forecasts consisting of<br />

51 members, generated with the global ensemble<br />

prediction system (EPS) of the European Centre<br />

for Medium-Range Weather Forecasts (ECMWF),<br />

are downscaled with the limited-area model Lokal<br />

Modell (LM). <strong>The</strong> resulting limited-area ensemble<br />

prediction system (LEPS) uses a horizontal grid<br />

spacing of 10 km and provides one-hourly output<br />

for driving the distributed hydrologic model Precipitation-Runoff-Evapotranspiration-Hydrotope<br />

(PREVAH) hydrologic response unit (HRU) with a<br />

resolution of 500 x 500 m(2) and a time step of 1<br />

h. <strong>The</strong> hydrologic model component is calibrated<br />

for the river catchments considered, which are<br />

characterized by highly complex topography, for<br />

the period 1997-98 using surface observations,<br />

and validated for 1999-2002. This study explores<br />

the feasibility of atmospheric ensemble predictions<br />

for runoff forecasting, in comparison with<br />

deterministic atmospheric forcing. Detailed analysis<br />

is presented for two case studies: the spring<br />

1999 flood event affecting central Europe due to<br />

a combination of snowmelt and heavy precipitation,<br />

and the November 2002 flood in the Alpine<br />

Rhine catchment. For both cases, the deterministic<br />

simulations yield forecast failures, while the<br />

coupled atmospheric-hydrologic EPS provides<br />

appropriate probabilistic forecast guidance with<br />

early indications for extreme floods. It is further<br />

shown that probabilistic runoff forecasts using a<br />

subsample of EPS members, selected by a cluster<br />

analysis, properly represent the forecasts using all<br />

51 EPS members, while forecasts from randomly<br />

chosen subsamples reveal a reduced spread compared<br />

to the representative members. Additional<br />

analyses show that the representation of horizontal<br />

advection of precipitation in the atmospheric<br />

model may be crucial for flood forecasts in alpine<br />

catchments.<br />

Journal of Hydrometeorology, 2007, V8, N4, AUG,<br />

pp 897-909.<br />

08.1-282<br />

Where a springhead becomes a springbrook -<br />

a regional zonation of springs<br />

von Fumetti S, Nagel P, Baltes B<br />

Switzerland<br />

Ecology , Marine & Freshwater Biology , Biodiversity<br />

Hydrology , Zoology<br />

Springs are important freshwater habitats that<br />

provide specific abiotic conditions for many species.<br />

<strong>The</strong>se conditions may change very rapidly<br />

downstream. Limnologists tend to treat spring<br />

sources and their adjacent springbrooks as a unity<br />

because of the lack of clear criteria to separate<br />

these sections. In this study, we investigated the<br />

longitudinal distribution of macroinvertebrate<br />

assemblages in ten undisturbed springs in northwestern<br />

Switzerland at three different distances


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

from the source. Using non-metric multidimensional<br />

scaling and analysis of similarities, we detected<br />

significant differences between the macroinvertebrate<br />

assemblages of the investigated<br />

sections in all spring ecosystems, even over short<br />

distances. <strong>The</strong>se results stress the importance of<br />

distinguishing between the sequential habitats in<br />

this upper region of headwaters. Although a complex<br />

of abiotic factors is responsible for the distribution<br />

of macroinvertebrates, we consider temperature<br />

to be of special importance. Based on our<br />

faunistic data, we propose that the rheocrene-like<br />

springs in the Jura Mountains consist of two sections:<br />

the springhead and the springbrook, with<br />

the springhead consisting of the source and the<br />

upper part of the adjacent downstream section.<br />

In accordance with literature and our faunistic<br />

and temperature data, we place the beginning of<br />

the springbrook at approximately 5 m from the<br />

springhead. With this distinction, we justify that<br />

springheads and springbrooks are unique, discrete<br />

ecosystems, and as such must be considered<br />

in conservation legislation.<br />

Fundamental and Applied Limnology, 2007, V169,<br />

N1, pp 37-48.<br />

08.1-283<br />

Nitrate-depleted conditions on the increase in<br />

shallow northern European lakes<br />

Weyhenmeyer G A, Jeppesen E, Adrian R, Arvola<br />

L, Blenckner T, Jankowski T, Jennings E, Noges P,<br />

Noges T, Straile D<br />

Sweden, Denmark, Germany, Finland, Switzerland,<br />

Ireland, Italy, Estonia<br />

Limnology , Geochemistry & Geophysics , Marine &<br />

Freshwater Biology<br />

We determined relative nitrate-nitrogen (NO 3- N)<br />

loss rates in 100 north-mid-European lakes from<br />

late spring to summer by using the exponential<br />

function N-2 5 N-1e(-k)((t)(2) - (t)(2)), where N-1 and<br />

N-2 are NO 3- N concentrations at the beginning<br />

(t(1)) and the end (t (2)) of the time interval, respectively,<br />

and k is the specific NO 3- N loss rate. We<br />

found that k decreased with increasing lake depth.<br />

Adjusting k to the lake depth (k(adj)), we observed<br />

that k(adj) was positively related to spring NO 3-N<br />

concentrations, but this relationship became insignificant<br />

at mean lake depths exceeding 12.5 m.<br />

A relationship between k(adj) and spring NO 3-N<br />

concentrations in lakes shallower than 12.5 m implies<br />

that changes in spring NO 3-N concentrations<br />

influence the NO 3- N loss rate and thereby summer<br />

NO 3- N concentrations. Time series from one<br />

Estonian, one German, and 14 Swedish lakes shallower<br />

than 12.5 m since 1988 revealed that May<br />

to August NO 3- N concentrations have decreased<br />

145<br />

over time everywhere, and the number of time periods<br />

exhibiting a NO 3- N depleted condition, i.e.,<br />

NO3-N levels below 10 µ g L-1, in these lakes has<br />

tripled since 1988. We explained the decreasing<br />

NO 3- N concentrations by a reduction in external<br />

nitrogen loading including atmospheric deposition,<br />

and by changes in climate. <strong>The</strong> observed prolongation<br />

of NO 3- N depleted conditions might be<br />

one possible explanation for the increasing occurrence<br />

of nitrogen- fixing cyanobacteria in a variety<br />

of lake ecosystems.<br />

Limnology and Oceanography, 2007, V52, N4, JUL,<br />

pp 1346-1353.<br />

08.1-284<br />

Differential decline and recovery of haplochromine<br />

trophic groups in the Mwanza Gulf<br />

of Lake Victoria<br />

Witte F, Wanink J H, Kishe Machumu M, Mkumbo<br />

O C, Goudswaard P C, Seehausen O<br />

Netherlands, Tanzania, Switzerland<br />

Marine & Freshwater Biology , Biodiversity , Ecology<br />

Zoology<br />

Lake Victoria had a fish fauna dominated by 500+<br />

species of haplochromine cichlids that made up<br />

more than 80% of the fish mass. <strong>The</strong> five main<br />

trophic groups caught with bottom trawlers in<br />

the sub- littoral areas of the Mwanza Gulf were:<br />

detritivores, zooplanktivores, insectivores, molluscivores<br />

and piscivores. <strong>The</strong> detritivores (13+<br />

species) formed the most important guild, making<br />

up 60-80% of the number of individuals, followed<br />

by the zooplanktivores (12+ species), which<br />

comprised 10-30%. In the 1980s the haplochromines<br />

from the sub-littoral and offshore areas (estimated<br />

at some 200 species) vanished almost completely.<br />

Commercial trawl fishery, the upsurge<br />

of the introduced Nile perch, and an increase of<br />

eutrophication were potential causes of this decline.<br />

In the 1990s, when Nile perch was heavily<br />

fished, a recovery of some haplochromine species<br />

was observed. We studied the decline and partial<br />

recovery of the different haplochromine trophic<br />

groups in the northern part of the Mwanza Gulf.<br />

<strong>The</strong> rate at which the trophic groups declined differed;<br />

the relatively large piscivores, insectivores<br />

and molluscivores were the first to disappear from<br />

the catches. <strong>The</strong> small detritivores and zooplanktivores<br />

declined at lower rates, especially the latter<br />

group. From the beginning of the 1990s a resurgence<br />

of both groups was observed. By 2001,<br />

the zooplanktivores had reached their previous<br />

level of abundance, but their diversity declined<br />

from more than 12 species to only three. Though<br />

four detritivorous species began being regularly<br />

caught again, they constituted only about 15% of


146 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

the number of individuals, while the zooplanktivores<br />

made up more than 80%. <strong>The</strong> patterns of<br />

decline and recovery indicate that, though fishery<br />

played a role locally, predation by Nile perch and<br />

eutrophication were the main factors determining<br />

the fate of the haplochromines. However, it<br />

has so far been impossible to establish the causal<br />

relationship between the two, and the relative<br />

impact of each of these phenomena separately.<br />

<strong>The</strong> potential effects of the changed trophic dominance,<br />

and the importance of the haplochromines<br />

for the ecosystem and a sustainable fishery,<br />

are discussed.<br />

Aquatic Ecosystem Health Management, 2007,<br />

V10, N4, pp 416-433.<br />

08.1-285<br />

Oxygen isotope biogeochemistry of pore water<br />

sulfate in the deep biosphere: Dominance<br />

of isotope exchange reactions with ambient<br />

water during microbial sulfate reduction (ODP<br />

Site 1130)<br />

Wortmann U G, Chernyavsky B, Bernasconi S M,<br />

Brunner B, Böttcher M E, Swart P K<br />

Canada, Switzerland, USA, Germany<br />

Geology , Modelling , Geochemistry & Geophysics ,<br />

Microbiology<br />

Microbially mediated sulfate reduction affects the<br />

isotopic composition of dissolved and solid sulfur<br />

species in marine sediments. Experiments and field<br />

data show that the delta O-18(SO 4) 2- composition is<br />

also modified in the presence of sulfate-reducing microorganisms.<br />

This has been attributed either to a<br />

kinetic isotope effect during the reduction of sulfate<br />

to sulfite, cell-internal exchange reactions between<br />

enzymatically-activated sulfate (APS), and /or sulfite<br />

with cytoplasmic water. <strong>The</strong> isotopic fingerprint of<br />

these processes may be further modified by the cellexternal<br />

reoxidation of sulfide to elemental sulfur,<br />

and the subsequent disproportionation to sulfide<br />

and sulfate or by the oxidation of sulfite to sulfate.<br />

Here we report delta O-18(SO 4) 2- values from interstitial<br />

water samples of ODP Leg 182 (Site 1130) and<br />

provide the mathematical framework to describe<br />

the oxygen isotope fractionation of sulfate during<br />

microbial sulfate reduction. We show that a purely<br />

kinetic model is unable to explain our delta(OSO 4 2-)-<br />

O-18 data, and that the data are well explained by a<br />

model using oxygen isotope exchange reactions. We<br />

propose that the oxygen isotope exchange occurs between<br />

APS and cytoplasmic water, and/or between<br />

sulfite and adenosine monophosphate (AMP) during<br />

APS formation. Model calculations show that cell external<br />

reoxidation of reduced sulfur species would<br />

require up to 3000 mol/m(3) of an oxidant at ODP<br />

Site 1130, which is incompatible with the sediment<br />

geochemical data. In addition, we show that the<br />

volumetric fluxes required to explain the observed<br />

delta O-18(SO 4) 2- data are on average 14 times higher<br />

than the volumetric sulfate reduction rates (SRR)<br />

obtained from inverse modeling of the porewater<br />

data. <strong>The</strong> ratio between the gross sulfate flux into<br />

the microbes and the net sulfate flux through the<br />

microbes is depth invariant, and independent of sulfide<br />

concentrations. This suggests that both fluxes<br />

are controlled by cell density and that cell-specific<br />

sulfate reduction rates remain constant with depth.<br />

Geochimica et Cosmochimica Acta, 2007, V71,<br />

N17, SEP 1, pp 4221-4232.<br />

08.1-286<br />

Virtual water: An unfolding concept in integrated<br />

water resources management<br />

Yang H, Zehnder A<br />

Switzerland<br />

Political Sciences , Economics , Water Resources<br />

In its broadest sense, virtual water refers to the water<br />

required for the production of food commodities. Issues<br />

relating to virtual water have drawn much attention<br />

in scientific communities and the political<br />

sphere since the mid 1990s. This paper provides a<br />

critical review of major research issues and results<br />

in the virtual water literature and pinpoints the remaining<br />

questions and the direction of research in<br />

future virtual water studies. We conclude that virtual<br />

water studies have helped to raise the awareness<br />

of water scarcity and its impact on food security and<br />

to improve the understanding of the role of food<br />

trade in compensating for water deficit. However,<br />

the studies so far have been overwhelmingly concerned<br />

with the international food trade, and many<br />

solely quantified virtual water flows associated with<br />

food trade. <strong>The</strong>re is a general lack of direct policy<br />

relevance to the solutions to water scarcity and food<br />

insecurity, which are often local, regional, and river<br />

basin issues. <strong>The</strong> obscurity in the conceptual basis of<br />

virtual water also entails some confusion. <strong>The</strong> methodologies<br />

and databases of the studies are often<br />

crude, affecting the robustness and reliability of the<br />

results. Looking ahead, future virtual water studies<br />

need to enhance the policy relevance by strengthening<br />

their linkages with national and regional water<br />

resources management. Meanwhile, integrated<br />

approaches taking into consideration the spatial<br />

and temporal variations of blue and green water resources<br />

availability and the complexity of natural,<br />

socioeconomic, and political conditions are necessary<br />

in assessing the trade-offs of the virtual water<br />

strategy in dealing with water scarcity. To this end,<br />

interdisciplinary efforts and quantitative methods<br />

supported by improved data availability are greatly<br />

important.<br />

Water Resources Research, 2007, V43, N12, DEC 5<br />

ARTN: W12301.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

08.1-287<br />

Hydrological modelling of the chaohe basin<br />

in china: Statistical model formulation and<br />

Bayesian inference<br />

Yang J, Reichert P, Abbaspour K C, Yang H<br />

Switzerland<br />

Hydrology , Modelling<br />

Calibration of hydrologic models is very difficult<br />

because of measurement errors in input and response,<br />

errors in model structure, and the large<br />

number of non-identifiable parameters of distributed<br />

models. <strong>The</strong> difficulties even increase in arid<br />

regions with high seasonal variation of precipitation,<br />

where the modelled residuals often exhibit<br />

high heteroscedasticity and autocorrelation. On<br />

the other hand, support of water management by<br />

hydrologic models is important in and regions,<br />

particularly if there is increasing water demand<br />

due to urbanization. <strong>The</strong> use and assessment of<br />

model results for this purpose require a careful<br />

calibration and uncertainty analysis. Extending<br />

earlier work in this field, we developed a procedure<br />

to overcome (i) the problem of non-identifiability<br />

of distributed parameters by introducing<br />

aggregate parameters and using Bayesian inference,<br />

(ii) the problem of heteroscedasticity of errors<br />

by combining a Box-Cox transformation of<br />

results and data with seasonally dependent error<br />

variances, (iii) the problems of autocorrelated errors,<br />

missing data and outlier omission with a<br />

continuous-time autoregressive error model, and<br />

(iv) the problem of the seasonal variation of error<br />

correlations with seasonally dependent characteristic<br />

correlation times. <strong>The</strong> technique was tested<br />

with the calibration of the hydrologic sub-model<br />

of the Soil and Water Assessment Toot (SWAT) in<br />

the Chaohe Basin in North China. <strong>The</strong> results demonstrated<br />

the good performance of this approach<br />

to uncertainty analysis, particularly with respect<br />

to the fulfilment of statistical assumptions of the<br />

error model. A comparison with an independent<br />

error model and with error models that only considered<br />

a subset of the suggested techniques clearly<br />

showed the superiority of the approach based<br />

on all the features (i)-(iv) mentioned above.<br />

Journal of Hydrology, 2007, V340, N3-4, JUL 15,<br />

pp 167-182.<br />

08.1-288<br />

Bayesian uncertainty analysis in distributed<br />

hydrologic modeling: A case study in the Thur<br />

River basin (Switzerland)<br />

Yang J, Reichert P, Abbaspour K C<br />

Switzerland<br />

Modelling , Hydrology , Instruments & Instrumentation<br />

147<br />

Calibration and uncertainty analysis in hydrologic<br />

modeling are affected by measurement errors in<br />

input and response and errors in model structure.<br />

Recently, extending similar approaches in discrete<br />

time, a continuous time autoregressive error<br />

model was proposed for statistical inference and<br />

uncertainty analysis in hydrologic modeling. <strong>The</strong><br />

major advantages over discrete time formulation<br />

are the use of a continuous time error model for<br />

describing continuous processes, the possibility of<br />

accounting for seasonal variations of parameters<br />

in the error model, the easier treatment of missing<br />

data or omitted outliers, and the opportunity<br />

for continuous time predictions. <strong>The</strong> model was<br />

developed for the Chaohe Basin in China and had<br />

some features specific for this semiarid climatic<br />

region (in particular, the seasonal variation of parameters<br />

in the error model in response to seasonal<br />

variation in precipitation). This paper tests and<br />

extends this approach with an application to the<br />

Thur River basin in Switzerland, which is subject<br />

to completely different climatic conditions. This<br />

application corroborates the general applicability<br />

of the approach but also demonstrates the necessity<br />

of accounting for the heavy tails in the distributions<br />

of residuals and innovations. This is done<br />

by replacing the normal distribution of the innovations<br />

by a Student t distribution, the degrees of<br />

freedom of which are adapted to best represent<br />

the shape of the empirical distribution of the innovations.<br />

We conclude that with this extension,<br />

the continuous time autoregressive error model<br />

is applicable and flexible for hydrologic modeling<br />

under different climatic conditions. <strong>The</strong> major<br />

remaining conceptual disadvantage is that this<br />

class of approaches does not lead to a separate<br />

identification of model input and model structural<br />

errors. <strong>The</strong> major practical disadvantage is the<br />

high computational demand characteristic for all<br />

Markov chain Monte Carlo techniques.<br />

Water Resources Research, 2007, V43, N10, OCT 2<br />

ARTN: W10401.<br />

08.1-289<br />

Salinization of groundwater in the Nefzawa<br />

oases region, Tunisia: results of a regionalscale<br />

hydrogeologic approach<br />

Zammouri M, Siegfried T, El Fahem T, Kriaa S,<br />

Kinzelbach W<br />

Tunisia, Switzerland, Germany, Nigeria<br />

Water Resources , Hydrology , Modelling<br />

Groundwater pumped from the semi-confined<br />

Complexe Terminal (CT) aquifer is an important<br />

production factor in irrigated oases agriculture in<br />

southern Tunisia. A rise in the groundwater salinity<br />

has been observed as a consequence of increas-


148 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

ing abstraction from the aquifer during the last<br />

few decades. All sources of contamination were<br />

investigated using hydrochemical data available<br />

from the 1980s. Water samples were taken from<br />

drains and observation wells tapping both the<br />

CT and the phreatic aquifers and analyzed with<br />

regard to chemistry, temperature, isotopes and<br />

other environmental tracers. Local salinization<br />

mechanisms are suggested, i.e. the upwelling of<br />

saline water from the underlying, confined Continental<br />

Intercalaire (CI) aquifer, as well as backflow<br />

of agricultural drainage water. At this stage, the<br />

main salt pan, the Chott el Djerid, is not a contamination<br />

source. A finite difference model was<br />

also developed to simulate groundwater flow and<br />

contaminant transport in the oases. Calibration<br />

for the period 1950-2000 was carried out in order<br />

to adjust geological and chemical system parameters.<br />

<strong>The</strong> simulation of planned extraction projects<br />

predicts a worsening of the present situation.<br />

Maintenance of the present abstraction regime<br />

will not reduce or stop the salinity increase.<br />

Hydrogeology Journal, 2007, V15, N7, NOV, pp<br />

1357-1375.<br />

08.1-290<br />

Extreme heat and runoff extremes in the <strong>Swiss</strong><br />

Alps<br />

Zappa M, Kan C<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , Modelling ,<br />

Cryology / Glaciology , Hydrology<br />

<strong>The</strong> hydrological response of <strong>Swiss</strong> river basins<br />

to the 2003 European summer heatwave was<br />

evaluated by a combined analysis of historical<br />

discharge records and specific applications of distributed<br />

hydrological modeling. In the summer<br />

of 2003, the discharge from headwater streams<br />

of the <strong>Swiss</strong> Central Plateau was only 40%-60% of<br />

the long-term average. For alpine basins runoff<br />

was about 60%-80% of the average. Glacierized basins<br />

showed the opposite behavior. According to<br />

the degree of glacierization, the average summer<br />

runoff was close or even above average. <strong>The</strong> hydrological<br />

model PREVAH was applied for the period<br />

1982-2005. Even if the model was not calibrated for<br />

such extreme meteorological conditions, it was<br />

well able to simulate the hydrological responses<br />

of three basins. <strong>The</strong> aridity index phi describes<br />

feedbacks between hydrological and meteorological<br />

anomalies, and was adopted as an indicator of<br />

hydrological drought. <strong>The</strong> anomalies of phi and<br />

temperature in the summer of 2003 exceeded the<br />

1982-2005 mean by more than 2 standard deviations.<br />

Catchments without glaciers showed negative<br />

correlations between phi and discharge R.<br />

In basins with about 15% glacierization, phi and<br />

R were not correlated. River basins with higher<br />

glacier percentages showed a positive correlation<br />

between phi and R. Icemelt was positively correlated<br />

with phi and reduced the variability of discharge<br />

with larger amounts of meltwater. Runoff<br />

generation from the non-glaciated sub-areas was<br />

limited by high evapotranspiration and reduced<br />

precipitation. <strong>The</strong> 2003 summer heatwave could<br />

be a precursor to similar events in the near future.<br />

Hydrological models and further data analysis<br />

will allow the identification of the most sensitive<br />

regions where heatwaves may become a recurrent<br />

natural hazard with large environmental, social<br />

and economical impacts.<br />

Natural Hazards and Earth System Sciences, 2007,<br />

V7, N3, pp 375-389.<br />

08.1-291<br />

Insights into the management of sea turtle<br />

internesting area through satellite telemetry<br />

Zbinden J A, Aebischer A, Margaritoulis D, Arlettaz<br />

R<br />

Switzerland, Greece<br />

Zoology , Marine & Freshwater Biology , Ecology ,<br />

Biodiversity<br />

Female sea turtles typically lay several clutches<br />

during each nesting season and rest in the time<br />

between laying clutches (the internesting period)<br />

in the waters off the nesting beach. Adequate protection<br />

of turtles in the internesting area requires<br />

knowledge on their spatial behaviour and was so<br />

far hampered by methodological limitations. Satellite<br />

telemetry data of exceptionally high quality<br />

allowed us to scrutinize internesting area use of<br />

four logger-head sea turtles nesting in the Bay of<br />

Laganas (Zakynthos, Greece). We assessed the efficacy<br />

of two zones of a marine reserve with distinct<br />

levels of protection (boats are excluded from one<br />

zone). Most of the obtained locations of three of the<br />

four turtles were within the bay, a result consistent<br />

with a strategy to minimize energy expenditure.<br />

T Turtles showed no obvious preference for the<br />

highly protected area of the bay. <strong>The</strong> availability<br />

of warmer water in the less protected area may be<br />

more crucial than avoidance of boat disturbance.<br />

Biological Conservation, 2007, V137, N1, JUN, pp<br />

157-162.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Energy Balance<br />

1.6 Energy Balance<br />

08.1-292<br />

Impact of ice supersaturated regions and thin<br />

cirrus on radiation in the midlatitudes<br />

Fusina F, Spichtinger P, Lohmann U<br />

Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences ,<br />

Cryology / Glaciology<br />

(1) In this study we investigate the radiative impact<br />

of ice supersaturated regions (ISSRs, i.e., cloud<br />

free air masses in the upper troposphere that are<br />

supersaturated with respect to ice) and thin cirrus.<br />

For this purpose we use corrected radiosonde<br />

data obtained from routine measurements over<br />

the meteorological observatory in Lindenberg,<br />

Germany. <strong>The</strong> radiative effect of the measured ice<br />

supersaturation is determined. By constructing<br />

an idealized profile from the measurement data<br />

the radiative properties of ISSRs and thin cirrus<br />

containing ice supersaturation were studied. <strong>The</strong><br />

impact of ISSRs on the surface forcing is negligible<br />

but locally, within the vertical profile, changes<br />

in the heating rates up to 1 K d (-1) for typical values<br />

of 130% relative humidity with respect to ice<br />

compared to the saturated profiles are found. This<br />

is also important for the local dynamics within<br />

the supersaturated layers. <strong>The</strong> outgoing longwave<br />

radiation due to the enhanced water vapor content<br />

inside ISSRs decreases up to 0.8 W m(-2). <strong>The</strong><br />

radiative impact of thin cirrus is much stronger.<br />

Thin cirrus influence the surface budget, the top<br />

of the atmosphere radiation and the vertical profile<br />

of the heating rates. <strong>Change</strong>s in the outgoing<br />

longwave radiation and in the reflected shortwave<br />

flux at top of the atmosphere up to 64 W m(-2) and<br />

79 W m(-2), respectively, are possible. <strong>Change</strong>s in<br />

the surface flux (downward) up to 89 W m(-2) are<br />

found. <strong>The</strong> maximal heating rate differences between<br />

thin cirrus and ISSR amount to 15 K d(-1).<br />

<strong>The</strong> radiative impact of thin cirrus clouds depends<br />

strongly on cloud ice content and the size<br />

of the ice crystals. Additionally, the radiative impact<br />

of cirrus formed by parameterizations not allowing<br />

ice supersaturations in large-scale models<br />

is estimated. <strong>The</strong> errors due to artificially formed<br />

cirrus are quite large; differences up to 3 K d(-1) in<br />

the vertical heating profiles and up to 38 and 40<br />

W m(-2) in the outgoing longwave radiation and<br />

the surface flux, respectively, are found. Thus we<br />

recommend using physically based parameterizations<br />

in GCMs which allow ice supersaturation.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND24, DEC 15 ARTN: D24514.<br />

149<br />

08.1-293<br />

Year-round observation of longwave radiative<br />

flux divergence in Greenland<br />

Hoch S W, Calanca P, Philipona R, Ohmura A<br />

Switzerland<br />

Modelling , Meteorology & Atmospheric Sciences<br />

Longwave radiative flux divergence within the lowest<br />

50 m of the atmospheric boundary layer was<br />

observed during the Eidgenossische Technische<br />

Hochschule (ETH) Greenland Summit experiment.<br />

<strong>The</strong> dataset collected at 72 degrees 35’N, 38 degrees<br />

30’W, 3203 m MSL is based on longwave radiation<br />

measurements at 2 and 48 m that are corrected for<br />

the influence of the supporting tower structure.<br />

<strong>The</strong> observations cover all seasons and reveal the<br />

magnitude of longwave radiative flux divergence<br />

and its incoming and outgoing component under<br />

stable and unstable conditions. Longwave radiative<br />

flux divergence during winter corresponds to<br />

a radiative cooling of -10 K day(-1), but values of -30<br />

K day(-1) can persist for several days. During summer,<br />

the mean cooling effect of longwave radiative<br />

flux divergence is small (-2 K day(-1)) but exhibits a<br />

strong diurnal cycle. With values ranging from -35<br />

K day(-1) around midnight to 15 K day(-1) at noon,<br />

the heating rate due to longwave radiative flux divergence<br />

is of the same order of magnitude as the<br />

observed temperature tendency. However, temperature<br />

tendency and longwave radiative flux divergence<br />

are out of phase, with temperature tendency<br />

leading the longwave radiative flux divergence by 3<br />

h. <strong>The</strong> vertical variation of the outgoing longwave<br />

flux usually dominates the net longwave flux divergence,<br />

showing a strong divergence at nighttime<br />

and a strong convergence during the day. <strong>The</strong> divergence<br />

of the incoming longwave flux plays a secondary<br />

role, showing a slight counteracting effect.<br />

Fog is frequently observed during summer nights.<br />

Under such conditions, a divergence of both incoming<br />

and outgoing fluxes leads to the strongest radiative<br />

cooling rates that are observed. Considering all<br />

data, a correlation between longwave radiative flux<br />

divergence and the temperature difference across<br />

the 2-48-m layer is found.<br />

Journal of Applied Meteorology and Climatology,<br />

2007, V46, N9, SEP, pp 1469-1479.<br />

08.1-294<br />

Long-term changes in the cosmic ray intensity<br />

at Earth, 1428-2005<br />

Mccracken K G, Beer J<br />

USA, Switzerland<br />

Meteorology & Atmospheric Sciences<br />

(1) <strong>The</strong> instrumental cosmic ray data recorded in<br />

the interval 1933-1965 by S. E. Forbush and H. V.<br />

Neher and cosmogenic 10 Be data are merged with


150 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Energy Balance<br />

the neutron monitor data since 1951 to study the<br />

long- and short-term variations in the galactic cosmic<br />

radiation intensity for the interval 1428-2005.<br />

It is shown that the ionization chamber data<br />

published by S. E. Forbush were deliberately detrended<br />

to remove long- term changes. <strong>The</strong> highaltitude<br />

ionization chambers used by H. V. Neher<br />

during this interval were well calibrated and their<br />

data exhibit a substantial decrease between 1933<br />

and 1954 that is consistent with the long- term<br />

trends in the cosmogenic 10 Be data. Using the<br />

specific yield functions appropriate to neutron<br />

monitors, ionization chambers, and 10 Be, the<br />

nonlinear relationships between these data types<br />

are determined. It is shown that the nonlinearities<br />

are large and will introduce serious errors if<br />

ignored. An intercalibrated record (the “pseudo-<br />

Climax neutron monitor record’’) is developed for<br />

the interval 1428-2005. It is used to study several<br />

features of the long- term periodicities in the cosmic<br />

radiation, after discussion of residual effects<br />

due to meteorological effects, and the production<br />

of 10 Be by solar cosmic rays. It is shown that (1)<br />

the average intensity in the neutron monitor energy<br />

range for the interval 1954-1996 is similar to<br />

16% less than the average for the period 1428-1944<br />

and that it shows a consistency and depth of<br />

modulation that had not occurred in the previous<br />

580 years. (2) <strong>The</strong> residual cosmic ray modulation<br />

was low throughout the Gleissberg cycle<br />

1540-1645, considerably higher for the next two<br />

Gleissberg Cycles, and highest of all since 1944. (3)<br />

<strong>The</strong> cosmogenic data imply that solar activity was<br />

anomalously low throughout the whole interval<br />

1428-1715, the amplitude of the solar activity during<br />

the Gleissberg cycle 1540-1645 being similar to<br />

50% of that during the following two Gleissberg<br />

cycles and similar to 25% of that in the post-1954<br />

era. (4) It is proposed that the steadily increasing<br />

cosmic ray modulation since 1428 constitutes a<br />

quarter cycle of the previously identified 2300 year<br />

periodicity in the cosmogenic data. (5) <strong>The</strong> cosmic<br />

ray intensity decreased in two steps between 1889<br />

and 1901 and 1944 and 1954, in broad agreement<br />

with the two-step increase in heliomagnetic field<br />

strength determined by Schrijver et al. (2002). It<br />

is proposed that the “pseudo-Climax neutron record’’<br />

will be of benefit in the normalization of<br />

other cosmogenic records to the neutron monitor<br />

record starting in 1951.<br />

Journal of Geophysical Research Space Physics,<br />

2007, V112, NA10, OCT 5 ARTN: A10101.<br />

08.1-295<br />

Modelling the ground heat flux of an urban<br />

area using remote sensing data<br />

Rigo G, Parlow E<br />

Switzerland<br />

Urban Studies , Remote Sensing , Modelling , Meteorology<br />

& Atmospheric Sciences<br />

During the Basel Urban Boundary Layer Experiment<br />

(BUBBLE) conducted in 2002, micrometeorological<br />

in-situ data were collected for different<br />

sites using a variety of instruments. This provides<br />

a unique data set for urban climate studies. Nevertheless,<br />

the spatial distribution of energy and<br />

heat fluxes can only be taken into account with<br />

remote sensing methods or numerical models.<br />

<strong>The</strong>refore, multiple satellite images from different<br />

platforms (NOAA-AVHRR, MODIS and LAND-<br />

SAT ETM+) were acquired, processed and analysed.<br />

In addition, a high resolution digital elevation<br />

model (DEM) and a 1 m resolution digital surface<br />

model (DSM) of a large part of the city of Basel<br />

was utilized. This paper focuses on the calculation<br />

and modelling of the ground (or storage) heat<br />

flux density using remotely sensed data combined<br />

with in-situ measurements using three different<br />

approaches. First, an empirical regression function<br />

was generated to estimate the storage heat<br />

flux from NDVI values second approach used the<br />

Objective Hysteresis Model (OHM) which is often<br />

used for in-situ measurements. <strong>The</strong> last method<br />

used information of the geometric parameters of<br />

urban street canyons, computed from the high<br />

resolution digital urban surface model. Modelled<br />

and measured data are found to be in agreement<br />

within +/- 30 Wm(-2) and result in a coefficient of<br />

determination (R-2) of 0.95.<br />

<strong>The</strong>oretical and Applied Climatology, 2007, V90,<br />

N3-4, NOV, pp 185-199.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Coupled Systems and Cycles<br />

1.7 Coupled Systems and Cycles<br />

08.1-296<br />

An Earth-system perspective of the global<br />

nitrogen cycle<br />

Gruber N, Galloway J N<br />

Switzerland, USA<br />

Ecology , Meteorology & Atmospheric Sciences ,<br />

Oceanography , Geochemistry & Geophysics<br />

With humans having an increasing impact on the<br />

planet, the interactions between the nitrogen cycle,<br />

the carbon cycle and climate are expected to<br />

become an increasingly important determinant<br />

of the Earth system.<br />

Nature, 2008, V451, N7176, JAN 17, pp 293-296.<br />

08.1-297<br />

Comparison of quantification methods to measure<br />

fire-derived (black /elemental) carbon in<br />

soils and sediments using reference materials<br />

from soil, water, sediment and the atmosphere<br />

Hammes K, Schmidt M W I, Smernik R J, Currie L<br />

A, Ball W P, Nguyen T H, Louchouarn P, Houel S,<br />

Gustafsson O, Elmquist M, Cornelissen G, Skjemstad<br />

J O, Masiello C A, Song J, Peng P, Mitra S,<br />

Dunn J C, Hatcher P G, Hockaday W C, Smith<br />

Dwight M, Hartkopf Fröder C, Böhmer A, Lueer B,<br />

Huebert B J, Amelung W, Brodowski S, Huang L,<br />

Zhang W, Gschwend P M, Flores C D X, Largeau C,<br />

Rouzaud J N, Rumpel C, Guggenberger G, Kaiser<br />

K, Rodionov A, Gonzalez Vila F J, Gonzalez Perez J<br />

A, de La Rosa J M, Manning D A C, Lopez Capel E,<br />

Ding L<br />

Switzerland, Germany, USA, Sweden, Spain, Canada,<br />

France, England, Peoples R China, Australia<br />

Agriculture, Soil Sciences , Geology , Geochemistry<br />

& Geophysics , Meteorology & Atmospheric<br />

Sciences<br />

Black carbon (BC), the product of incomplete<br />

combustion of fossil fuels and biomass (called elemental<br />

carbon (EC) in atmospheric sciences), was<br />

quantified in 12 different materials by 17 laboratories<br />

from different disciplines, using seven different<br />

methods. <strong>The</strong> materials were divided into<br />

three classes: (1) potentially interfering materials,<br />

(2) laboratory-produced BC-rich materials, and (3)<br />

BC-containing environmental matrices (from soil,<br />

water, sediment, and atmosphere). This is the first<br />

comprehensive intercomparison of this type (multimethod,<br />

multilab, and multisample) , focusing<br />

mainly on methods used for soil and sediment<br />

BC studies. Results for the potentially interfering<br />

materials (which by definition contained no firederived<br />

organic carbon) highlighted situations<br />

where individual methods may overestimate BC<br />

concentrations. Results for the BC-rich materials<br />

(one soot and two chars) showed that some of the<br />

methods identified most of the carbon in all three<br />

151<br />

materials as BC, whereas other methods identified<br />

only soot carbon as BC. <strong>The</strong> different methods<br />

also gave widely different BC contents for the environmental<br />

matrices. However, these variations<br />

could be understood in the light of the findings<br />

for the other two groups of materials, i.e., that<br />

some methods incorrectly identify non-BC carbon<br />

as BC, and that the detection efficiency of each<br />

technique varies across the BC continuum. We<br />

found that atmospheric BC quantification methods<br />

are not ideal for soil and sediment studies as<br />

in their methodology these incorporate the definition<br />

of BC as light-absorbing material irrespective<br />

of its origin, leading to biases when applied to<br />

terrestrial and sedimentary materials. This study<br />

shows that any attempt to merge data generated<br />

via different methods must consider the different,<br />

operationally defined analytical windows of<br />

the BC continuum detected by each technique,<br />

as well as the limitations and potential biases of<br />

each technique. A major goal of this ring trial was<br />

to provide a basis on which to choose between the<br />

different BC quantification methods in soil and<br />

sediment studies. In this paper we summarize the<br />

advantages and disadvantages of each method. In<br />

future studies, we strongly recommend the evaluation<br />

of all methods analyzing for BC in soils and<br />

sediments against the set of BC reference materials<br />

analyzed here.<br />

<strong>Global</strong> Biogeochemical Cycles, 2007, V21, N3, AUG<br />

31 ARTN: GB3016.<br />

08.1-298<br />

Analysis of seasonal terrestrial water storage<br />

variations in regional climate simulations over<br />

Europe<br />

Hirschi M, Seneviratne S I, Hagemann S, Schär C<br />

Germany, Switzerland<br />

Modelling , Agriculture, Soil Sciences , Hydrology ,<br />

Meteorology & Atmospheric Sciences<br />

Land-surface processes play a major role in the<br />

climate system, and their validation is crucial to<br />

improve current climate models. Here we investigate<br />

the seasonal evolution of terrestrial water<br />

storage (TWS) (includes all water stored on land)<br />

in an ensemble of 30-year- long climate simulations<br />

from the PRUDENCE archive (9 regional and<br />

2 global models), representing current and future<br />

climatic conditions. For validation purposes we<br />

employ a recently published basin-scale waterbalance<br />

(BSWB) data set of diagnosed monthly<br />

TWS variations, where the term variations refers<br />

to monthly changes in TWS. <strong>The</strong> analysis is conducted<br />

in five large-scale European domains composed<br />

of major river basins. This analysis shows<br />

that the climatology of most models lies within


152 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Coupled Systems and Cycles<br />

the interannual variability of the BSWB data set<br />

in the investigated regions, but the different models<br />

sometimes display considerable discrepancies<br />

in the seasonal evolution of TWS. In particular,<br />

we find that all models suffer from a considerable<br />

underestimation of interannual TWS variability.<br />

<strong>The</strong> deviations of the individual models from the<br />

BSWB data set can be linked to biases in the hydrological<br />

fluxes (i.e., precipitation, runoff, evapotranspiration).<br />

<strong>The</strong> simulated future changes for<br />

the Intergovernmental Panel on Climate <strong>Change</strong><br />

(IPCC) A2 scenario suggest an enhancement of the<br />

seasonal cycle of TWS, with drier soils in summer.<br />

Mainly in the Central European domain, several<br />

models show a reduction of the year-to-year variability<br />

of summer TWS variations, indicating an<br />

exhaustion of the models’ soil water reservoirs by<br />

the end of summer under future climatic conditions.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND22, NOV 30 ARTN: D22109.<br />

08.1-299<br />

Evaluation of AMIP II global climate model<br />

simulations of the land surface water budget<br />

and its components over the GEWEX-CEOP<br />

regions<br />

Irannejad P, Henderson Sellers A<br />

Iran, Australia, Switzerland<br />

Meteorology & Atmospheric Sciences , Modelling ,<br />

Hydrology<br />

<strong>The</strong> land surface water balance components simulated<br />

by 20 atmospheric global circulation models<br />

(AGCMs) participating in phase II of the Atmospheric<br />

Model Intercomparison Project (AMIP II)<br />

are analyzed globally and over seven <strong>Global</strong> Energy<br />

and Water Cycle Experiment Coordinated<br />

Enhanced Observing Period basins. In contrast to<br />

the conclusions from analysis of AMIP I, the results<br />

presented here suggest that the group average<br />

of available AGCMs does not outperform all<br />

individual AGCMs in simulating the surface water<br />

balance components. Analysis shows that the<br />

available reanalysis products are not appropriate<br />

for evaluation of AGCMs’ simulated land surface<br />

water components. <strong>The</strong> worst simulation of the<br />

surface water budget is in the Murray-Darling, the<br />

most arid basin, where all the reanalyses and seven<br />

of the AGCMs produce a negative surface water<br />

budget, with evaporation alone exceeding precipitation<br />

and soil moisture decreasing over the<br />

whole AMIP II period in this basin. <strong>The</strong> spatiotemporal<br />

correlation coefficients between observed<br />

and AGCM- simulated runoff are smaller than<br />

those for precipitation. In almost all basins (except<br />

for the two most arid basins), the spatiotem-<br />

poral variations of the AGCMs’ simulated evaporation<br />

are more coherent and agree better with<br />

observations, compared to those of simulated precipitation.<br />

This suggests that differences among<br />

the AGCMs’ surface water budget predictions are<br />

not solely due to model- generated precipitation<br />

differences. Specifically, it is shown that different<br />

land surface parameterization schemes partition<br />

precipitation between evaporation and runoff differently<br />

and that this, in addition to the predicted<br />

differences in atmospheric forcings, is responsible<br />

for different predictions of basin-scale water budgets.<br />

<strong>The</strong> authors conclude that the selection of<br />

a land surface scheme for an atmospheric model<br />

has significant impacts on the predicted continental<br />

and basin-scale surface hydrology.<br />

Journal of Hydrometeorology, 2007, V8, N3, JUN,<br />

pp 304-326.<br />

08.1-300<br />

Comprehensive comparison of gap-filling techniques<br />

for eddy covariance net carbon fluxes<br />

Moffat A M, Papale D, Reichstein M, Hollinger D<br />

Y, Richardson A D, Barr A G, Beckstein C, Braswell<br />

B H, Churkina G, Desai A R, Falge E, Gove J H,<br />

Heimann M, Hui D, Jarvis A J, Kattge J, Noormets<br />

Asko, Stauch V J<br />

Germany, Italy, USA, Canada, England, Switzerland<br />

Modelling , Forestry , Plant Sciences , Agriculture,<br />

Soil Sciences<br />

We review 15 techniques for estimating missing<br />

values of net ecosystem CO 2 exchange (NEE) in<br />

eddy covariance time series and evaluate their<br />

performance for different artificial gap scenarios<br />

based on a set of 10 benchmark datasets from six<br />

forested sites in Europe. <strong>The</strong> goal of gap filling is<br />

the reproduction of the NEE time series and hence<br />

this present work focuses on estimating missing<br />

NEE values, not on editing or the removal of suspect<br />

values in these time series due to systematic<br />

errors in the measurements (e.g., nighttime flux,<br />

advection). <strong>The</strong> gap filling was examined by generating<br />

50 secondary datasets with artificial gaps<br />

(ranging in length from single half- hours to 12<br />

consecutive days) for each benchmark dataset and<br />

evaluating the performance with a variety of statistical<br />

metrics. <strong>The</strong> performance of the gap filling<br />

varied among sites and depended on the level of aggregation<br />

(native half-hourly time step versus daily),<br />

long gaps were more difficult to fill than short<br />

gaps, and differences among the techniques were<br />

more pronounced during the day than at night.<br />

<strong>The</strong> non-linear regression techniques (NLRs), the<br />

look-up table (LUT), marginal distribution sampling<br />

(MDS), and the semiparametric model (SPM)<br />

generally showed good overall performance. <strong>The</strong>


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Coupled Systems and Cycles<br />

artificial neural network based techniques (ANNs)<br />

were generally, if only slightly, superior to the other<br />

techniques. <strong>The</strong> simple interpolation technique<br />

of mean diurnal variation (MDV) showed a moderate<br />

but consistent performance. Several sophisticated<br />

techniques, the dual unscented Kalman filter<br />

(UKF), the multiple imputation method (MIM),<br />

the terrestrial biosphere model (BETHY), but also<br />

one of the ANNs and one of the NLRs showed high<br />

biases which resulted in a low reliability of the<br />

annual sums, indicating that additional development<br />

might be needed. An uncertainty analysis<br />

comparing the estimated random error in the 10<br />

benchmark datasets with the artificial gap residuals<br />

suggested that the techniques are already at or<br />

very close to the noise limit of the measurements.<br />

Based on the techniques and site data examined<br />

here, the effect of gap filling on the annual sums<br />

of NEE is modest, with most techniques falling<br />

within a range of +/- 25 g C m(-2) year(-1.)<br />

Agricultural and Forest Meteorology, 2007, V147,<br />

N3-4, DEC 10, pp 209-232.<br />

08.1-301<br />

Impact of circulation on export production,<br />

dissolved organic matter, and dissolved oxygen<br />

in the ocean: Results from Phase II of the<br />

Ocean Carbon-cycle Model Intercomparison<br />

Project (OCMIP-2)<br />

Najjar R G, Jin X, Louanchi F, Aumont O, Caldeira K,<br />

Doney S C, Dutay J C, Follows M, Gruber N, Joos F,<br />

Lindsay K, Maier Reimer E, Matear R J, Matsumoto<br />

K, Monfray P, Mouchet A, Orr J C, Plattner G K,<br />

Sarmiento J L, Schlitzer R, Slater R D, Weirig M F,<br />

Yamanaka Y, Yool A<br />

USA, France, Switzerland, Algeria, Germany, Australia,<br />

Belgium, Japan, England<br />

Modelling , Oceanography , Geochemistry & Geophysics<br />

Results are presented of export production, dissolved<br />

organic matter (DOM) and dissolved oxygen<br />

simulated by 12 global ocean models participating<br />

in the second phase of the Ocean Carbon-cycle<br />

Model Intercomparison Project. A common, simple<br />

biogeochemical model is utilized in different<br />

coarse-resolution ocean circulation models. <strong>The</strong><br />

model mean (+/- 1 sigma) downward flux of organic<br />

matter across 75 m depth is 17 +/- 6 Pg C yr(-1).<br />

Model means of globally averaged particle export,<br />

the fraction of total export in dissolved form, surface<br />

semilabile dissolved organic carbon (DOC),<br />

and seasonal net outgassing (SNO) of oxygen are<br />

in good agreement with observation- based estimates,<br />

but particle export and surface DOC are<br />

153<br />

too high in the tropics. <strong>The</strong>re is a high sensitivity<br />

of the results to circulation, as evidenced by (1)<br />

the correlation of surface DOC and export with<br />

circulation metrics, including chlorofluorocarbon<br />

inventory and deep-ocean radiocarbon, (2) very<br />

large intermodel differences in Southern Ocean<br />

export, and (3) greater export production, fraction<br />

of export as DOM, and SNO in models with<br />

explicit mixed layer physics. However, deep-ocean<br />

oxygen, which varies widely among the models, is<br />

poorly correlated with other model indices. Crossmodel<br />

means of several biogeochemical metrics<br />

show better agreement with observation-based<br />

estimates when restricted to those models that<br />

best simulate deep-ocean radiocarbon. Overall,<br />

the results emphasize the importance of physical<br />

processes in marine biogeochemical modeling<br />

and suggest that the development of circulation<br />

models can be accelerated by evaluating them<br />

with marine biogeochemical metrics.<br />

<strong>Global</strong> Biogeochemical Cycles, 2007, V21, N3, AUG<br />

8 ARTN: GB3007.<br />

08.1-302<br />

Experimental assessment of N 2O background<br />

fluxes in grassland systems<br />

Neftel A, Flechard C, Ammann C, Conen F, Emmenegger<br />

L, Zeyer K<br />

Switzerland<br />

Agriculture, Soil Sciences , Meteorology & Atmospheric<br />

Sciences<br />

In the absence of, or between, fertilization events<br />

in agricultural systems, soils are generally assumed<br />

to emit N 2O at a small rate, often described<br />

as the ‘background’ flux. In contrast, net uptake of<br />

N 2O by soil has been observed in many field studies,<br />

but has not gained much attention. Observations<br />

of net uptake of N 2O form a large fraction<br />

(about half) of all individual flux measurements<br />

in a long- term time series at our temperate fertilized<br />

grassland site. Individual uptake fluxes from<br />

chamber measurements are often not statistically<br />

significant but mean values integrated over longer<br />

time periods from days to weeks do show a clear<br />

uptake. An analysis of semi- continuous chamber<br />

flux data in conjunction with continuous measurements<br />

of the N 2O concentration in the soil profile<br />

and eddy covariance measurements suggests that<br />

gross production and gross consumption of N 2O<br />

are of the same order, and as consequence only a<br />

minor fraction of N 2O molecules produced in the<br />

soil reaches the atmosphere.<br />

Tellus Series B Chemical and Physical Meteorology,<br />

2007, V59, N3, JUL, pp 470-482.


154 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Coupled Systems and Cycles<br />

08.1-303<br />

Effects of increased soil water availability on<br />

grassland ecosystem carbon dioxide fluxes<br />

Risch A C, Frank D A<br />

USA, Switzerland<br />

Agriculture, Soil Sciences , Ecology , Plant Sciences<br />

<strong>The</strong>re is considerable interest in how ecosystems<br />

will respond to changes in precipitation. Alterations<br />

in rain and snowfall are expected to influence<br />

the spatio-temporal patterns of plant and soil<br />

processes that are controlled by soil moisture, and<br />

potentially, the amount of carbon (C) exchanged<br />

between the atmosphere and ecosystems. Because<br />

grasslands cover over one third of the terrestrial<br />

landscape, understanding controls on grassland<br />

C processes will be important to forecast how<br />

changes in precipitation regimes will influence<br />

the global C cycle. In this study we examined how<br />

irrigation affects carbon dioxide (CO 2) fluxes in<br />

five widely variable grasslands of Yellowstone National<br />

Park during a year of approximately average<br />

growing season precipitation. We irrigated plots<br />

every 2 weeks with 25% of the monthly 30-year average<br />

of precipitation resulting in plots receiving<br />

approximately 150% of the usual growing season<br />

water in the form of rain and supplemented irrigation.<br />

Ecosystem CO 2 fluxes were measured with<br />

a closed chamber-system once a month from May-<br />

September on irrigated and unirrigated plots in<br />

each grassland. Soil moisture was closely associated<br />

with CO 2 fluxes and shoot biomass, and was<br />

between 1.6% and 11.5% higher at the irrigated<br />

plots (values from wettest to driest grassland) during<br />

times of measurements. When examining the<br />

effect of irrigation throughout the growing season<br />

(May-September) across sites, we found that<br />

water additions increased ecosystem CO 2 fluxes<br />

at the two driest and the wettest sites, suggesting<br />

that these sites were water-limited during the<br />

climatically average precipitation conditions of<br />

the 2005 growing season. In contrast, no consistent<br />

responses to irrigation were detected at the<br />

two sites with intermediate soil moisture. Thus,<br />

the ecosystem CO 2 fluxes at those sites were not<br />

water-limited, when considering their responses<br />

to supplemental water throughout the whole season.<br />

In contrast, when we explored how the effect<br />

of irrigation varied temporally, we found that irrigation<br />

increased ecosystem CO 2 fluxes at all the<br />

sites late in the growing season (September). <strong>The</strong><br />

spatial differences in the response of ecosystem<br />

CO 2 fluxes to irrigation likely can be explained<br />

by site specific differences in soil and vegetation<br />

properties. <strong>The</strong> temporal effects likely were due to<br />

delayed plant senescence that promoted plant and<br />

soil activity later into the year. Our results suggest<br />

that in Yellowstone National Park, above-normal<br />

amounts of soil moisture will only stimulate CO 2<br />

fluxes across a portion of the ecosystem. Thus, depending<br />

on the topographic location, grassland<br />

CO 2 fluxes can be water-limited or not. Such information<br />

is important to accurately predict how<br />

changes in precipitation/soil moisture will affect<br />

CO 2 dynamics and how they may feed back to the<br />

global C cycle.<br />

Biogeochemistry, 2007, V86, N1, OCT, pp 91-103.<br />

08.1-304<br />

Chemistry, transport and dry deposition of<br />

trace gases in the boundary layer over the<br />

tropical Atlantic Ocean and the Guyanas during<br />

the GABRIEL field campaign<br />

Stickler A, Fischer H, Bozem H, Gurk C, Schiller C,<br />

Martinez Harder M, Kubistin D, Harder H, Williams<br />

J, Eerdekens G, Yassaa N, Ganzeveld L, Sander R,<br />

Lelieveld J<br />

Switzerland, Germany, Canada<br />

Meteorology & Atmospheric Sciences , Modelling<br />

We present a comparison of different Lagrangian<br />

and chemical box model calculations with measurement<br />

data obtained during the GABRIEL campaign<br />

over the tropical Atlantic Ocean and the<br />

Amazon rainforest in the Guyanas, October 2005.<br />

Lagrangian modelling of boundary layer (BL) air<br />

constrained by measurements is used to derive a<br />

horizontal gradient (approximate to 5.6 pmol/mol<br />

km(-1)) of CO from the ocean to the rainforest (east<br />

to west). This is significantly smaller than that derived<br />

from the measurements (16-48 pmol/mol<br />

km(-1)), indicating that photochemical production<br />

from organic precursors alone cannot explain the<br />

observed strong gradient. It appears that HCHO<br />

is overestimated by the Lagrangian and chemical<br />

box models, which include dry deposition but not<br />

exchange with the free troposphere (FT). <strong>The</strong> relatively<br />

short lifetime of HCHO implies substantial<br />

BL-FT exchange. <strong>The</strong> mixing-in of FT air affected<br />

by African and South American biomass burning<br />

at an estimated rate of 0.12 h(-1) increases the CO<br />

and decreases the HCHO mixing ratios, improving<br />

agreement with measurements. A mean deposition<br />

velocity of 1.35 cm/s for H 2O 2 over the ocean<br />

as well as over the rainforest is deduced assuming<br />

BL-FT exchange adequate to the results for CO.<br />

<strong>The</strong> measured increase of the organic peroxides<br />

from the ocean to the rainforest (approximate to<br />

0.66 nmol/mol d(-1)) is significantly overestimated<br />

by the Lagrangian model, even when using high<br />

values for the deposition velocity and the entrainment<br />

rate. Our results point at either heterogeneous<br />

loss of organic peroxides and/or their radical<br />

precursors, underestimated photodissociation


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Coupled Systems and Cycles<br />

or missing reaction paths of peroxy radicals not<br />

forming peroxides in isoprene chemistry. We<br />

calculate a mean integrated daytime net ozone<br />

production (NOP) in the BL of (0.2+/-5.9) nmol/mol<br />

(ocean) and (2.4+ /-2.1) nmol/mol (rainforest). <strong>The</strong><br />

NOP strongly correlates with NO and has a positive<br />

tendency in the boundary layer over the rainforest.<br />

Atmospheric Chemistry and Physics, 2007, V7,<br />

N14, pp 3933-3956.<br />

08.1-305<br />

Challenges in quantifying biosphere-atmosphere<br />

exchange of nitrogen species<br />

Sutton M A, Nemitz E, Erisman J W, Beier C, Butterbach<br />

Bahl K, Cellier P, de Vries W, Cotrufo F,<br />

Skiba U, Di Marco C, Jones S, Laville P, Soussana J F,<br />

Loubet B, Twigg M, Famulari D, Whitehead J, Gallagher<br />

M W, Neftel A, Flechard C R, Herrmann B,<br />

Calanca P, Schjoerring J K, Daemmgen U, Horvath<br />

L, Tang Y S, Emmett B A, Tietema A, Penuelas J,<br />

Kesik M, Brueggemann N, Pilegaard K, Vesala T,<br />

Campbell C L, Olesen J E, Dragosits U, <strong>The</strong>obald M<br />

R, Levy P, Mobbs D C, Milne R, Viovy N, Vuichard N,<br />

Smith J U, Smith P, Bergamaschi P, Fowler D, Reis S<br />

Scotland, Netherlands, Denmark, Germany, France,<br />

Italy, England, Switzerland, Hungary, Wales, Spain,<br />

Finland<br />

Modelling , Meteorology & Atmospheric Sciences ,<br />

Agriculture, Soil Sciences<br />

Recent research in nitrogen exchange with the<br />

atmosphere has separated research communities<br />

according to N form. <strong>The</strong> integrated perspective<br />

needed to quantify the net effect of N on greenhouse-gas<br />

balance is being addressed by the Nitro-<br />

Europe Integrated Project (NEU). Recent advances<br />

have depended on improved methodologies, while<br />

ongoing challenges include gas-aerosol interactions,<br />

organic nitrogen and N-2 fluxes. <strong>The</strong> NEU<br />

strategy applies a 3-tier Flux Network together<br />

with a Manipulation Network of global-change experiments,<br />

linked by common protocols to facilitate<br />

model application. Substantial progress has<br />

been made in modelling N fluxes, especially for<br />

N 2O, NO and bi-directional NH 3 exchange. Landscape<br />

analysis represents an emerging challenge<br />

to address the spatial interactions between farms,<br />

fields, ecosystems, catchments and air dispersion<br />

/deposition. European up-scaling of N fluxes is<br />

highly uncertain and a key priority is for better<br />

data on agricultural practices. Finally, attention is<br />

needed to develop N flux verification procedures<br />

to assess compliance with international protocols.<br />

Environmental Pollution, 2007, V150, N1, NOV, pp<br />

125-139.<br />

155<br />

08.1-306<br />

Sensitivity of carbon cycling in the European<br />

Alps to changes of climate and land cover<br />

Zierl B, Bugmann H<br />

Switzerland<br />

Forestry , Modelling , Plant Sciences , Ecology<br />

Assessments of the impacts of global change on<br />

carbon stocks in mountain regions have received<br />

little attention to date, in spite of the considerable<br />

role of these areas for the global carbon cycle. We<br />

used the regional hydro-ecological simulation system<br />

RHESSys in five case study catchments from<br />

different climatic zones in the European Alps to<br />

investigate the behavior of the carbon cycle under<br />

changing climatic and land cover conditions derived<br />

from the SRES scenarios of the IPCC. <strong>The</strong> focus<br />

of this study was on analyzing the differences<br />

in carbon cycling across various climatic zones of<br />

the Alps, and to explore the differences between<br />

the impacts of various SRES scenarios (A1FI, A2, B1,<br />

B2), and between several global circulation models<br />

(GCMs, i.e., HadCM3, CGCM2, CSIRO2, PCM).<br />

<strong>The</strong> simulation results indicate that the warming<br />

trend generally enhances carbon sequestration in<br />

these catchments over the first half of the twenty-<br />

first century, particularly in forests just below<br />

treeline. <strong>The</strong>reafter, forests at low elevations<br />

increasingly release carbon as a consequence of<br />

the changed balance between growth and respiration<br />

processes, resulting in a net carbon source at<br />

the catchment scale. Land cover changes have a<br />

strong modifying effect on these climate- induced<br />

patterns. While the simulated temporal pattern of<br />

carbon cycling is qualitatively similar across the<br />

five catchments, quantitative differences exist due<br />

to the regional differences of the climate and land<br />

cover scenarios, with land cover exerting a stronger<br />

influence. <strong>The</strong> differences in the simulations<br />

with scenarios derived from several GCMs under<br />

one SRES scenario are of the same magnitude as<br />

the differences between various SRES scenarios<br />

derived from one single GCM, suggesting that the<br />

uncertainty in climate model projections needs to<br />

be narrowed before accurate impact assessments<br />

under the various SRES scenarios can be made at<br />

the local to regional scale. We conclude that the<br />

carbon balance of the European Alps is likely to<br />

shift strongly in the future, driven mainly by land<br />

cover changes, but also by changes of the climate.<br />

We recommend that assessments of carbon cycling<br />

at regional to continental scales should make sure<br />

to adequately include sub-regional differences of<br />

changes in climate and land cover, particularly in<br />

areas with a complex topography.<br />

Climatic <strong>Change</strong>, 2007, V85, N1-2, NOV, pp<br />

195-212.


156 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

2 Past <strong>Global</strong> <strong>Change</strong>s<br />

08.1-307<br />

Pleistocene ice and paleo-strain rates at Taylor<br />

Glacier, Antarctica<br />

Aciego S M, Cuffey K M, Kavanaugh J L, Morse D L,<br />

Severinghaus J P<br />

USA, Switzerland, Canada<br />

Cryology / Glaciology , Paleontology<br />

Ice exposed in ablation zones of ice sheets can<br />

be a valuable source of samples for paleoclimate<br />

studies and information about long-term ice dynamics.<br />

We report a 28-km long stable isotope<br />

sampling transect along a flowline on lower Taylor<br />

Glacier, Antarctica, and show that ice from<br />

the last glacial period is exposed here over tens<br />

of kilometers. Gas isotope analyses on a small<br />

number of samples confirm our age hypothesis.<br />

<strong>The</strong>se chronostratigraphic data contain information<br />

about past ice dynamics and in particular<br />

should be sensitive to the longitudinal strain rate<br />

on the north flank of Taylor Dome, averaged over<br />

millennia. <strong>The</strong> imprint of climatic changes on ice<br />

dynamics may be discernible in these data.<br />

Quaternary Research, 2007, V68, N3, NOV, pp<br />

303-313.<br />

08.1-308<br />

Sequencing events across the Permian-Triassic<br />

boundary, Guryul Ravine (Kashmir, India)<br />

Algeo T J, Hannigan R, Rowe H, Brookfield M, Baud<br />

A, Krystyn L, Ellwood B B<br />

USA, Canada, Switzerland<br />

Geochemistry & Geophysics , Geology ,<br />

Paleontology<br />

<strong>The</strong> Permian-Triassic boundary (PTB) section at<br />

Guryul Ravine (Kashmir, India) comprises a ><br />

100-m-thick, apparently conformable succession<br />

of mixed siliciclastic-carbonate sediments deposited<br />

in a deep-shelf or ramp setting. This section,<br />

although long important in debates concerning<br />

placement of the PTB, has not previously been the<br />

focus of an integrated chemostratigraphic study.<br />

In the present study, samples from a 20-m-thick<br />

interval straddling the PTB were analyzed for major-<br />

and trace-element concentrations, TOC-TIC,<br />

REEs, and organic delta C-13-delta N-15 to investigate<br />

contemporaneous environmental changes.<br />

<strong>The</strong> Guryul Ravine section exhibits a sequence of<br />

discrete events that provide potentially important<br />

information about the character and cause(s) of<br />

the PTB. Two transient negative C-isotopic excursions<br />

within the upper changxingensis zone predate<br />

the Late Permian event horizon (LPEH, i.e., the<br />

global mass extinction event) by similar to 200-400<br />

kyr and are associated with the onset of a major<br />

eustatic rise and with secondary extinction peaks.<br />

<strong>The</strong>se excursions may record minor environmen-<br />

tal disturbances prior to the main end-Permian<br />

crisis, supporting an intrinsic mechanism such<br />

as volcanism and climate change rather than an<br />

extrinsic mechanism such as a bolide impact. <strong>The</strong><br />

onset of a large (similar to -4.0 to -4.5%), sustained<br />

negative C-isotope shift marks the LPEH, which is<br />

located at the Zewan-Khunamub formation contact<br />

similar to 260 cm below the biostratigraphically<br />

defined PTB, <strong>The</strong> Guryul Ravine section<br />

exhibits a stepwise extinction pattern, with the<br />

largest peak between the LPEH and PTB and a secondary<br />

peak just above the PTB, a pattern similar<br />

to that observed in the Meishan D GSSP.<br />

Palaeogeography Palaeoclimatology Palaeoecology,<br />

2007, V252, N1-2, AUG 20, pp 328-346.<br />

08.1-309<br />

Sub-orbital sea-level change in early MIS 5e:<br />

New evidence from the Gulf of Corinth, Greece<br />

Andrews J E, Portman C, Rowe P J, Leeder M R,<br />

Kramers J D<br />

England, Switzerland<br />

Paleontology , Geochemistry & Geophysics ,<br />

Geology<br />

New evidence from uplifted marine isotope stage<br />

(MIS) 5e carbonate deposits in the Gulf of Corinth<br />

demonstrate two rapid, sub-orbitally forced, sealevel<br />

oscillations in the early part of MIS 5e. Microbial<br />

bioherms with inter-grown marine coralline<br />

algae are interpreted as early highstand deposits.<br />

Presence of thin vadose flowstone (speleothem)<br />

coating inter-bioherm surfaces mark a short-lived<br />

regression of > 10 m, followed by sea-level recovery<br />

and re- establishment of the highstand, marked<br />

by coralline algae coating inter-bioherm cavity<br />

surfaces. <strong>The</strong>se marine algae are then coated<br />

by a younger vadose flowstone, thick enough to<br />

provide an uncontaminated U/Th date of 134.8 +/-<br />

12.0 ka. <strong>The</strong> dated flowstone is itself encrusted by<br />

marine fauna and the entire sequence overlain by<br />

highstand marine sediments and marine aragonite<br />

cements dated to 114-118 ka, part of the sustained<br />

MIS 5e highstand. <strong>The</strong> age of the younger<br />

flowstone demonstrates that the early highstand<br />

occurred before 134.8 +/- 2.0 ka, and uplift arguments<br />

suggest that the bioherms are unlikely to<br />

be older than similar to 136 ka. <strong>The</strong>se data are<br />

consistent with the notion that most of termination<br />

II (TII) sea- level rise had occurred before<br />

135 ka; indeed they suggest sea-level at this time<br />

reached about 2-4 (+/- 4) m below present sea-level,<br />

6-18 (+/- 4) m higher than previous estimates. This<br />

early highstand was itself punctuated by a rapid<br />

sea-level oscillation of > 10 m (as yet undated),<br />

and this oscillation, supported by new TII sealevel<br />

data from the Red Sea (Siddall, M., Bard, E.,


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

Rohling, E.J., Hemleben, C., 2006, Sea-level reversal<br />

during termination 11, Geology, 34, 817-820.),<br />

probably occurred in about 1000 yr. <strong>The</strong> flowstone<br />

dated at 134.8 2.0 ka is interpreted to record the<br />

early part of the ‘Aladdin’s Cave’ regressive event<br />

from Papua New Guinea, although in Greece only<br />

the first 16 m of the event is recorded. <strong>The</strong> new<br />

data presented here support a recently published<br />

Red Sea TII sea- level curve: they also highlight minor<br />

discrepancies in the absolute dating of these<br />

early MIS 5e sea-level events worldwide.<br />

Earth and Planetary Science Letters, 2007, V259,<br />

N3-4, JUL 30, pp 457-468.<br />

08.1-310<br />

Age and significance of former low-altitude<br />

corrie glaciers on Hoy, Orkney Islands<br />

Ballantyne C K, Hall A M, Phillips W, Binnie S,<br />

Kubik P W<br />

Scotland, USA, Switzerland<br />

Geomorphology , Paleontology , Cryology /<br />

Glaciology<br />

Geomorphological mapping provides evidence for<br />

two former low-level corrie glaciers on Hoy, both<br />

defined by end moraines. Five Be-10 exposure ages<br />

obtained from sandstone boulders on moraine<br />

crests fall within the range 12.4 +/- 1.5 ka to 10.4<br />

+/- 1.7 ka (weighted mean 11.7 +/- 0.6 ka), confirming<br />

that these glaciers developed during the Loch<br />

Lomond (Younger Dryas) Stade (LLS) of 12.9-11.5<br />

cal. ka BP, and demonstrate the feasibility of using<br />

this approach to establish the age of LLS glacier<br />

limits. <strong>The</strong> equilibrium line altitude (ELA) of<br />

one of the glaciers (99 m) is the lowest recorded<br />

for any LLS glacier, and the area-weighted mean<br />

ELA for both (141 m) is consistent with a general<br />

northward ELA decrease along the west coast<br />

of Britain. <strong>The</strong> size of moraines fronting these<br />

small (


158 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

cover) and pollen for the Juniperus site (eg, r(2) =<br />

0.76 between crown cover and arboreal pollen, AP)<br />

and the Picea site (r(2) = 0.85), whereas the linkage<br />

is weaker at the Juglans site (r(2) = 0.35) and<br />

in mixed forests (r(2) = 0.32). <strong>The</strong> results of the<br />

surface samples of moss polsters are compared<br />

and discussed with surface samples of lake sediments<br />

that were taken at the same locations. We<br />

use vegetational maps from around the lakes to<br />

discuss the link between vegetation and pollen at<br />

extra-local scales (800 m around the sites). <strong>The</strong>se<br />

comparisons show that AP underestimates the effective<br />

tree cover around all sites, with in extreme<br />

cases densely forested areas corresponding to AP<br />

values as low as < 60; 30%. We explain this finding<br />

by the prevalent background pollen load that<br />

derives from the dry lowland and slope steppes<br />

(Artemisia, Chenopodiaceae, Poaceae). Our investigation<br />

may improve the reconstruction of<br />

Quaternary vegetation and climate history of<br />

these forest belts in Kyrgyzstan (Central Asia) on<br />

the basis of fossil pollen assemblages from mire<br />

and lake sediments. It provides new insights into<br />

the pollen reflection of forest isles (eg, on humid<br />

slopes or mountain tops) that are surrounded by<br />

continental steppes; a vegetational situation that<br />

may be used as an analogue for the conditions<br />

during the full glacial in Eurasia and Northern<br />

America.<br />

Holocene, 2007, V17, N5, JUL, pp 599-611.<br />

08.1-313<br />

Surface-exposure ages of Front Range moraines<br />

that may have formed during the<br />

Younger Dryas, 8.2cal ka, and Little Ice Age<br />

events<br />

Benson L, Madole R, Kubik P W, Mcdonald R<br />

USA, Switzerland<br />

Paleontology , Meteorology & Atmospheric Sciences<br />

, Geomorphology , Geology<br />

Surface-exposure (Be-10) ages have been obtained<br />

on boulders from three post-Pinedale end-moraine<br />

complexes in the Front Range, Colorado. Boulder<br />

rounding appears related to the cirque-to-moraine<br />

transport distance at each site with subrounded<br />

boulders being typical of the 2-km-long Chicago<br />

Lakes Glacier, subangular boulders being typical<br />

of the 1-km-long Butler Gulch Glacier, and angular<br />

boulders being typical of the few-hundred-mlong<br />

Isabelle Glacier. Surface-exposure ages of angular<br />

boulders from the Isabelle Glacier moraine,<br />

which formed during the Little Ice Age (LIA) according<br />

to previous lichenometric dating, indicate<br />

cosmogenic inheritance values ranging from<br />

0 to similar to 3.0 Be-10 ka. (1) Subangular boulders<br />

from the Butler Gulch end moraine yielded<br />

surface-exposure ages ranging from 5 to 10.2 Be-10<br />

ka. We suggest that this moraine was deposited<br />

during the 8.2 cal ka event, which has been associated<br />

with outburst floods from Lake Agassiz and<br />

Lake Ojibway, and that the large age range associated<br />

with the Butler Gulch end moraine is caused<br />

by cosmogenic shielding of and(or) spalling from<br />

boulders that have ages in the younger part of the<br />

range and by cosmogenic inheritance in boulders<br />

that have ages in the older part of the range. <strong>The</strong><br />

surface-exposure ages of eight of nine subrounded<br />

boulders from the Chicago Lakes area fall within<br />

the 13.0-11.7 Be-10 ka age range, and appear to<br />

have been deposited during the Younger Dryas<br />

interval. <strong>The</strong> general lack of inheritance in the<br />

eight samples probably stems from the fact that<br />

only a few thousand years intervened between the<br />

retreat of the Pinedale glacier and the advance of<br />

the Chicago Lakes glacier; in addition, bedrock in<br />

the Chicago Lakes cirque area may have remained<br />

covered with snow and ice during that interval,<br />

thus partially shielding the bedrock from cosmogenic<br />

radiation.<br />

Quaternary Science Reviews, 2007, V26, N11-12,<br />

JUN, pp 1638-1649.<br />

08.1-314<br />

Palaeoclimate-induced range shifts may explain<br />

current patterns of spatial genetic variation<br />

in renosterbos (Elytropappus rhinocerotis,<br />

Asteraceae)<br />

Bergh N G, Hedderson T A, Linder H P, Bond W J<br />

South Africa, Switzerland<br />

Paleontology , Microbiology , Plant Sciences , Meteorology<br />

& Atmospheric Sciences<br />

<strong>The</strong> impact of Pleistocene climatic fluctuations on<br />

the distributions of plant species in the Greater<br />

Cape Floristic Region is largely unknown. We used<br />

a molecular fingerprinting tool, inter-simple sequence<br />

repeat (ISSR) PCR to examine the spatial<br />

distribution of genetic variation in the common<br />

and widespread shrub Elytropoppus rhinocerotis.<br />

We wished to test the hypothesis that refugia<br />

for the species were located in areas which were<br />

buffered from marked variations in precipitation<br />

between glacial and interglacial periods. Populations<br />

from less protected areas, in contrast, should<br />

have suffered size reductions or extinctions during<br />

the dry Holocene optimum. We detected a<br />

large amount of genetic variation in the species,<br />

which was apportioned largely amongst individuals<br />

within populations rather than amongst populations<br />

or regions, as expected for an outcrossing<br />

and well-dispersed plant species. However, there<br />

was significant spatial structure and an uneven<br />

distribution of diversity across the range. Geo-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

graphic distance is a very poor predictor of genetic<br />

distance between localities, especially towards<br />

the cast of the range. This may be due to range<br />

alteration over the time-scale reflected by ISSR<br />

polymorphism. Inter-SSR variation declined from<br />

south to north in the western arm of the range,<br />

consistent with the prediction of Holocene aridification<br />

starting first and being most extreme in<br />

the north. Areas shown by the marker to harbour<br />

populations with high levels of variability include<br />

most parts of the eastern arm of the range, and<br />

the Kamiesberg highlands. Possible explanations<br />

for the observed patterns of ISSR variation are discussed.<br />

Taxon, 2007, V56, N2, MAY, pp 393-408.<br />

08.1-315<br />

Decadal-scale autumn temperature reconstruction<br />

back to AD 1580 inferred from the varved<br />

sediments of Lake Silvaplana (southeastern<br />

<strong>Swiss</strong> Alps)<br />

Blass A, Bigler C, Grosjean M, Sturm M<br />

Switzerland, Sweden<br />

Limnology , Geology , Geochemistry & Geophysics<br />

Paleontology<br />

A quantitative high-resolution autumn (September-November)<br />

temperature reconstruction for<br />

the southeastern <strong>Swiss</strong> Alps back to AD 1580 is<br />

presented here. We used the annually resolved<br />

biogenic silica (diatoms) flux derived from the accurately<br />

dated and annually sampled sediments of<br />

Lake Silvaplana (46 degrees 27’N, 9 degrees 48’E,<br />

1800 m a.s.l.). <strong>The</strong> biogenic silica flux smoothed<br />

by means of a 9-yr running mean was calibrated<br />

(r=0.70, p < 0.01) against local instrumental temperature<br />

data (AD 1864-1949). <strong>The</strong> resulting reconstruction<br />

(+/- 2 standard errors= 0.7 degrees C) indicates<br />

that autumns during the late Little Ice Age<br />

were generally cooler than they were during the<br />

20th century. During the cold anomaly around<br />

AD 1600 and during the Maunder Minimum, however,<br />

the reconstructed autumn temperatures did<br />

not experience strong negative departures from<br />

the 20th-century mean. <strong>The</strong> warmest autumns<br />

prior to 1900 occurred around AD 1770 and 1820<br />

(0.75 degrees C above the 20th-century mean). Our<br />

data agree closely with two other autumn temperature<br />

reconstructions for the Alps and for Europe<br />

that are based on documentary evidence and are<br />

completely unrelated to our data, revealing a very<br />

consistent picture over the centuries.<br />

Quaternary Research, 2007, V68, N2, SEP, pp<br />

184-195.<br />

159<br />

08.1-316<br />

Signature of explosive volcanic eruptions in<br />

the sediments of a high- altitude <strong>Swiss</strong> lake<br />

Blass A, Grosjean M, Livingstone D M, Sturm M<br />

Switzerland<br />

Paleontology , Limnology , Geology<br />

<strong>The</strong> analysis of 125 years of well-dated varved sediments<br />

in Lake Silvaplana, located at 1,791 m a.s.l.<br />

in the Upper Engadine region of south-eastern<br />

Switzerland, reveals that 7 out of the 8 climatically<br />

relevant explosive volcanic eruptions between<br />

A.D. 1880 and 2004 were followed by distinct<br />

peaks in median grain-size. Although the underlying<br />

mechanisms are yet unclear, an analysis of<br />

local meteorological data suggests that this phenomenon<br />

is unlikely to be related to any change<br />

in air temperature associated with the eruptions,<br />

but instead may be related to an increase in autumn<br />

precipitation subsequent to the eruptions<br />

that led to the erosion and fluvial transport of particles<br />

larger than normal.<br />

Journal of Paleolimnology, 2008, V39, N1, JAN, pp<br />

35-42.<br />

08.1-317<br />

A European pattern climatology 1766-2000<br />

Casty C, Raible C C, Stocker T F, Wanner H, Luterbacher<br />

J<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , Modelling ,<br />

Paleontology<br />

Using monthly independently reconstructed gridded<br />

European fields for the 500 hPa geopotential<br />

height, temperature, and precipitation covering<br />

the last 235 years we investigate the temporal and<br />

spatial evolution of these key climate variables<br />

and assess the leading combined patterns of climate<br />

variability. Seasonal European temperatures<br />

show a positive trend mainly over the last 40 years<br />

with absolute highest values since 1766. Precipitation<br />

indicates no clear trend. Spatial correlation<br />

technique reveals that winter, spring, and autumn<br />

covariability between European temperature and<br />

precipitation is mainly influenced by advective<br />

processes, whereas during summer convection<br />

plays the dominant role. Empirical Orthogonal<br />

Function analysis is applied to the combined<br />

fields of pressure, temperature, and precipitation.<br />

<strong>The</strong> dominant patterns of climate variability for<br />

winter, spring, and autumn resemble the North<br />

Atlantic Oscillation and show a distinct positive<br />

trend during the past 40 years for winter and<br />

spring. A positive trend is also detected for summer<br />

pattern 2, which reflects an increased influence<br />

of the Azores High towards central Europe<br />

and the Mediterranean coinciding with warm


160 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

and dry conditions. <strong>The</strong> question to which extent<br />

these recent trends in European climate patterns<br />

can be explained by internal variability or are a<br />

result of radiative forcing is answered using cross<br />

wavelets on an annual basis. Natural radiative<br />

forcing (solar and volcanic) has no imprint on annual<br />

European climate patterns. Connections to<br />

CO 2 forcing are only detected at the margins of<br />

the wavelets where edge effects are apparent and<br />

hence one has to be cautious in a further interpretation.<br />

Climate Dynamics, 2007, V29, N7-8, DEC, pp<br />

791-805.<br />

08.1-318<br />

Reconstructing recent environmental changes<br />

from proglacial lake sediments in the western<br />

Alps (Lake blanc huez, 2543 m a.s.l., grandes<br />

rousses massif, france)<br />

Chapron E, Faien X, Magand O, Charlet L, Debret<br />

M, Melieres M A<br />

Switzerland, France<br />

Paleontology , Geology , Geomorphology<br />

<strong>The</strong> evolution of high-altitude glaciers and human<br />

activities in the Grandes Rousses massif is<br />

documented by high-resolution seismic reflection<br />

profiling and multiproxy analysis of short<br />

sediment cores in proglacial Lake Blanc Huez.<br />

<strong>The</strong>se lacustrine data are compared with historical<br />

chronicles, geomorphological features and<br />

glaciological studies in this region of the western<br />

Alps and they allow the documentation of recent<br />

environmental changes. <strong>The</strong> specific geometry<br />

of high-amplitude reflections in the uppermost<br />

seismic unit, the lithology of short cores and the<br />

available limnological data in the lake suggest<br />

that elastic particles eroded by the glaciers and<br />

transported in suspension by glacial melt waters<br />

in early summer essentially develop homopycnal<br />

flood events in the lake. A conceptual model<br />

linking fluctuations of glacier equilibrium line<br />

altitudes in the catchment area with sedimentary<br />

facies retrieved in the lake basin is proposed.<br />

This approach allows reconstructing continuous<br />

glacier fluctuations since AD1820-1850 and suggests<br />

several phases of glacier fluctuations during<br />

the Little Ice Age (LIA). <strong>The</strong>se reconstructions are<br />

based on changes in lacustrine sediment laminations,<br />

density, magnetic susceptibility, reflectance<br />

spectra, organic matter and Arsenic content. <strong>The</strong><br />

age-depth model of short sediment cores is provided<br />

by Pb-210, 117CS and Am-241 radionuclide<br />

dating. This chronology is further supported by<br />

identifying in lacustrine sediments the impact of<br />

(i) the nearby M 5.3 Corren on earthquake in AD<br />

1962, (ii) the development of the ski resort at high-<br />

altitude close to the lake and (iii) the last advance<br />

of glaciers during the LIA in AD1820-1850 and the<br />

following phase of glacier retreat observed in the<br />

alpine region at the end of the LIA in AD 1880. Frequent<br />

sandy layers enriched in organic matter and<br />

associated with fluctuations in the Arsenic concentrations<br />

may result from hydraulic remobilisation<br />

of Middle Age mine tailings at the lake shore<br />

by snow melt or heavy rain fall events during the<br />

LIA. (c) 2007 Elsevier B.V. All rights reserved.<br />

Palaeogeography Palaeoclimatology Palaeoecology,<br />

2007, V252, N3-4, SEP 3, pp 586-600.<br />

08.1-319<br />

Long-term interactions between Mediterranean<br />

climate, vegetation and fire regime at<br />

Lago di Massaciuccoli (Tuscany, Italy)<br />

Colombaroli D, Marchetto A, Tinner W<br />

Switzerland, Italy<br />

Plant Sciences , Forestry , Meteorology & Atmospheric<br />

Sciences , Paleontology , Ecology<br />

1. A Holocene sedimentary sequence from a coastal<br />

lake in the Mediterranean area (Lago di Massaciuccoli,<br />

Tuscany, Italy, 0 m a.s.l.) was sampled<br />

for pollen and microscopic charcoal analyses.<br />

Contiguous 1-cm samples represent an estimated<br />

time interval of c. 13 years, thus providing a highresolution<br />

sequence from 6100 to 5400 cal. years<br />

BP. 2. Just before 6000 cal. years BP, sub-Mediterranean<br />

and Mediterranean forests were present together<br />

with fir (Abies alba), a submontane species<br />

that is today absent at low altitudes in the Mediterranean.<br />

A sharp vegetational change occurred<br />

after 6000 cal. years BP involving a drastic decline<br />

of Abies alba around the site. 3. Time-series analyses<br />

suggest that increased fire activity at this time<br />

caused a strong decline in Abies alba, a highly<br />

fire-sensitive species. During 100 years of higher<br />

fire incidence, diverse (predominantly evergreen)<br />

forest communities were converted to low- diversity<br />

fire-prone shrub communities. 4. Cross-correlations<br />

reveal that fire during the mid-Holocene<br />

hindered the expansion of holm oak (Quercus<br />

ilex), the most common tree species today in Mediterranean<br />

environments. While the factors that<br />

triggered the Holocene expansion of this species<br />

in the Mediterranean area are unclear, our results<br />

do not support the hypothesis that fire was key<br />

for holm oak expansion. 5. Diatom analyses of<br />

the same sediment core provide an independent<br />

palaeoenvironmental proxy for palaeoclimatic<br />

reconstruction. A change in the eutrophy and<br />

salinity of the lake occurred just before 6000 cal.<br />

years BP, suggesting that a climatic shift towards<br />

aridity may have triggered the observed change<br />

in hydrology and possibly also in fire regime. 6.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

Over the millennia fire has decisively contributed<br />

to the establishment of the present fire-adapted<br />

vegetation type (macchia). Native fire-sensitive<br />

species were displaced or repressed, and arboreal<br />

vegetation became less diverse. Combined ecological<br />

and palaeoecological data may help to assess<br />

possible future scenarios of biosphere responses<br />

to global change. Our results imply that the forecasted<br />

global warming and fire increase may trigger<br />

irrecoverable biodiversity losses and shifts in<br />

vegetational composition within a few decades or<br />

centuries at most. In particular, fire and drought-<br />

sensitive vegetation types, such as the relict forests<br />

of Abies alba in the Apennines, seem particularly<br />

threatened by large-scale displacement.<br />

Journal of Ecology, 2007, V95, N4, JUL, pp<br />

755-770.<br />

08.1-320<br />

Using toponymy to reconstruct past land use:<br />

a case study of ‘brusada’ (burn) in southern<br />

Switzerland<br />

Conedera M, Vassere S, Neff C, Meurer M, Krebs P<br />

Switzerland, Germany<br />

History , Agriculture, Soil Sciences , Ecology , Paleontology<br />

Toponyms are frequently the outcome of a creative<br />

process, a subjective interpretation by the<br />

local inhabitants at the time of naming. <strong>The</strong>y often<br />

survive changes in the local landscape, thus<br />

becoming historical documents of landscape dynamics<br />

or changes in land use. In this contribution<br />

we provide a systematic synchronic analysis<br />

of the toponym brusada (burn) in Canton Ticino.<br />

In total, 182 instances of place names containing<br />

brusada were recorded, of which 102 cases (56.0%)<br />

were localised. Based on oral information provided<br />

by the local people or on archival documents, it<br />

was possible to group the selected toponyms into<br />

different meaning classes such as burnt building,<br />

exposed sites, pasture-land and others without<br />

any indication (classified here as generic). On the<br />

basis of etymological, topographic, documentary,<br />

bibliographic, and historic evidence, as well<br />

as proxy-archives (such as charcoal in lake sediments),<br />

we hypothesise that most of the toponyms<br />

associated with pasture-land - and probably also a<br />

large portion of the generic toponyms - are directly<br />

or indirectly related to the habit of using fire<br />

to clear brushwood to improve pasture-land or to<br />

eliminate trees. In the study area, the practice of<br />

pasture-fires appears to have been a very well controlled<br />

and targeted activity in medieval times. In<br />

contrast, pasture-fires became very frequent and<br />

uncontrolled in the second half of the nineteenth<br />

century up until the Second World War. Our study<br />

161<br />

confirms the usefulness and suitability of toponymy,<br />

in combination with other disciplines, for<br />

ecohistorical reconstructions of past environmental<br />

and land-use changes.<br />

Journal of Historical Geography, 2007, V33, N4,<br />

OCT, pp 729-748.<br />

08.1-321<br />

Multiproxy late quaternary stratigraphy of<br />

the Nile deep-sea turbidite system - Towards a<br />

chronology of deep-sea terrigeneous systems<br />

Ducassou E, Capotondi L, Murat A, Bernasconi<br />

S M, Mulder T, Gonthier E, Migeon S, Duprat J,<br />

Giraudeau J, Mascle J<br />

France, Italy, Switzerland<br />

Geology , Paleontology<br />

Understanding the recent formation of a sedimentary<br />

system such as a deep-sea turbidite system<br />

(DSTS) requires an accurate stratigraphic control<br />

on deposits. Due to the important terrigeneous input<br />

which disrupts the sedimentary record, DSTS<br />

is an environment where stratigraphic control<br />

is difficult to assess. Most of the time, traditional<br />

stratigraphic tools are not accurate enough. This<br />

has led to a rather limited number of studies concerning<br />

stratigraphy in DSTS. In this study, we examine<br />

several hemipelagic long piston cores collected<br />

from the Nile DSTS (eastern Mediterranean),<br />

in order to understand the recent evolution of the<br />

complex sedimentary system in this area. <strong>The</strong> first<br />

aim of this study is to show how to obtain a reliable<br />

timeframe in DSTS. Indeed, we provided a detailed<br />

ecostratigraphical scheme based on planktonic foraminiferal<br />

distribution, oxygen isotope records and<br />

lithostratigraphy (sapropels and tephra) of three<br />

cores where the sedimentation is least disturbed.<br />

We have identified 29 foraminiferal ecozones during<br />

the last 250,000 years BP, with an approximately<br />

2000-year time resolution. <strong>The</strong> time span of each<br />

ecozone was constrained by the oxygen isotope<br />

record, C-14 AMS radiometric data, tephrochronology<br />

and the sapropel chronology. <strong>The</strong>se high-resolution<br />

ecostratigraphical time subdivisions have<br />

been applied in discontinuous mixed hemipelagic/<br />

turbiditic sequences of a levee record. This example<br />

shows how to date gravity events, formation and<br />

time periods of sedimentary accumulations. (c)<br />

2007 Elsevier B.V. All rights reserved.<br />

Sedimentary Geology, 2007, V200, N1-2, AUG 1,<br />

pp 1-13.<br />

08.1-322<br />

Paleoecology of Pennsylvanian phylloid algal<br />

buildups in south Guizhou, China<br />

Enpu G, Samankassou E, Changqing G, Yongli Z<br />

Baoliang S


162 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

Switzerland, Peoples R China<br />

Paleontology , Marine & Freshwater Biology<br />

Pennsylvanian phylloid algal reefs are widespread<br />

and well exposed in south Guizhou, China. Here<br />

we report on reefs ranging from 2 to 8 m thickness<br />

and 30-50 m lateral extension. Algae, the<br />

main components, display a wide spectrum of<br />

growth forms, but are commonly cyathiform<br />

(cup-shaped) and leaf-like (undulate plates). <strong>The</strong><br />

algal reef facies is dominated by boundstone. Algal<br />

thalli form a dense carpet whose framework<br />

pores are filled with marine cement and peloidal<br />

micrite. <strong>The</strong> peloidal matrix is dense, partly laminated<br />

or clotted with irregular surfaces and often<br />

gravity defying. Algal reefs in Guizhou differ from<br />

examples reported to date by the high biodiversity<br />

of organisms other than phylloids: e.g., the<br />

intergrowth of algae with corals (some of which<br />

are twice the size of algal thalli) and numerous<br />

large brachiopods. This contrasts to previous<br />

views that phylloid algal “meadows” dominated<br />

the actual seafloor, excluding other biota. Also,<br />

the pervasive marine cements (up to 50%) including<br />

botryoidal cement are noteworthy. Algal reefs<br />

developed at platform margins, a depositional<br />

environment similar to that of modern Halimeda<br />

mounds in Java, Australia and off Bahamas, and to<br />

that of time-equivalent examples reported from<br />

the Canadian Arctic Archipelago. Whereas nutrients<br />

appear decisive in the growth of Halimeda<br />

reefs, algal reefs reported herein seemingly grew<br />

under conditions of low nutrient levels. Overall,<br />

algal reefs in Guizhou challenge previous views<br />

on growth forms, diversity patterns, and depositional<br />

environments and add to the spectrum of<br />

these partly puzzling biogenic structures.<br />

Facies, 2007, V53, N4, NOV, pp 615-623.<br />

08.1-323<br />

Long-term drought severity variations in<br />

Morocco<br />

Esper J, Frank D, Buentgen U, Verstege A, Luterbacher<br />

J<br />

Switzerland<br />

Plant Sciences , Forestry , Meteorology & Atmospheric<br />

Sciences , Paleontology<br />

Cedrus atlantica ring width data are used to reconstruct<br />

long-term changes in the Palmer Drought<br />

Severity Index (PDSI) over the past 953 years in<br />

Morocco, NW Africa. <strong>The</strong> reconstruction captures<br />

the dry conditions since the 1980s well and places<br />

this extreme period within a millennium-long<br />

context. PDSI values were above average for most<br />

of the 1450-1980 period, which let recent drought<br />

appear exceptional. However, our results also indicate<br />

that this pluvial episode of the past millen-<br />

nium was preceded by generally drier conditions<br />

back to 1049. Comparison of PDSI estimates with<br />

large-scale pressure field reconstructions revealed<br />

steady synoptic patterns for drought conditions<br />

over the past 350 years. <strong>The</strong> long-term changes<br />

from initially dry to pluvial to recent dry conditions<br />

are similar to PDSI trends reported from N<br />

America, and we suggest that they are related to<br />

long-term temperature changes, potentially teleconnected<br />

with ENSO variability and forced by<br />

solar irradiance changes.<br />

Geophysical Research Letters, 2007, V34, N17, SEP<br />

5 ARTN: L17702.<br />

08.1-324<br />

Modern pollen assemblages as climate indicators<br />

in southern Europe<br />

Finsinger W, Heiri O, Valsecchi V, Tinner W,<br />

Lotter A F<br />

Netherlands, Switzerland<br />

Meteorology & Atmospheric Sciences , Plant Sciences<br />

, Paleontology<br />

Aim and Location Our aim is to develop pollen-climate<br />

inference models for southern Europe and<br />

to test their performance and inference power by<br />

cross-validation with modern climate data. Surface<br />

sediments collected from lakes along a climate<br />

gradient from the winter-cold/summer-wet<br />

Alps to winter-wet/summer-dry Sicily were analysed<br />

for modern pollen assemblages. Methods For<br />

each lake, mean monthly temperatures, seasonal<br />

precipitation and site-specific climate uncertainties<br />

have been estimated. Pollen-climate relationships<br />

were studied using numerical analyses, and<br />

inference models were derived by partial least<br />

squares (PLS) and weighted-averaging PLS (WA-PLS)<br />

regressions for January and July temperatures (T),<br />

and for winter, spring and summer precipitation<br />

(P). In order to assess whether these variables are<br />

also of ecological importance for vegetation in the<br />

subregions, we split the data set into an Alpine<br />

and a Mediterranean subset. Results Low bootstrap<br />

cross-validated root mean square errors of<br />

prediction (RMSEP) for January T (1.7 degrees C),<br />

July T (2.1 degrees C) and summer P (38 mm), as<br />

well as low RMSEPs expressed as a percentage of<br />

the gradient length (8-9%), indicate a good inference<br />

power. Models revealed excellent to good<br />

performance statistics for January T, July T and<br />

summer P (r(2)= 0.8), and for winter and spring P<br />

(r(2) =c. 0.5). We show that the variables with the<br />

highest explanatory power differ between the two<br />

subregions. <strong>The</strong>se are summer T and P for the Alpine<br />

set, and January T, winter P and July T for the<br />

Mediterranean set. Main conclusions <strong>The</strong> study<br />

reveals the influence of climatic conditions dur-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

ing the growing season on modern pollen assemblages<br />

and indicates the potential of pollen data<br />

for long-term climate reconstructions of parameters<br />

such as winter precipitation and temperature,<br />

which seem to be the main factors having<br />

an influence on the variability of Mediterranean<br />

climate. <strong>The</strong>se models may therefore provide important<br />

information on past regional climate variability<br />

in southern Europe.<br />

<strong>Global</strong> Ecology and Biogeography, 2007, V16, N5,<br />

SEP, pp 567-582.<br />

08.1-325<br />

Reconstruction of millennial changes in dust<br />

emission, transport and regional sea ice coverage<br />

using the deep EPICA ice cores from the<br />

Atlantic and Indian Ocean sector of Antarctica<br />

Fischer H, Fundel F, Ruth U, Twarloh B, Wegner A,<br />

Udisti R, Becagli S, Castellano E, Morganti A, Severi<br />

M, Wolff E, Littot G, Röthlisberger R, Mulvaney<br />

R, Hutterli M A, Kaufmann P, Federer U, Lambert<br />

F, Bigler M, Hansson M, Jonsell U, de Angelis M,<br />

Boutron C, Siggaard Andersen M L, Steffensen J P,<br />

Barbante C, Gaspari V, Gabrielli P, Wagenbach D<br />

Germany, Italy, England, Switzerland, Sweden,<br />

France, Denmark<br />

Meteorology & Atmospheric Sciences , Geochemistry<br />

& Geophysics , Cryology / Glaciology , Paleontology<br />

Continuous sea salt and mineral dust aerosol records<br />

have been studied on the two EPICA (European<br />

Project for Ice Coring in Antarctica) deep ice<br />

cores. <strong>The</strong> joint use of these records from opposite<br />

sides of the East Antarctic plateau allows for an<br />

estimate of changes in dust transport and emission<br />

intensity as well as for the identification of<br />

regional differences in the sea salt aerosol source.<br />

<strong>The</strong> mineral dust flux records at both sites show a<br />

strong coherency over the last 150 kyr related to<br />

dust emission changes in the glacial Patagonian<br />

dust source with three times higher dust fluxes in<br />

the Atlantic compared to the Indian Ocean sector<br />

of the Southern Ocean (SO). Using a simple conceptual<br />

transport model this indicates that transport<br />

can explain only 40% of the atmospheric dust<br />

concentration changes in Antarctica, while factor<br />

5-10 changes occurred. Accordingly, the main<br />

cause for the strong glacial dust flux changes in<br />

Antarctica must lie in environmental changes in<br />

Patagonia. Dust emissions, hence environmental<br />

conditions in Patagonia, were very similar during<br />

the last two glacials and interglacials, respectively,<br />

despite 2-4 degrees C warmer temperatures<br />

163<br />

recorded in Antarctica during the penultimate<br />

interglacial than today. 2-3 times higher sea salt<br />

fluxes found in both ice cores in the glacial compared<br />

to the Holocene are difficult to reconcile<br />

with a largely unchanged transport intensity and<br />

the distant open ocean source. <strong>The</strong> substantial<br />

glacial enhancements in sea salt aerosol fluxes<br />

can be readily explained assuming sea ice formation<br />

as the main sea salt aerosol source with<br />

a significantly larger expansion of (summer) sea<br />

ice in the Weddell Sea than in the Indian Ocean<br />

sector. During the penultimate interglacial, our<br />

sea salt records point to a 50% reduction of winter<br />

sea ice coverage compared to the Holocene both<br />

in the Indian and Atlantic Ocean sector of the SO.<br />

However, from 20 to 80 ka before present sea salt<br />

fluxes show only very subdued millennial changes<br />

despite pronounced temperature fluctuations,<br />

likely due to the large distance of the sea ice salt<br />

source to our drill sites.<br />

Earth and Planetary Science Letters, 2007, V260,<br />

N1-2, AUG 15, pp 340-354.<br />

08.1-326<br />

Adjustment for proxy number and coherence<br />

in a large-scale temperature reconstruction<br />

Frank D, Esper J, Cook E R<br />

Switzerland, USA<br />

Paleontology , Meteorology & Atmospheric Sciences<br />

(1) Proxy records may display fluctuations in climate<br />

variability that are artifacts of changing replication<br />

and interseries correlation of constituent<br />

time-series and also from methodological considerations.<br />

<strong>The</strong>se biases obscure the understanding<br />

of past climatic variability, including estimation of<br />

extremes, differentiation between natural and anthropogenic<br />

forcing, and climate model validation.<br />

Herein, we evaluate as a case-study, the Esper et al.<br />

(2002) extra-tropical millennial-length temperature<br />

reconstruction that shows increasing variability<br />

back in time. We provide adjustments considering<br />

biases at both the site and hemispheric scales. <strong>The</strong><br />

variance adjusted record shows greatest differences<br />

before 1200 when sample replication is quite low. A<br />

reduced amplitude of peak warmth during Medieval<br />

Times by about 0.4 degrees C (0.2 degrees C)<br />

at annual (40-year) timescales slightly re-draws the<br />

longerterm evolution of past temperatures. Many<br />

other regional and large-scale reconstructions appear<br />

to contain variancerelated biases.<br />

Geophysical Research Letters, 2007, V34, N16,<br />

AUG 29 ARTN: L16709.


164 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

08.1-327<br />

Carbon dioxide release from the North Pacific<br />

abyss during the last deglaciation<br />

Galbraith E D, Jaccard S L, Pedersen T F, Sigman D<br />

M, Haug G H, Cook M, Southon J R, Francois R<br />

Canada, USA, Switzerland<br />

Paleontology , Meteorology & Atmospheric<br />

Sciences , Oceanography<br />

Atmospheric carbon dioxide concentrations were<br />

significantly lower during glacial periods than<br />

during intervening interglacial periods, but the<br />

mechanisms responsible for this difference remain<br />

uncertain. Many recent explanations call<br />

on greater carbon storage in a poorly ventilated<br />

deep ocean during glacial periods(1-5), but direct<br />

evidence regarding the ventilation and respired<br />

carbon content of the glacial deep ocean is sparse<br />

and often equivocal(6). Here we present sedimentary<br />

geochemical records from sites spanning the<br />

deep subarctic Pacific that-together with previously<br />

published results(7)- show that a poorly ventilated<br />

water mass containing a high concentration<br />

of respired carbon dioxide occupied the North Pacific<br />

abyss during the Last Glacial Maximum. Despite<br />

an inferred increase in deep Southern Ocean<br />

ventilation during the first step of the deglaciation<br />

(18,000-15,000 years ago)(4,8), we find no<br />

evidence for improved ventilation in the abyssal<br />

subarctic Pacific until a rapid transition similar<br />

to 14,600 years ago: this change was accompanied<br />

by an acceleration of export production from the<br />

surface waters above but only a small increase in<br />

atmospheric carbon dioxide concentration (8). We<br />

speculate that these changes were mechanistically<br />

linked to a roughly coeval increase in deep water<br />

formation in the North Atlantic (9-11), which<br />

flushed respired carbon dioxide from northern<br />

abyssal waters, but also increased the supply of<br />

nutrients to the upper ocean, leading to greater<br />

carbon dioxide sequestration at mid-depths and<br />

stalling the rise of atmospheric carbon dioxide<br />

concentrations. Our findings are qualitatively<br />

consistent with hypotheses invoking a deglacial<br />

flushing of respired carbon dioxide from an isolated,<br />

deep ocean reservoir(1-5,12), but suggest that<br />

the reservoir may have been released in stages,<br />

as vigorous deep water ventilation switched between<br />

North Atlantic and Southern Ocean source<br />

regions.<br />

Nature, 2007, V449, N7164, OCT 18, pp 890-U9.<br />

08.1-328<br />

Smithian-Spathian boundary event: Evidence<br />

for global climatic change in the wake of the<br />

end-Permian biotic crisis<br />

Galfetti T, Hochuli P A, Brayard A, Bucher H, Weissert<br />

H, Vigran J O<br />

Switzerland, France<br />

Meteorology & Atmospheric Sciences , Paleontology<br />

, Geology<br />

One of the most important carbon cycle perturbations<br />

following the end-Permian mass extinction<br />

event straddles the Smithian-Spathian boundary<br />

(SSB) (Olenekian, Early Triassic). This anomaly<br />

is characterized by a prominent positive carbon<br />

isotope excursion known from Tethyan marine<br />

rocks. Its global significance is established here<br />

by a new high paleolatitude record (Spitsbergen).<br />

Paleontological evidence, such as Boreal palynological<br />

data (Barents Sea, Norway) and global patterns<br />

of ammonoid distribution, indicates a synchronous<br />

major change in terrestrial and marine<br />

ecosystems near the SSB. <strong>The</strong> reestablishment of<br />

highly diverse plant ecosystems, including the<br />

rise of woody gymnosperms and decline of the<br />

formerly dominating lycopods, is interpreted as<br />

an effect of a major climate change. This hypothesis<br />

is supported by modeling of ammonoid paleobiogeography,<br />

the distribution patterns of which<br />

are interpreted as a proxy for sea surface temperatures<br />

(SST). <strong>The</strong> latest Smithian thus appears to<br />

have been a time of a warm and equable climate<br />

as expressed by an almost flat pole to equator SST<br />

gradient. In contrast, the steep Spathian SST gradient<br />

suggests latitudinally differentiated climatic<br />

conditions. We propose that this drastic climate<br />

change and the global carbon cycle perturbation<br />

were triggered by a massive end-Smithian CO 2 injection.<br />

<strong>The</strong> SSB event could therefore represent<br />

one of the causes for stepwise and delayed recovery<br />

of marine and terrestrial biotas in the wake of<br />

the end- Permian biotic crisis.<br />

Geology, 2007, V35, N4, APR, pp 291-294.<br />

08.1-329<br />

Dating of syngenetic ice wedges in permafrost<br />

with Cl-36<br />

Gilichinsky D A, Nolte E, Basilyan A E, Beer J, Blinov<br />

A V, Lazarev V E, Kholodov A L, Meyer H, Nikolskiy<br />

P A, Schirrmeister L, Tumskoy V E<br />

Russia, Germany, Switzerland<br />

Cryology / Glaciology , Paleontology<br />

A new method of permafrost dating with the cosmogenic<br />

radionuclide Cl-36 is presented. In the<br />

first application, syngenetic ice wedges are dated<br />

using the ratio of Cl-36 and Cl concentrations in<br />

ice as the signal. Cl-36 is produced in the atmo-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

sphere by nuclear reactions of cosmic rays on argon.<br />

Stable chlorine enters the atmosphere from<br />

the oceans. <strong>The</strong>ir ratio does not depend on chloride<br />

concentration in precipitations and on sublimation<br />

of snow. In situ production of Cl-36 in<br />

permafrost ice via cosmic ray-induced reactions<br />

and neutron capture are calculated and the dating<br />

age limit is estimated as 3 million years. Cl-36/<br />

Cl ratios in permafrost samples from cape Svyatoy<br />

Nos (Laptev Sea coast), North-Eastern Siberia, are<br />

measured by accelerator mass spectrometry. Analysis<br />

of the first results and the calculated dates<br />

support the feasibility of the Cl-36 permafrost dating<br />

method.<br />

Quaternary Science Reviews, 2007, V26, N11-12,<br />

JUN, pp 1547-1556.<br />

08.1-330<br />

Assimilation of the plutonic roots of the Andean<br />

arc: Evidence from CO 2-rich fluid inclusions<br />

in olivines<br />

Ginibre C, Dungan M A<br />

Switzerland<br />

Geochemistry & Geophysics , Geology ,<br />

Paleontology<br />

Geochimica et Cosmochimica Acta, 2007, V71,<br />

N15, AUG, SS, p A325.<br />

08.1-331<br />

Paleoecology of Late Carboniferous phylloid<br />

algae in southern Guizhou, SW China<br />

Gong E, Mang Y, Guan C, Samankassou E, Sun B,<br />

Sun B L<br />

Peoples R China, Switzerland<br />

Ecology , Paleontology , Marine & Freshwater<br />

Biology<br />

Phylloid algae are important reef-builders in the<br />

late Carboniferous. This paper focuses on the paleoecology<br />

of phylloid algae in the Late Carboniferous<br />

on well-exposed reefs in Ziyun County,<br />

Guizhou Province. Phylloid algae growing closely<br />

packed are attached via holdfast or similar structure<br />

to substrate. <strong>The</strong>y were growing in environments<br />

such as shallow water, photic zone and below<br />

the wave base with medium energy currents.<br />

<strong>The</strong>y have a variety of morphological forms, such<br />

as single cup-shaped, cabbage-shaped and clustering<br />

cup-shaped. <strong>The</strong> thalli are of certain tenacity<br />

and intensity. In the areas dominated by phylloid<br />

algae, other marine organisms are relatively<br />

scarce. Obviously, phylloid algae are stronger competitors<br />

for living space than other co-occurring<br />

organisms.<br />

Acta Geologica Sinica English Edition, 2007, V81,<br />

N4, AUG, pp 566-572.<br />

165<br />

08.1-332<br />

Late Quaternary river development in the<br />

southwest Chad Basin: OSL dating of sediment<br />

from the Komadugu palaeofloodplain (northeast<br />

Nigeria)<br />

Gumnior M, Preusser F<br />

Switzerland, Germany<br />

Paleontology , Geology , Hydrology<br />

<strong>The</strong> Komadugu river system is the major Nigerian<br />

tributary to Lake Chad. its large alluvial complex<br />

represents an important archive of the late Quaternary<br />

environmental history of the Chad Basin.<br />

Modern floodplains are incised into an older fluvial<br />

terrace that extends over 5000 km(2). Evidence<br />

from satellite images suggests that the ancient<br />

river system was dammed up by the Bama Beach<br />

Ridge during high stands of mega Lake Chad. This<br />

caused the formation of extensive wetlands with<br />

a chaotic network of relic channels. <strong>The</strong> first set<br />

of luminescence ages presented here fits well, into<br />

the previously established environmental history<br />

of the Chad Basin. Both the early and mid-Holocene<br />

pluvial periods as well as a final relatively humid<br />

period during the late Holocene are reflected<br />

by point bar to overbank deposits or channel fills.<br />

<strong>The</strong> onset of the Holocene was characterised by<br />

erosion of older dune fields as indicated by grain-<br />

size distributions of the alluvium. Satellite images<br />

and sedimentological observations show that<br />

the floodplain was dominated by meandering<br />

channels shifted by frequent avulsion, reflecting<br />

a high variability in precipitation and discharge<br />

patterns at the beginning and end of Holocene<br />

humid periods.<br />

Journal of Quaternary Science, 2007, V22, N7,<br />

OCT, pp 709-719.<br />

08.1-333<br />

Radiocarbon ages of soil charcoals from the<br />

southern Alps, Ticino Switzerland<br />

Hajdas I, Schlumpf N, Minikus Stary N, Hagedorn F,<br />

Eckmeier E, Schoch W, Burga C, Bonani G, Schmidt<br />

M W I, Cherubini P<br />

Switzerland<br />

Agriculture, Soil Sciences , Geochemistry & Geophysics<br />

, Forestry , Plant Sciences , Paleontology<br />

Radiocarbon dating of macroscopic charcoal is a<br />

useful toot for paleocliniatic and paleoecologic reconstructions.<br />

Here we present results of C-14 dating<br />

of charcoals found in charcoal-rich soils of Ticino<br />

and the Misox Valley (southern Switzerland)<br />

which indicate that the Late Glacial and early<br />

Holocene fires coincided with warm phases in the<br />

North Atlantic region and low lake levels in the<br />

Central Europe. Late Holocene charcoals found<br />

in these soils document an earlier than believed


166 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

presence of sweet chestnut (Castanea sativa Mill.)<br />

in southern Switzerland. Sweet chestnut trees<br />

play a key role in Mediterranean woodlands, and<br />

for longer than two millennia have been used as a<br />

food source. Based on palynological evidence it is<br />

commonly believed that in southern Switzerland<br />

C. sativa was first introduced 2000 years ago by<br />

the Romans, who cultivated it for wood and fruit<br />

production. Our results indicate that this tree<br />

species was present on the southern slopes of the<br />

Alps similar to 1500 years earlier than previously<br />

assumed, and therefore was likely introduced independently<br />

from cultivation by the Romans.<br />

Nuclear Instruments Methods in Physics Research<br />

Section B Beam Interactions with Materials and<br />

Atoms, 2007, V259, N1, JUN, pp 398-402.<br />

08.1-334<br />

Cosmogenic Be-10-ages from the Store Koldewey<br />

island, NE Greenland<br />

Hakansson L, Graf A, Strasky S, Ivy Ochs S, Kubik P<br />

W, Hjort C, Schlüchter C<br />

Switzerland, Sweden, USA<br />

Paleontology , Cryology / Glaciology , Geology<br />

Earlier work in northeast Greenland has suggested<br />

a limited advance of the Greenland Ice Sheet<br />

during the Last Glacial Maximum (LGM). However,<br />

this concept has recently been challenged by marine<br />

geological studies, indicating grounded ice on<br />

the continental shelf at this time. New Be-10-ages<br />

from the Store Koldewey island, northeast Greenland,<br />

suggest that unscoured mountain plateaus<br />

at the outer coast were covered at least partly by<br />

cold-based ice during the LGM. It is, however, still<br />

inconclusive whether this ice was dynamically<br />

connected to the Greenland Ice Sheet or not. Regardless<br />

of the LGM ice sheet extent, the Be-10 results<br />

from Store Koldewey add to a growing body<br />

of evidence suggesting considerable antiquity of<br />

crystalline unscoured terrain near present and<br />

Pleistocene ice sheet margins.<br />

Geografiska Annaler Series A Physical Geography,<br />

2007, V89A, N3, pp 195-202.<br />

08.1-335<br />

Evidence for recurrent changes in Lower Triassic<br />

oceanic circulation of the Tethys: <strong>The</strong> delta<br />

C-13 record from marine sections in Iran<br />

Horacek M, Richoz S, Brandner R, Krystyn L,<br />

Spoetl C<br />

Switzerland, Austria<br />

Paleontology , Geochemistry & Geophysics , Oceanography<br />

, Geology<br />

Stable carbon isotope curves derived from Lower<br />

Triassic carbonate rocks from three Iranian sections<br />

are established to investigate changes in the<br />

carbon cycle during the Early Triassic in this area.<br />

<strong>The</strong> sections are located in the south-center (Abadeh),<br />

north (Amol), and northwest (Zal) of Iran.<br />

All three curves show a similar pattern starting<br />

out with high delta C-13 values in the uppermost<br />

Permian decreasing across the Permian-Triassic<br />

boundary, an increase toward more positive values<br />

during the Griesbachian that slowly increase<br />

further up during the Dienerian, followed by a<br />

positive excursion to values as high as +8%o near<br />

the Dienerian/Smithian boundary. During the<br />

Smithian values return to below O%o, whereas<br />

second positive excursion to values higher than +<br />

3%o is recorded at the Smithian /Spathian boundary,<br />

again followed by a drop in delta C-13 into<br />

the Spathian and a final excursion to positive<br />

values at the Spathian /Anisian boundary. <strong>The</strong><br />

results from these Iranian sections are consistent<br />

with previous studies from Italy and China, thus<br />

strongly suggesting that the recorded delta C-13<br />

variability represents at least Tethys-wide geochemical<br />

signals. Moreover, the new curves reveal<br />

evidence of hich-amplitude, frequent oscillations<br />

pointing toward rapid and profound changes in<br />

the global carbon cycle during the Lower Triassic.<br />

Stratification of the ocean interrupted by episodic<br />

overturning transporting deep water to the ocean<br />

surface is a viable mechanism to account for the<br />

recorded isotope variations. Provided that the delta<br />

C-13 curve is representative of the global Lower<br />

Triassic ocean. it has high potential for accurately<br />

dating sedimentary successions via chemostratigraphy.<br />

Palaeogeography Palaeoclimatology Palaeoecology,<br />

2007, V252, N1-2, AUG 20, pp 355-369.<br />

08.1-336<br />

1. Flaje-Kiefern (Krusne Hory Mountains): Late<br />

Glacial and Holocene vegetation development<br />

Jankovska V, Kunes P, van der Knaap W O<br />

Czech Republic, Switzerland<br />

Paleontology , Forestry , Plant Sciences<br />

Grana, 2007, V46, N3, pp 214-216.<br />

08.1-337<br />

Microgram level radiocarbon (C-14) determination<br />

on carbonaceous particles in ice<br />

Jenk T M, Szidat S, Schwikowski M, Gäggeler H W,<br />

Wacker L, Synal H A, Saurer M<br />

Switzerland<br />

Cryology / Glaciology , Geochemistry & Geophysics<br />

Paleontology , Instruments & Instrumentation<br />

In climate research the interest on carbonaceous<br />

particles has increased over the last years because<br />

of their influence on the radiation balance of the<br />

earth. Nevertheless, there is a paucity of available


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

data regarding their concentrations and sources<br />

in the past. Such data would be important for a<br />

better understanding of their effects and for estimating<br />

their influence on future climate. Here,<br />

a technique is described to extract carbonaceous<br />

particles from ice core samples with subsequent<br />

separation of the two main constituents into organic<br />

carbon (OC) and elemental carbon (EC) for<br />

analysis of their concentrations in the past. This<br />

is combined with further analysis of OC and EC<br />

C-14/C-12 ratios by accelerator mass spectrometry<br />

(AMS), what can be used for source apportionment<br />

studies of past emissions. We further present how<br />

C-14 analysis of the OC fraction could be used in<br />

the future to date any ice core extracted from a<br />

high-elevation glacier. Described sample preparation<br />

steps to final analysis include the combustion<br />

of micrograms of water- insoluble carbonaceous<br />

particles, primary collected by filtration of melted<br />

ice samples, the graphitisation of the obtained<br />

CO 2 to solid AMS target material and final AMS<br />

measurements. Possible fractionation processes<br />

were investigated for quality assurance. Procedural<br />

blanks were reproducible and resulted in<br />

carbon masses of 1.3 +/- 0.6 µ g OC and 0.3 +/- 0.1 µ<br />

g EC per filter. <strong>The</strong> determined fraction of modern<br />

carbon (f(M)) for the OC blank was 0.61 0.13. <strong>The</strong><br />

analysis of processed IAEA-C6 and IAEA-C7 reference<br />

material resulted in f(M) = 1.521 +/- 0.011 and<br />

delta C-13 = -10.85 0.19%, and f(M) = 0.505 +/- 0.011<br />

and delta C-13 = - 14.21 0.19 parts per thousand,<br />

respectively, in agreement with consensus values.<br />

Initial carbon contents were thereby recovered<br />

with an average yield of 93%.<br />

Nuclear Instruments Methods in Physics Research<br />

Section B Beam Interactions with Materials and<br />

Atoms, 2007, V259, N1, JUN, pp 518-525.<br />

08.1-338<br />

Orbital and millennial Antarctic climate variability<br />

over the past 800,000 years<br />

Jouzel J, Masson Delmotte V, Cattani O, Dreyfus G,<br />

Falourd S, Hoffmann G, Minster B, Nouet J, Barnola<br />

J M, Chappellaz J, Fischer H, Gallet J C, Johnsen S,<br />

Leuenberger M, Loulergue L, Lüthi D, Oerter H, Parrenin<br />

F, Raisbeck G, Raynaud D, Schilt A, Schwander<br />

J, Selmo E, Souchez R, Spahni R, Stauffer B,<br />

Steffensen J P, Stenni B, Stocker T F, Tison J L,<br />

Werner M, Wolff E W<br />

France, Germany, Denmark, Iceland, Switzerland,<br />

Italy, Belgium, England<br />

Paleontology , Cryology / Glaciology , Meteorology<br />

& Atmospheric Sciences<br />

A high-resolution deuterium profile is now available<br />

along the entire European Project for Ice<br />

Coring in Antarctica Dome C ice core, extending<br />

167<br />

this climate record back to marine isotope stage<br />

20.2, similar to 800,000 years ago. Experiments<br />

performed with an atmospheric general circulation<br />

model including water isotopes support<br />

its temperature interpretation. We assessed the<br />

general correspondence between Dansgaard-Oeschger<br />

events and their smoothed Antarctic counterparts<br />

for this Dome C record, which reveals the<br />

presence of such features with similar amplitudes<br />

during previous glacial periods. We suggest that<br />

the interplay between obliquity and precession<br />

accounts for the variable intensity of interglacial<br />

periods in ice core records.<br />

Science, 2007, V317, N5839, AUG 10,<br />

pp 793-796.<br />

08.1-339<br />

Applying SAR-IRSL methodology for dating<br />

fine-grained sediments from lake El’gygytgyn,<br />

north-eastern Siberia<br />

Juschus O, Preusser F, Melles M, Radtke U<br />

Germany, Switzerland<br />

Geology , Geochemistry & Geophysics , Paleontology<br />

Lake El’gygytgyn is situated in a 3.6 Ma old impact<br />

crater in north- eastern Siberia and probably represents<br />

one of the most complete archives of Arctic<br />

climate change. Investigated here is the potential<br />

of infra-red stimulated luminescence (IRSL)<br />

using the single-aliquot regenerative-dose (SAR)<br />

approach for dating sediments from this lake.<br />

Independent age control is available from a published<br />

age model of a parallel core that is based on<br />

tuning sediment proxies with regional insolation<br />

and the results of previous multiple aliquot IRSL<br />

dating. Although the site is located within volcanic<br />

bedrock, anomalous fading seems to have<br />

little effect on the calculated ages. <strong>The</strong> modelled<br />

water content for the entire time of burial is seen<br />

as the most prominent uncertainty at this particular<br />

site. Despite these potential error sources,<br />

SAR-IRSL ages are in acceptable agreement with<br />

the given timeframe and clearly point to the possibility<br />

to establish independent chronologies at<br />

this site up to at least 400,000 years.<br />

Quaternary Geochronology, 2007, V2, N1-4, SI, pp<br />

187-194.<br />

08.1-340<br />

Unfractionated excess air: <strong>The</strong> result of incomplete<br />

dissolution of entrapped air?<br />

Klump S, Cirpka O A, Kipfer R<br />

Switzerland<br />

Paleontology , Geochemistry & Geophysics<br />

Geochimica et Cosmochimica Acta, 2007, V71, N15,<br />

AUG, SS, p A496.


168 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

08.1-341<br />

Excess air as a potential tracer for paleohydrological<br />

conditions<br />

Klump S, Grundl T, Purtschert R, Kipfer R<br />

Switzerland, USA<br />

Paleontology , Hydrology , Geochemistry & Geophysics<br />

Geochimica et Cosmochimica Acta, 2007, V71, N15,<br />

AUG, SS, p A497.<br />

08.1-342<br />

Bedrock landsliding, river incision, and<br />

transience of geomorphic hillslope-channel<br />

coupling: Evidence from inner gorges in the<br />

<strong>Swiss</strong> Alps<br />

Korup O, Schlunegger F<br />

Switzerland<br />

Paleontology , Geomorphology , Geology<br />

<strong>The</strong> formation of inner gorges cut into bedrock<br />

has been explained as relief rejuvenation by fluvial<br />

incision in response to rapid base level drop,<br />

repeated glaciations, frequent pore pressuredriven<br />

landsliding focused at hillslope toes, or<br />

catastrophic outburst flows from natural dam<br />

failures. Prominent inner gorges occur in soft<br />

Mesozoic Bundner schist and lower Tertiary<br />

flysch units of the formerly glaciated Alpenrhein<br />

catchment, eastern <strong>Swiss</strong> Alps. <strong>The</strong>ir channel and<br />

hillslope morphologies differ from basins characterized<br />

by strong glacial or landslide imprints,<br />

while formally resembling the theoretically predicted<br />

transient response of detachment-limited<br />

bedrock rivers to rapid base level fall by headward<br />

knickpoint migration. Assuming a postglacial onset<br />

of fluvial bedrock incision into a Last Glacial<br />

Maximum surface in response to base level drop<br />

induced by downwasting of trunk valley glaciers<br />

requires downcutting rates E > 20 mm yr(-1) and<br />

requires hillslopes to adjust by frequent landsliding<br />

toward development of a threshold state. We<br />

test this scenario using data on surface uplift,<br />

geomorphometry, geomorphic hillslope coupling,<br />

and probabilistic slope stability models. We find<br />

that adjustment of inner gorge walls through<br />

landsliding is mainly strength limited and structurally<br />

controlled, and threshold conditions are<br />

restricted to the lower 25% of local hillslope relief.<br />

Mass movement processes on upper hillslopes remain<br />

largely decoupled from channel incision despite<br />

inferred postglacial specific sediment yields<br />

of 10(4) m(3) km(-2) yr(-1) from the studied basins.<br />

Conversely, several constraints imposed by fluvial<br />

bedrock detachment, postglacial sediment yields,<br />

and bedrock landsliding argue for a pre-Holocene<br />

origin for at least some of the inner gorges in the<br />

area. This implies partial protection of fluvial<br />

gorge topography by subglacial sediment fill during<br />

the last (Wurm) extensive glaciation and implies<br />

that glaciers were insufficient to fully eradicate<br />

fluvially sculpted bedrock topography. This<br />

leads us to conclude that lithology and major climate<br />

oscillations should be considered as further<br />

alternative controls on inner gorge formation.<br />

Journal of Geophysical Research Earth Surface,<br />

2007, V112, NF3, SEP 27 ARTN: F03027.<br />

08.1-343<br />

Millenial scale variations of the isotopic composition<br />

of atmospheric oxygen over Marine<br />

Isotopic Stage 4<br />

Landais A, Masson Delmotte V, Combourieu<br />

Nebout N, Jouzel J, Blunier T, Leuenberger M, Dahl<br />

Jensen D, Johnsen S<br />

Israel, France, Switzerland, Denmark<br />

Meteorology & Atmospheric Sciences , Paleontology<br />

, Cryology / Glaciology , Geochemistry &<br />

Geophysics<br />

During rapid events of the last glacial period (DO<br />

events), dramatic changes are recorded at high<br />

and low latitudes. Without a precise common<br />

timescale, links between changes in Greenland<br />

temperature and changes in biosphere productivity,<br />

hydrology regimes and sea level are difficult<br />

to establish. <strong>The</strong> composition of atmospheric<br />

oxygen (delta O-18(atm)) is influenced by global<br />

sea level changes, the global hydrologic cycle and<br />

the biosphere productivity. Since delta O-18(atm)<br />

is measured in ice cores it gives the opportunity<br />

to investigate the underlying processes with no<br />

timescale uncertainty. Here, we present the first<br />

high resolution (50 yrs) record of the isotopic composition<br />

of atmospheric oxygen (delta O-19(atm))<br />

measured in the air trapped in a Greenland ice<br />

core (NorthGRIP). Our record covers a sequence of<br />

DO events (18-19-20) corresponding to the Marine<br />

Isotopic Stage 4, similar to 75 to 60 ka ago. Our<br />

measurements reveal rapid changes of delta O-<br />

18(atm) associated with the DO events. With a few<br />

additional measurements of the third isotope of<br />

oxygen (O-17) during the DO event 19, we exclude<br />

the hypothesis that sea level changes are responsible<br />

for the isotopic variations. <strong>The</strong>y originate<br />

more likely from large changes in relative humidity<br />

and latitudinal repartition of the continental<br />

vegetation over the DO events.<br />

Earth and Planetary Science Letters, 2007, V258,<br />

N1-2, JUN 15, pp 101-113.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

08.1-344<br />

Ages for the Big Stone Moraine and the oldest<br />

beaches of glacial Lake Agassiz: Implications<br />

for deglaciation chronology<br />

Lepper K, Fisher T G, Hajdas I, Lowell T V<br />

USA, Switzerland<br />

Paleontology , Cryology / Glaciology , Geology<br />

Glacial Lake Agassiz has been implicated as the<br />

tritmer for numerous episodes of abrupt climate<br />

change at the close of the last ice age, yet the beginning<br />

age of the lake has never been determined.<br />

Here we report the first numerical age data on the<br />

Big Stone Moraine and the oldest beaches of glacial<br />

Lake Agassiz. Organic remains from lakes, bogs,<br />

and channels distal to, and inset to, the Big Stone<br />

Moraine require that glacial activity at this moraine<br />

ceased prior to 12,000 C-14 yr B.P. (13,950 cal<br />

(calendar) yr). A site near New Effington, South Dakota<br />

(United States), implies full glacial recession<br />

north of the topographic divide prior to 11,810 C-14<br />

yr B.P. (13,670 cal yr), synchronous with the beginning<br />

of glacial Lake Agassiz. Lake Agassiz shorelines<br />

inset to the moraine yield optically stimulated luminescence<br />

(OSL) ages from 14,200-12,600 yr cal.<br />

Lower strandlines are younger, but the similarity of<br />

ages suggests that initial lake lowering was faster<br />

than OSL ages can currently resolve. Nevertheless,<br />

the OSL ages represent the first numerical age assignments<br />

for the Herman, Norcross, and Upham<br />

beach ridges, setting the stage for future numerical<br />

age assignments within the Lake Agassiz basin.<br />

<strong>The</strong>se two dating methods yield strongly consistent<br />

results within stated uncertainties. <strong>The</strong> age of<br />

the Big Stone Moraine implies an interval of rapid<br />

retreat for the Des Moines lobe of the Laurentide<br />

Ice Sheet during the BiAling-Allerod warm interval.<br />

<strong>The</strong> overlapping ages for the uppermost beach<br />

levels and abandonment of the highest Lake Agassiz<br />

spillway indicate a rapidly evolving lake until at<br />

least 13,500 yr cal.<br />

Geology, 2007, V35, N7, JUL, pp 667-670.<br />

08.1-345<br />

Variable Be-10 fluxes in lacustrine sediments<br />

from Tristan da Cunha, South Atlantic: a solar<br />

record?<br />

Ljung K, Bjorck S, Muscheler R, Beer J, Kubik P W<br />

Sweden, USA, Switzerland<br />

Geology , Geochemistry & Geophysics ,<br />

Oceanography , Paleontology<br />

A 650-yr-long sediment sequence from a crater<br />

lake on Tristan da Cunha, South Atlantic, was<br />

analysed for its Be-10 content. Based on C-14 dating,<br />

and sedimentary, geochemical, magnetic<br />

and palynological records, the period between<br />

900 and 1450 AD appears to have been unusually<br />

169<br />

stable in terms of sedimentation and vegetation<br />

and therefore this period was chosen for analysis<br />

of the Be-10 content. During this period of highly<br />

organic sedimentation and closed vegetation, the<br />

pattern of Be-10 flux variations follows the Be-10<br />

fluctuations from the GRIP ice core and estimated<br />

C-14 production rates well. However, before and<br />

after this stable period, variable sedimentation<br />

rates have to be accounted for to obtain results<br />

that are comparable to the established Be-10/C-14<br />

records. Our data show not only the possibility of<br />

obtaining detailed enough Be-10 flux data from<br />

sedimentary sequences to reconstruct past solar<br />

forcing but also how sensitive this type of record<br />

is to sedimentary and environmental changes. If<br />

suitable archives can be found, they have the potential<br />

to improve reconstructions of solar activity<br />

far back in time.<br />

Quaternary Science Reviews, 2007, V26, N7-8,<br />

APR, pp 829-835<br />

08.1-346<br />

Characterizing carbon isotopic variability in<br />

Sphagnum<br />

Loader N J, Mccarroll D, van der Knaap W O,<br />

Robertson I, Gagen M<br />

Wales, Switzerland<br />

Paleontology , Plant Sciences , Forestry , Geology<br />

To understand more fully the nature of isotopic<br />

fractionation in mosses and to explore the potential<br />

of stable isotope analyses of selected peat<br />

constituents for palaeoenvironmental research,<br />

we present results from a study of inter- and intraplant<br />

delta C-13 variability in Sphagnum spp. Subdivisions<br />

of stem, pendant and horizontal branch<br />

elements of modern Sphagnum capillifolium<br />

plants revealed consistent and statistically significant<br />

differences in their isotopic composition. Sequential<br />

(downstem) analysis of a further cohort<br />

of four modern Sphagnum capillifolium plants<br />

also reveals evidence of common forcing on the<br />

isotopic composition of sequentially formed stem<br />

and branch increments. This relationship was<br />

tested further by analysis of a series of branch and<br />

stem samples manually recovered from Sphagnum<br />

fuscum preserved within a late Holocene (AD<br />

2003-1970) peat monolith from a European mire.<br />

<strong>The</strong> high degree of isotopic coherence observed<br />

between plants supports the analysis of Sphagnum<br />

in palaeoecological investigations. However<br />

inter- and intra-plant variability between both<br />

branch and stem. sections emphasize the need for<br />

representative sampling, replication and sample<br />

homogeneity when conducting palaeoecological<br />

studies.<br />

Holocene, 2007, V17, N3, APR, pp 403-410.


170<br />

08.1-347<br />

Detailed record of the mid-Oxfordian (Late<br />

Jurassic) positive carbon- isotope excursion in<br />

two hemipelagic sections (France and Switzerland):<br />

A plate tectonic trigger?<br />

Louis Schmid B, Rais P, Bernasconi S M, Pellenard P,<br />

Collin P Y, Weissert H<br />

Switzerland, France<br />

Paleontology , Oceanography , Geology , Geochemistry<br />

& Geophysics<br />

<strong>The</strong> Oxfordian (Late Jurassic) was a time of widespread<br />

change in Jurassic marine (carbonate) sedimentation<br />

patterns. A marked positive excursion<br />

in delta C-13 is dated as Middle Oxfordian in age.<br />

In this study we investigate if changes in carbonate<br />

sedimentation coincided with altered carbon<br />

cycling and climate. We use C-isotope records as<br />

a proxy for the evolution of the carbon cycle and<br />

compare delta C-13- trends with the evolution of<br />

sedimentation in a segment of the opening Tethys<br />

seaway. One of the studied sections is located in<br />

the Subalpine basin of France (Trescleoux and<br />

Oze), the other in the <strong>Swiss</strong> Jura mountains (Liesberg).<br />

Carbon-isotope stratigraphy of carbonate<br />

carbon locates the peak values of the Middle Oxfordian<br />

positive excursion to the antecedens and<br />

parandieri subzones of the plicatilis and transversarium<br />

ammonite zones, respectively. Causes of<br />

the excursion remain enigmatic. <strong>The</strong> excursion<br />

seems not to coincide with a global oceanic anoxic<br />

event, but regionally enhanced organic carbon<br />

accumulation during the Early and early Middle<br />

Oxfordian may be the cause of the increase in<br />

delta C-13. <strong>The</strong> excursion occurs during a time of<br />

progressive climate warming, and its peak values<br />

coincide with the first calcareous sediments recurring<br />

after a period of reduced carbonate accumulation<br />

in the Early and early Middle Oxfordian.<br />

<strong>The</strong> excursion is also time-equivalent to a major<br />

reorganisation of global ocean currents: the opening<br />

Atlantic and Tethys oceans combined with rising<br />

sea level led to the formation of an efficient<br />

circumglobal seaway. We conclude that this favoured<br />

the widespread recurrence of carbonate<br />

producers by providing new habitats. As a result,<br />

C-carb burial increased, leading to a lower C- org/<br />

C-carb burial rate and therefore to stabilisation<br />

and decrease in delta C-13 in the Middle Oxfordian.<br />

Thus, the mid-Oxfordian positive excursion<br />

in carbonate C-isotopes may reflect changes in the<br />

carbon cycle that were triggered by a copious reorganisation<br />

of the ocean current system caused by<br />

major plate tectonic movements.<br />

Palaeogeography Palaeoclimatology Palaeoecology,<br />

2007, V248, N3-4, MAY 25, pp 459-472.<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

08.1-348<br />

Impact of methane seeps on the local carbonisotope<br />

record: a case study from a Late Jurassic<br />

hemipelagic section<br />

Louis Schmid B, Rais P, Logvinovich D, Bernasconi S<br />

M, Weissert H<br />

Switzerland<br />

Geology , Paleontology , Geochemistry &<br />

Geophysics<br />

An Oxfordian (Late Jurassic) hemipelagic succession<br />

from Beauvoisin (SE France) contains a<br />

pronounced, short-lived negative excursion in<br />

the bulk-carbonate carbon-isotope record, with<br />

an amplitude of 47 parts per thousand. it was<br />

shown previously that the Beauvoisin paleoenvironment<br />

was impacted by hydrocarbon seepage.<br />

New isotopic data corroborate that methane was<br />

a significant constituent of these hydrocarbons.<br />

<strong>The</strong> negative excursion was caused by transient<br />

enhanced precipitation of 13 C-depleted carbonate,<br />

mediated by anaerobic oxidation of methane.<br />

Despite its local diagenetic origin, the Beauvoisin<br />

excursion is similar in shape and duration to globally<br />

recognized negative C-isotope excursions that<br />

have been related to catastrophic, massive dissociation<br />

of methane hydrate. Shape and duration<br />

of negative excursions therefore cannot be used<br />

as an argument when determining their origin if<br />

they have not been shown to represent a global<br />

perturbation of the carbon cycle.<br />

Terra Nova, 2007, V19, N4, AUG, pp 259-265.<br />

08.1-349<br />

Plate tectonic trigger of changes in pCO(2)<br />

and climate in the Oxfordian (Late Jurassic):<br />

Carbon isotope and modeling evidence<br />

Louis Schmid B, Rais P, Schäffer P, Bernasconi S M,<br />

Weissert H<br />

Switzerland, France<br />

Modelling , Paleontology , Meteorology & Atmospheric<br />

Sciences , Geochemistry & Geophysics<br />

<strong>The</strong> transition from the Middle to the Late Jurassic<br />

was characterized by significant changes<br />

in oceanography and climate and by changes in<br />

global carbon cycle as shown in the C-isotope<br />

record. A prominent mid-Oxfordian positive excursion<br />

in bulk carbonate carbon isotope values<br />

(delta C-13(carb)) With an amplitude of more than<br />

1% has been documented from many sections in<br />

the Northern Tethys realm. In this study we present<br />

new bulk organic matter C-isotope data (delta<br />

C-13 (org)) from northwestern Tethys that do not<br />

record the mid-Oxfordian positive excursion in<br />

carbonate carbon. On the contrary, delta C-13<br />

(org) decreases during the interval of the most


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s 171<br />

rapid increase in delta C-13(carb). We demonstrate<br />

that this decrease is not due to a changing marine-terrestrial<br />

organic carbon partitioning but<br />

that the contrasting isotope trends record peculiar<br />

environmental and climate changes which<br />

occurred near the beginning of the Late Jurassic.<br />

Using a simple carbon cycle model we show<br />

that an increase in atmospheric p CO(2) starting<br />

at modem levels could be the cause of contrasting<br />

trends in delta C-13(carb) and delta C-13(org).<br />

We suggest that a reorganisation of ocean currents<br />

related to the opening and/or widening of<br />

the Tethys-Atlantic-Pacific seaway, and a massive<br />

spread of shallow-sea carbonate production led<br />

to higher pCO(2). Model simulations indicate that<br />

this increase in pCO(2) may have triggered changes<br />

in the biological carbon pump and in organic<br />

carbon burial that can explain the Middle Oxfordian<br />

C-isotope record.<br />

Earth and Planetary Science Letters, 2007, V258,<br />

N1-2, JUN 15, pp 44-60.<br />

08.1-350<br />

New constraints on the gas age-ice age difference<br />

along the EPICA ice cores, 0-50 kyr<br />

Loulergue L, Parrenin F, Blunier T, Barnola J M,<br />

Spahni R, Schilt A, Raisbeck G, Chappellaz J<br />

France, Switzerland<br />

Paleontology , Meteorology & Atmospheric Sciences<br />

, Cryology / Glaciology<br />

Gas is trapped in polar ice sheets at similar to 50-120<br />

m below the surface and is therefore younger than<br />

the surrounding ice. Firn densification models<br />

are used to evaluate this ice age-gas age difference<br />

(Delta age) in the past. However, such models need<br />

to be validated by data, in particular for periods<br />

colder than present day on the East Antarctic plateau.<br />

Here we bring new constraints to test a firn<br />

densification model applied to the EPICA Dome C<br />

(EDC) site for the last 50 kyr, by linking the EDC<br />

ice core to the EPICA Dronning Maud Land (EDML)<br />

ice core, both in the ice phase (using volcanic horizons)<br />

and in the gas phase (using rapid methane<br />

variations). We also use the structured Be-10 peak,<br />

occurring 41 kyr before present (BP) and due to<br />

the low geomagnetic field associated with the<br />

Laschamp event, to experimentally estimate the<br />

Delta age during this event. Our results seem to<br />

reveal an overestimate of the Delta age by the firn<br />

densification model during the last glacial period<br />

at EDC. Tests with different accumulation rates<br />

and temperature scenarios do not entirely resolve<br />

this discrepancy. Although the exact reasons for<br />

the Delta age overestimate at the two EPICA sites<br />

remain unknown at this stage, we conclude that<br />

current densification model simulations have def-<br />

icits under glacial climatic conditions. Whatever<br />

the cause of the Delta age overestimate, our finding<br />

suggests that the phase relationship between<br />

CO 2 and EDC temperature previously inferred for<br />

the start of the last deglaciation (lag of CO 2 by 800<br />

+/- 600 yr) seems to be overestimated.<br />

Climate of the Past, 2007, V3, N3, pp 527-540.<br />

08.1-351<br />

Comparison of techniques for dating of subsurface<br />

ice from Monlesi ice cave, Switzerland<br />

Luetscher M, Bolius D, Schwikowski M, Schotterer<br />

U, Smart P L<br />

Switzerland, England<br />

Paleontology , Cryology / Glaciology<br />

<strong>The</strong> presence of cave ice is documented in many<br />

karst regions but very little is known about the age<br />

range of this potential paleoclimate archive. This<br />

case study from the Monlesi ice cave, <strong>Swiss</strong> Jura<br />

Mountains, demonstrates that dating of cave ice<br />

is possible using a multi-parameter approach. Ice<br />

petrography, debris content and oxygen isotope<br />

composition have the potential for identification<br />

of annual growth layers, but require a continuous<br />

core from the ice deposits, limiting application<br />

of this approach. Furthermore, complete melting<br />

of ice accumulations from individual years<br />

may occur, causing amalgamation of several annual<br />

bands. Use of H-3 content of the ice and C-14<br />

dating of organic debris present in the ice proved<br />

to be of limited utility, providing rather broad<br />

bounds for the actual age. Initial estimates based<br />

on Pb-210 analyses from clear ice samples gave<br />

results comparable to those from other methods.<br />

<strong>The</strong> most reliable techniques applied were the determination<br />

of ice turnover rates, and the dating<br />

of anthropogenic inclusions (a roof tile) in the ice.<br />

<strong>The</strong>se suggest, respectively, that the base of the<br />

cave ice was a minimum of 120 and a maximum<br />

of 158 years old. <strong>The</strong>refore, our data support the<br />

idea that mid-latitude and low-altitude subsurface<br />

ice accumulations result from modern deposition<br />

processes rather than from presence of<br />

Pleistocene relict ice.<br />

Journal of Glaciology, 2007, V53, N182,<br />

pp 374-384.<br />

08.1-352<br />

Detailed sedimentary N isotope records from<br />

Cariaco Basin for terminations I and V: Local<br />

and global implications<br />

Meckler N A , Haug G H, Sigman D M, Plessen B,<br />

Peterson L C, Thierstein H R<br />

Switzerland, Germany, USA<br />

Geology , Geochemistry & Geophysics , Oceanography<br />

, Paleontology


172 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

(1) For the last deglaciation and Termination<br />

V (the initiation of MIS 11 at around 430 ka) we<br />

report high-resolution sedimentary nitrogen<br />

isotope (delta N-15)records from Cariaco Basin<br />

in the Caribbean Sea. During both terminations<br />

the previously reported interglacial decrease in<br />

delta N-15 clearly lags local changes such as water<br />

column anoxia as well as global increases in<br />

denitrification by several thousand years. On top<br />

of the glacial-interglacial change, several delta<br />

N-15 peaks were observed during the last deglaciation.<br />

<strong>The</strong> deglacial signal in Cariaco Basin can be<br />

best explained as a combination of (1) local variations<br />

in suboxia and water column denitrification<br />

as the reason for the millennial-scale peaks, (2) a<br />

deglacial maximum in mean ocean nitrate delta<br />

N-15, and (3) increasing N-2 fixation in response<br />

to globally increased denitrification causing the<br />

overall deglacial delta N-15 decrease. In the Holocene,<br />

much of the decrease in delta N-15 occurred<br />

between 6 and 3 ka, coinciding with an expected<br />

precession-modulated increase in African dust<br />

transport to the tropical North Atlantic and the<br />

Caribbean. This begs the hypothesis that N-2 fixation<br />

in this region increased in response to interglacial<br />

maxima in denitrification elsewhere but<br />

that this response strengthened with increased<br />

mid- Holocene iron input. It remains to be seen<br />

whether the data for MIS 11 support this interpretation.<br />

<strong>Global</strong> Biogeochemical Cycles, 2007, V21, N4, DEC<br />

15 ARTN: GB4019.<br />

08.1-353<br />

Grape harvest dates as a proxy for <strong>Swiss</strong> April<br />

to August temperature reconstructions back to<br />

AD 1480<br />

Meier N, Rutishauser T, Pfister C, Wanner H, Luterbacher<br />

J<br />

Switzerland<br />

Plant Sciences , Meteorology & Atmospheric Sciences<br />

, Paleontology<br />

We present an annually resolved record of grape<br />

harvest dates for Switzerland. <strong>The</strong> strong negative<br />

relationship between grape harvest dates<br />

and April August temperatures allowed a new<br />

reconstruction, with associated uncertainties, to<br />

be derived back to 1480. Calibration (1928 -1979)<br />

was performed with monthly data from the Basel<br />

and Geneva stations and verified over 1980<br />

-2006. Twelve days of grape harvest difference<br />

correspond to around 1 degrees C April - August<br />

temperature difference. Periods cooler (late grape<br />

harvest dates) than the 1961 -1990 mean are reconstructed<br />

during the 17th century and at the beginning<br />

of the 19th century. Warmer conditions were<br />

experienced in the early 18th century and during<br />

the recent decades, in agreement with grape harvest<br />

temperature reconstructions from France and<br />

other independent temperature estimates. On<br />

decadal (annual) time-scales the earliest harvests<br />

were in the 1580s (2003) and the latest vintages in<br />

the 1740s (1816). Large tropical volcanic eruptions<br />

led to significantly later grape harvest dates (cooling)<br />

one to two years after the event.<br />

Geophysical Research Letters, 2007, V34, N20, OCT<br />

24 ARTN: L20705.<br />

08.1-354<br />

Evidence of a two-fold glacial advance during<br />

the last glacial maximum in the Tagliamento<br />

end moraine system (eastern Alps)<br />

Monegato G, Ravazzi C, Donegana M, Pini R, Calderoni<br />

G, Wick L<br />

Italy, Switzerland<br />

Paleontology , Cryology / Glaciology ,<br />

Geomorphology<br />

<strong>The</strong> glacial history of the Tagliamento morainic<br />

amphitheater (southeastern Alpine foreland, Italy)<br />

during the last glacial maximum (LGM) has<br />

been reconstructed by means of a geological survey<br />

and drillings, radiocarbon dating and pollen<br />

analysis in the amphitheater and in the sandur.<br />

Two phases of glacial culmination, separated by a<br />

distinct recession, are responsible for glacial landforms<br />

and related sediments in the outer part of<br />

the amphitheater. <strong>The</strong> age of the younger advance<br />

fits the chronology of the culmination of the last<br />

glaciation in the Alps, well established between<br />

24 and 21 cal ka BP (20 to 17.5 C-14 ka BP), whereas<br />

the first pulse between 26.5 and 23 cal ka BP (22<br />

to 21 (14C) ka BP), previously undated, was usually<br />

related to older (pre-LGM) glaciations by previous<br />

authors. Here, the first pulse is the most extensive<br />

LGM culmination, but is often buried by the subsequent<br />

pulse. <strong>The</strong> onset and final recession of the<br />

late Wurm Alpine glaciation in the Tagliamento<br />

amphitheater are synchronous with the established<br />

global glacial maximum between 30 and 19<br />

cal ka BP. <strong>The</strong> two-fold LGM glacial oscillation is interpreted<br />

as a millennial-scale modulation within<br />

the late Warm glaciation, caused by oscillations in<br />

inputs of southerly atmospheric airflows related<br />

to Dansgaard-Oeschger cycles. Phases of enhanced<br />

southerly circulation promoted increased rainfall<br />

and ice accumulation in the southern Alps.<br />

Quaternary Research, 2007, V68, N2, SEP, pp<br />

284-302.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

08.1-355<br />

European ammonoid diversity questions the<br />

spreading of anoxia as primary cause for the<br />

Cenomanian/Turonian (Late Cretaceous) mass<br />

extinction<br />

Monnet C, Bucher H<br />

Switzerland<br />

Marine & Freshwater Biology , Geology ,<br />

Paleontology , Biodiversity<br />

Ammonoid diversity patterns show that the<br />

spreading of oceanic anoxia is not the initial and<br />

major kill mechanism for the Cenomanian /Turonian<br />

mass extinction as usually suggested. In the<br />

Anglo-Paris Basin and the Vocontian Basin, the<br />

drop of ammonoid species richness starts around<br />

the middle/late Cenomanian boundary, i.e. 0.75<br />

myr before the occurrence of anoxic deep-water<br />

sediments. <strong>The</strong> stepwise extinction of first heteromorphs<br />

and then acanthoceratids is incompatible<br />

with the rise of the oxygen minimum zone. Moreover,<br />

shelf environments of these basins remained<br />

well oxygenated during the Cenomanian/Turonian<br />

boundary interval. Thus, we stress that other<br />

causative mechanisms initiated the ammonoid<br />

extinction even if anoxia subsequently participated<br />

in the demise of marine ecosystems.<br />

<strong>Swiss</strong> Journal of Geosciences, 2007, V100, N1,<br />

JUN, pp 137-144.<br />

08.1-356<br />

Phosphorus and the roles of productivity and<br />

nutrient recycling during oceanic anoxic event 2<br />

Mort H P, Adatte T, Föllmi K B, Keller G, Steinmann<br />

P, Matera V, Berner Z, Stüben D<br />

Switzerland, USA, Germany<br />

Oceanography , Geology , Geochemistry & Geophysics<br />

, Paleontology<br />

Four sections documenting the impact of the late<br />

Cenomanian oceanic anoxic event (OAE 2) were<br />

studied in basins with different paleoenvironmental<br />

regimes. Accumulation rates of phosphorus<br />

(P) bound to iron, organic matter, and authigenic<br />

phosphate are shown to rise and arrive at a<br />

distinct maximum at the onset of OAE 2, with an<br />

associated increase in delta C-13 values. Accumulation<br />

rates of P return to preexcursion values in<br />

the interval where the delta C-13 record reaches<br />

its first maximum. An offset in time between the<br />

maximum in P accumulation and peaks in organic<br />

carbon burial, hydrogen indices, and C-org/P-react<br />

molar ratios is explained by the evolution of OAE 2<br />

in the following steps. (1) An increase in productivity<br />

increased the flux of organic matter and P into<br />

the sediments; the preservation of organic matter<br />

was low and its oxidation released P, which was<br />

predominantly mineralized. (2) Enhanced produc-<br />

173<br />

tivity and oxidation of organic matter created dysoxic<br />

bottom waters; the preservation potential for<br />

organic matter increased, whereas the sediment<br />

retention potential for P decreased. (3) <strong>The</strong> latter<br />

effect sustained high primary productivity, which<br />

led to an increase in the abundance of free oxygen<br />

in the ocean and atmosphere system. After the<br />

sequestration of CO 2 in the form of black shales,<br />

this oxygen helped push the ocean back into equilibrium,<br />

terminating black shale deposition and<br />

removing bioavailable P from the water column.<br />

Geology, 2007, V35, N6, JUN, pp 483-486.<br />

08.1-357<br />

<strong>The</strong> Cenomanian/Turonian anoxic event at the<br />

Bonarelli level in Italy and Spain: enhanced<br />

productivity and/or better preservation?<br />

Mort H, Jacquat O, Adatte T, Steinmann P, Föllmi K<br />

B, Matera V, Berner Z, Stüben D<br />

Switzerland, Germany<br />

Paleontology , Geology , Oceanography<br />

<strong>The</strong> upper Cenomanian pelagic sediments of Furlo<br />

in the northern Apennines, Italy, are characterized<br />

by a 1.5-m-thick organic-rich stratigraphic horizon<br />

called the Bonarelli Level, which represents<br />

the second major oceanic anoxic event in the<br />

Cretaceous (OAE 2). <strong>The</strong> Bonarelli Level is depleted<br />

in carbonates and consists essentially of biogenic<br />

quartz, phyllosilicates, and organic matter, with<br />

values of TOC reaching 18%. <strong>The</strong> age of the Furlo<br />

section is constrained by correlating its delta C-13<br />

curve with that of the well-dated Pueblo (USA)<br />

and Eastbourne (UK) sections. <strong>The</strong> presence of all<br />

the planktonic foraminiferid zones and details of<br />

the OAE 2 delta C-13 excursion indicates a relatively<br />

continuous but reduced sedimentation rate<br />

across the Cenomanian/Turonian (C/T) boundary.<br />

Sediment and TOC mass accumulation rates have<br />

been calculated and suggest a sedimentation<br />

break in the upper Bonarelli Level. This may be an<br />

artifact of the diachronous FAD of the planktonic<br />

foraminiferid Helvetoglobotruncana helvetica and<br />

suggests that in some sections the delta C-13 curve<br />

may provide more reliable age control for dating<br />

the C/T boundary. In order quantitatively to explain<br />

the carbon isotope curve and the measured<br />

TOC mass accumulation rate, a simple dynamic<br />

model of the isotope effects of organic versus inorganic<br />

carbon burial was developed. In order to<br />

verify the consistency of the model we correlated<br />

the modeled Output of the Furlo section with<br />

that of the Manilva section, in southeast Spain.<br />

<strong>The</strong> modeling shows that increasing productivity<br />

only partially explains the measured delta C-13<br />

excursion and is not the only factor relevant to<br />

black shales deposition. Preservation may play a


174 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

central role, especially in the later stages of OAE 2.<br />

Phosphorus and TOC accumulation patterns in the<br />

Bonarelli Level in both Furlo and Manilva suggest a<br />

similar process although other factors may also be<br />

involved. (c) 2007 Elsevier Ltd. All rights reserved.<br />

Cretaceous Research, 2007, V28, N4, AUG,<br />

pp 597-612.<br />

08.1-358<br />

Glacial in situ survival in the Western Alps and<br />

polytopic autopolyploidy in Biscutella laevigata<br />

L. (Brassicaceae)<br />

Parisod C, Besnard G<br />

Switzerland<br />

Cryology / Glaciology , Plant Sciences , Paleontology<br />

, Microbiology<br />

Past climatic changes and especially the ice ages<br />

have had a great impact on both the distribution<br />

and the genetic composition of plant populations,<br />

but whether they promoted speciation is still controversial.<br />

<strong>The</strong> autopolyploid complex Biscutella<br />

laevigata is a classical example of polyploidy linked<br />

to glaciations and is an interesting model to explore<br />

migration and speciation driven by climate<br />

changes in a complex alpine landscape. Diploid<br />

taxa survived the last glacial maximum in several<br />

never-glaciated areas and autotetraploids are clearly<br />

dominant in the central parts of the Alps; however,<br />

previous range-wide studies failed to identify<br />

their diploid ancestor(s). This study highlights the<br />

phylogeographical relationships of maternal lineages<br />

in the Western Alps and investigates the polyploidy<br />

process using plastid DNA sequences (trn StrnG<br />

and trnK-intron) combined with plastid DNA<br />

length polymorphism markers, which were transferable<br />

among Brassicaceae species. Twenty- one<br />

distinct plastid DNA haplotypes were distinguished<br />

in 67 populations densely sampled in the Western<br />

Alps and main lineages were identified by a median-joining<br />

network. <strong>The</strong> external Alps harboured<br />

high levels of genetic diversity, while the Central<br />

Alps contained only a subset of haplotypes due to<br />

postglacial recolonization. Several haplotypes were<br />

restricted to local peripheral refugia and evidence<br />

of in situ survival in central nunataks was detected<br />

by the presence of highly differentiated haplotypes<br />

swamped by frequent ones. As hierarchical genetic<br />

structure pointed to an independent evolution of<br />

the species in different biogeographical districts,<br />

and since tetraploids displayed haplotypes belonging<br />

to different lineages restricted to either<br />

the northern or the southern parts of the Alpine<br />

chain, polytopic autopolyploidy was also apparent<br />

in the Western Alps.<br />

Molecular Ecology, 2007, V16, N13, JUL,<br />

pp 2755-2767.<br />

08.1-359<br />

<strong>The</strong> EDC3 chronology for the EPICA dome C ice<br />

core<br />

Parrenin F, Barnola J M, Beer J, Blunier T, Castellano<br />

E, Chappellaz J, Dreyfus G, Fischer H, Fujita S,<br />

Jouzel J, Kawamura K, Lemieux Dudon B, Loulergue<br />

L, Masson Delmotte V, Narcisi B, Petit J R, Raisbeck<br />

G, Raynaud D, Ruth U, Schwander J, Severi<br />

M, Spahni R, Steffensen J P, Svensson A, Udisti R,<br />

Waelbroeck C, Wolff E<br />

France, Switzerland, Italy, Germany, Japan, Denmark,<br />

England<br />

Paleontology , Meteorology & Atmospheric Sciences<br />

, Cryology / Glaciology<br />

<strong>The</strong> EPICA (European Project for Ice Coring in<br />

Antarctica) Dome C drilling in East Antarctica has<br />

now been completed to a depth of 3260 m, at only<br />

a few meters above bedrock. Here we present the<br />

new EDC3 chronology, which is based on the use<br />

of 1) a snow accumulation and mechanical flow<br />

model, and 2) a set of independent age markers<br />

along the core. <strong>The</strong>se are obtained by pattern<br />

matching of recorded parameters to either absolutely<br />

dated paleoclimatic records, or to insolation<br />

variations. We show that this new time scale<br />

is in excellent agreement with the Dome Fuji and<br />

Vostok ice core time scales back to 100 kyr within<br />

1 kyr. Discrepancies larger than 3 kyr arise during<br />

MIS 5.4, 5.5 and 6, which points to anomalies<br />

in either snow accumulation or mechanical flow<br />

during these time periods. We estimate that EDC3<br />

gives accurate event durations within 20% (2 sigma)<br />

back to MIS11 and accurate absolute ages with<br />

a maximum uncertainty of 6 kyr back to 800 kyr.<br />

Climate of the Past, 2007, V3, N3, pp 485-497.<br />

08.1-360<br />

Palaeoceanographic and palaeoclimatic reorganization<br />

around the Middle-Late Jurassic<br />

transition<br />

Rais P, Louis Schmid B, Bernasconi S M, Weissert H<br />

Switzerland<br />

Paleontology , Oceanography , Geology<br />

A Middle to Upper Jurassic succession of submarine<br />

hardgrounds overlain by nodular limestones<br />

is exposed in the Jura mountains and in<br />

the Helvetic of the <strong>Swiss</strong> Alps. <strong>The</strong>se sediments<br />

were accumulated along the northern shelf of<br />

the cast-west trending Tethys seaway. Submarine<br />

hardgrounds and nodular limestones were also<br />

formed on the Brianconnais High, today outcropping<br />

in the middle Perminic nappe pile of the<br />

Alps. Hardgrounds record strong and persistent<br />

current activity along the northern Tethys shelf<br />

and on the Brianconnais High during the Callovian<br />

and Early Oxfordian. <strong>The</strong> transition from


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

hardgrounds to nodular limestones corresponds<br />

to a major reorganization of Tethys oceanography.<br />

<strong>The</strong> change occurred in Plicatilis ammonite Zone<br />

(Middle Oxfordian). Carbon isotope stratigraphy,<br />

calibrated against an ammonite-dated reference<br />

section in the French Subalpine Basin, serves as<br />

a correlation tool between ammonite-dated sections<br />

and successions with poor biostratigraphic<br />

resolution. Correlation demonstrates that the end<br />

of hardground formation was synchronous over<br />

wide parts of the northern Tethys. <strong>The</strong> change<br />

in shelf sedimentation coincides with a positive<br />

carbon isotope excursion with an amplitude of<br />

1.5%o. <strong>The</strong> change in Cisotope stratigraphy indicates<br />

that observed reorganization of current patterns<br />

along the northern Tethys shelf was coupled<br />

with global change in oceanography and climate.<br />

We propose that the change in northern Tethys<br />

sedimentation was caused by opening of new seaways<br />

at a time of progressive collapse of Pangaea.<br />

(c) 2007 Elsevier B.V. All rights reserved.<br />

Palaeogeography Palaeoclimatology Palaeoecology,<br />

2007, V251, N3-4, AUG 8, pp 527-546.<br />

08.1-361<br />

Direct north-south synchronization of abrupt<br />

climate change record in ice cores using Beryllium<br />

10<br />

Raisbeck G M, Yiou F, Jouzel J, Stocker T F<br />

France, Switzerland<br />

Paleontology , Meteorology & Atmospheric<br />

Sciences , Cryology / Glaciology<br />

A new, decadally resolved record of the Be-10 peak<br />

at 41 kyr from the EPICA Dome C ice core (Antarctica)<br />

is used to match it with the same peak<br />

in the GRIP ice core (Greenland). This permits a<br />

direct synchronisation of the climatic variations<br />

around this time period, independent of uncertainties<br />

related to the ice age-gas age difference<br />

in ice cores. Dansgaard-Oeschger event 10 is in the<br />

period of best synchronisation and is found to be<br />

coeval with an Antarctic temperature maximum.<br />

Simulations using a thermal bipolar seesaw model<br />

agree reasonably well with the observed relative<br />

climate chronology in these two cores. <strong>The</strong>y<br />

also reproduce three Antarctic warming events<br />

observed between A1 and A2.<br />

Climate of the Past, 2007, V3, N3, pp 541-547.<br />

175<br />

08.1-362<br />

Temporal stability of climate-isotope relationships<br />

in tree rings of oak and pine (Ticino,<br />

Switzerland)<br />

Reynolds Henne C E, Siegwolf R T W, Treydte K S,<br />

Esper J, Henne S, Saurer M<br />

Switzerland<br />

Paleontology , Plant Sciences , Forestry<br />

Climate reconstructions based on stable isotopes<br />

in tree rings commonly rely on the assumption<br />

that climate-isotope relations are stable over time.<br />

However, studies of tree ring growth have revealed<br />

trends thought to result from either physiological<br />

changes or changes in the climate-growth relationship.<br />

We investigated whether or not similar<br />

trends exist for tree ring stable isotopic ratios using<br />

a statistical approach. Correlations between<br />

climate (temperature and precipitation amount)<br />

and tree ring cellulose delta C-13 and delta O-18<br />

of oak and pine from Ticino, Switzerland, were<br />

calculated for the period AD 1660 - 2000. Climate<br />

calibration of tree rings was enabled by long-term<br />

monthly resolved temperature and precipitation<br />

data sets on the basis of instrumental and documentary<br />

proxy data. Overall, five findings have<br />

been identified: (1) Isotopic ratios in tree rings<br />

most strongly reflect conditions of the current<br />

growing season, (2) temporally stable climate signals<br />

are found in pine delta C-13 only, (3) all other<br />

correlations between tree ring isotopes and climate<br />

are temporally unstable and characterized<br />

by shifts in correlation sign and strength, (4) climate<br />

signals in oak are strongest in the 20th century,<br />

and (5) tree ring delta C-13 reflects local climatic<br />

conditions while delta O-18 is influenced by<br />

large- scale synoptic circulation. <strong>The</strong> nonstationary<br />

relationships observed could reflect changes<br />

in the relationship between the climate variables<br />

or a physiological adaptation to warmer conditions.<br />

Our results provide a cautionary note for<br />

the calibration of long tree ring series with 20th<br />

century relationships, at least for trees located at<br />

ecologically nonextreme sites.<br />

<strong>Global</strong> Biogeochemical Cycles, 2007, V21, N4, NOV<br />

2 ARTN: GB4009.<br />

08.1-363<br />

Climatic cycles during a Neoproterozoic<br />

“snowball” glacial epoch<br />

Rieu R, Allen P A, Ploetze M, Pettke T<br />

Spain, England, Switzerland<br />

Meteorology & Atmospheric Sciences , Cryology /<br />

Glaciology , Modelling , Paleontology<br />

<strong>The</strong> profound glaciations of the Neoproterozoic<br />

Cryogenian period (ca. 850-544 Ma) represent an<br />

extreme climatic mode when, it is claimed, Earth


176 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

was fully or almost completely covered with ice<br />

for millions of years. We show that the geochemistry<br />

and mineralogy of finegrained Neoproterozoic<br />

sedimentary rocks in Oman are best explained by<br />

climatic oscillations that drove variations in the<br />

intensity of chemical weathering on contemporary<br />

land surfaces. <strong>The</strong> cold climate modes of the<br />

Cryogenian were therefore cyclical, punctuated<br />

with welldefined warm-humid interglacial periods.<br />

<strong>The</strong> hydrological cycle and the routing of sediment<br />

were active throughout the glacial epoch,<br />

which requires substantial open ocean water. This<br />

reconstruction represents a significantly different<br />

target for numerical climate models at this critical<br />

time in the evolution of Earth’s biosphere.<br />

Geology, 2007, V35, N4, APR, pp 299-302.<br />

08.1-364<br />

EDML1: a chronology for the EPICA deep ice<br />

core from Dronning Maud Land, Antarctica,<br />

over the last 150 000 years<br />

Ruth U, Barnola J M, Beer J, Bigler M, Blunier T,<br />

Castellano E, Fischer H, Fundel F, Huybrechts P,<br />

Kaufmann P, Kipfstuhl S, Lambrecht A, Morganti A,<br />

Oerter H, Parrenin F, Rybak O, Severi M, Udisti R,<br />

Wilhelms F, Wolff E<br />

Germany, France, Switzerland, Italy, England, Denmark,<br />

Belgium<br />

Cryology / Glaciology , Paleontology<br />

A chronology called EDML1 has been developed<br />

for the EPICA ice core from Dronning Maud Land<br />

(EDML). EDML1 is closely interlinked with EDC3, the<br />

new chronology for the EPICA ice core from Dome-C<br />

(EDC) through a stratigraphic match between EDML<br />

and EDC that consists of 322 volcanic match points<br />

over the last 128 ka. <strong>The</strong> EDC3 chronology comprises<br />

a glaciological model at EDC, which is constrained<br />

and later selectively tuned using primary dating<br />

information from EDC as well as from EDML, the<br />

latter being transferred using the tight stratigraphic<br />

link between the two cores. Finally, EDML1 was<br />

built by exporting EDC3 to EDML. For ages younger<br />

than 41 ka BP the new synchronized time scale<br />

EDML1/EDC3 is based on dated volcanic events and<br />

on a match to the Greenlandic ice core chronology<br />

GICC05 via Be-10 and methane. <strong>The</strong> internal consistency<br />

between EDML1 and EDC3 is estimated to be<br />

typically similar to 6 years and always less than 450<br />

years over the last 128 ka (always less than 130 years<br />

over the last 60 ka), which reflects an unprecedented<br />

synchrony of time scales. EDML1 ends at 150 ka BP<br />

(2417 m depth) because the match between EDML<br />

and EDC becomes ambiguous further down. This<br />

hints at a complex ice flow history for the deepest<br />

350 m of the EDML ice core.<br />

Climate of the Past, 2007, V3, N3, pp 475-484.<br />

08.1-365<br />

Six millennia of atmospheric dust deposition<br />

in southern South America (Isla Navarino,<br />

Chile)<br />

Sapkota A, Cheburkin A K, Bonani G, Shotyk W<br />

Germany, Switzerland<br />

Paleontology , Geology<br />

To characterize dust deposition in southern<br />

South America for the Holocene, a 542 cm long<br />

core from a peat bog in southern Chile (Oreste<br />

bog. Isla Navarino) was studied. Peat formation<br />

started similar to 11 160 C-14 yr before present<br />

(BP). <strong>The</strong> titanium (Ti) concentration in bulk peat,<br />

combined with dry bulk density, and peat accumulation<br />

rate, were used to calculate the mineral<br />

accumulation rate (MAR) in the Oreste bog. <strong>The</strong><br />

distribution of calcium (Ca), manganese (Mn) and<br />

titanium (Ti) showed that mineral accumulation<br />

for the last c. 6000 yr was predominantly atmospheric<br />

with a record of effectively constant deposition<br />

(0.43 +/- 0.12g/m(2) per yr). Similarly, Ti<br />

and zirconium (Zr) concentrations in the acid<br />

insoluble ash (AIA) were also effectively constant<br />

and agreed well with the MAR for the last six millennia,<br />

except at c. 4200 cal. yr BP, where Zr was<br />

enriched relative to Ti. Here, Scanning Electron<br />

Microscope (SEM) micrographs A showed that the<br />

AIA was dominated by volcanic particles (> 20-40<br />

µm), with the Mt Burney eruption identified as<br />

the most likely source. In contrast with this anomalous<br />

zone, SEM studies showed that the mineral<br />

particles found in the majority of the sample were<br />

predominantly fine grained (< 20 ton) and rounded.<br />

Derived from surficial sediment and supplied<br />

by long-range atmospheric transport, they reflect<br />

the climate stability for the past 6000yr.<br />

Holocene, 2007, V17, N5, JUL, pp 561-572.<br />

08.1-366<br />

Siliceous algae-based seasonal temperature<br />

inference and indicator pollen tracking ca.<br />

4,000 years of climate/land use dependency in<br />

the southern Austrian Alps<br />

Schmidt R, Kamenik C, Roth M<br />

Austria, Switzerland<br />

Paleontology , Limnology , Marine & Freshwater<br />

Biology , Meteorology & Atmospheric Sciences<br />

Diatom and chrysophyte cyst-based reconstructions<br />

of the dates of spring and autumn lakemixing<br />

enabled us to estimate spring (STanom)<br />

and autumn (AT(anom)) temperature anomalies<br />

as well as ice-cover of the last ca. 4,000 years in<br />

a lake sediment core (Oberer Landschitzsee, 2,076<br />

m a.s.l.) from the southern slopes of the Austrian<br />

Central Alps. <strong>The</strong> two independently inferred temperature<br />

anomalies were significantly correlated.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

On average, spring and autumn temperatures<br />

were lower during the two millennia B.C than during<br />

0-1,300 A.D. Marked spring and autumn temperature<br />

minima occurred at about 1,300 and 600<br />

B.C. At about 1,300 A.D, STanom declined again.<br />

Spring-temperature anomalies during Roman<br />

and Medieval times equaled or slightly exceeded<br />

the modern values and paralleled tree-line and<br />

glacier fluctuations. <strong>The</strong> de-coupling of autumn<br />

and spring climates, which began during the Medieval<br />

period, might indicate changes in major<br />

circulation modes. It was assumed that the North-<br />

Atlantic influence, triggering winter-rain climate<br />

in the Northern Mediterranean, became weaker<br />

during Medieval times, resulting in a trend towards<br />

warmer autumns and overall more continental<br />

climate conditions in the study area. Four<br />

pulses of land use, inferred from indicator pollen,<br />

occurred during (1) the Early to Late Bronze, (2)<br />

the transition from Late Bronze to Early Iron Age<br />

(Hallstatt), (3) Late Iron Age (La Tene, Celtic time)<br />

to Roman times, and (4) during high to late Medieval<br />

times. Climate seemed to be an important,<br />

though complex, trigger of Alpine land use.<br />

Journal of Paleolimnology, 2007, V38, N4, NOV, pp<br />

541-554.<br />

08.1-367<br />

Synchronisation of the EDML and EDC ice<br />

cores for the last 52 kyr by volcanic signature<br />

matching<br />

Severi M, Becagli S, Castellano E, Morganti A,<br />

Traversi R, Udisti R, Ruth U, Fischer H, Huybrechts<br />

P, Wolff E, Parrenin F, Kaufmann P, Lambert F, Steffensen<br />

J P<br />

Italy, Germany, England, France, Switzerland, Denmark,<br />

Belgium<br />

Cryology / Glaciology , Paleontology<br />

A common time scale for the EPICA ice cores from<br />

Dome C (EDC) and Dronning Maud Land (EDML)<br />

has been established. Since the EDML core was not<br />

drilled on a dome, the development of the EDML1<br />

time scale for the EPICA ice core drilled in Dronning<br />

Maud Land was based on the creation of a detailed<br />

stratigraphic link between EDML and EDC,<br />

which was dated by a simpler 1D ice-flow model.<br />

<strong>The</strong> synchronisation between the two EPICA ice<br />

cores was done through the identification of several<br />

common volcanic signatures. This paper describes<br />

the rigorous method, using the signature<br />

of volcanic sulfate, which was employed for the<br />

last 52 kyr of the record. We estimated the discrepancies<br />

between the modelled EDC and EDML<br />

glaciological age scales during the studied period,<br />

by evaluating the ratio R of the apparent duration<br />

of temporal intervals between pairs of isochrones.<br />

177<br />

On average R ranges between 0.8 and 1.2 corresponding<br />

to an uncertainty of up to 20% in the<br />

estimate of the time duration in at least one of<br />

the two ice cores. Significant deviations of R up<br />

to 1.4-1.5 are observed between 18 and 28 kyr before<br />

present (BP), where present is defined as 1950.<br />

At this stage our approach does not allow us unequivocally<br />

to find out which of the models is affected<br />

by errors, but assuming that the thinning<br />

function at both sites and accumulation history<br />

at Dome C (which was drilled on a dome) are correct,<br />

this anomaly can be ascribed to a complex<br />

spatial accumulation variability (which may be<br />

different in the past compared to the present day)<br />

upstream of the EDML core.<br />

Climate of the Past, 2007, V3, N3, pp 367-374.<br />

08.1-368<br />

A high-resolution, absolute-dated deglacial<br />

speleothem record of Indian Ocean climate<br />

from Socotra Island, Yemen<br />

Shakun J D, Burns S J, Fleitmann D, Kramers J D,<br />

Matter A, Al Subary A<br />

USA, Switzerland, Germany, Yemen<br />

Paleontology , Geology , Geochemistry &<br />

Geophysics<br />

Stalagmite M1-5 from Socotra Island, Yemen in<br />

the northwest Indian Ocean provides a robust,<br />

high-resolution paleoclimate record from similar<br />

to 27.4-11.1 ka based on 717 stable isotope and 28<br />

Th-230 measurements. Variations in M1-5 oxygen<br />

isotope ratios (delta O-18) are interpreted to be<br />

primarily driven by an amount effect related to<br />

changes in the mean position and/or intensity of<br />

convection of the intertropical convergence zone,<br />

the island’s only source of precipitation. <strong>The</strong> M<br />

1-5 delta O-18 time series is strongly correlated<br />

to the Greenland ice cores, similar to an older<br />

Socotra speleothem deposited from 53-40 ka (S.J.<br />

Bums, D. Fleitmann, A. Matter, J. Kramers, A. Al-<br />

Subbary, Indian Ocean climate and an absolute<br />

chronology over Dansgaard/Oeschger events 9 to<br />

13, Science 301 (2003) 1365-1367), indicating that<br />

a North Atlantic-Indian Ocean cold-dry/warm-wet<br />

teleconnection persisted through the end of the<br />

last glacial period. Peak aridification occurred at<br />

similar to 23 ka and a gradual increase in moisture<br />

thereafter was interrupted by an abrupt drying<br />

event at similar to 16.4 ka, perhaps related to<br />

Heinrich event 1. Indian Ocean rainfall increased<br />

dramatically during the Bolling period and then<br />

decreased continuously and gradually through<br />

the Allerod and Younger Dryas. <strong>The</strong> Holocene began<br />

abruptly with increased precipitation at 11.4<br />

ka and was followed by a major but short-lived<br />

drying during the Preboreal Oscillation at similar


178 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

to 11.2 ka. M1-5 is highly correlated to the Dongge<br />

Cave record from 15.5-11 ka, suggesting much of<br />

the Indian Ocean monsoon region responded similarly<br />

to the major climate changes of the last deglaciation.<br />

<strong>The</strong> transitions into the Younger Dryas<br />

and to a lesser extent the Bolling are remarkably<br />

gradual in M1-5, as they are in all other Asian speleothem<br />

records, occurring over several centuries.<br />

<strong>The</strong>se gradual transitions are in striking contrast<br />

to high-resolution records from around the North<br />

Atlantic basin where the transitions are extremely<br />

abrupt and generally occur in under a century.<br />

This spatially variable pattern of climate change<br />

is consistent with an Atlantic origin for these deglacial<br />

climate events.<br />

Earth and Planetary Science Letters, 2007, V259,<br />

N3-4, JUL 30, pp 442-456.<br />

08.1-369<br />

Climate changes and volcanic signals during<br />

the Bronze Age: A stalagmite record<br />

Siklosy Z, Demeny A, Vennemann T W, Hegner E,<br />

Kramers J D, Leel Ossy Sz<br />

Hungary, Switzerland<br />

Geochemistry & Geophysics , Geology ,<br />

Paleontology<br />

Geochimica et Cosmochimica Acta, 2007, V71, N15,<br />

AUG, SS, p A936.<br />

08.1-370<br />

Hyalinea marmarica, a new species of benthic<br />

foraminifera from the sea of Marmara (Turkey)<br />

Spezzaferri S, Yanko Hombach V<br />

Switzerland, Canada<br />

Paleontology , Marine & Freshwater Biology<br />

Traditionally, the benthic foraminifera Hyalinea<br />

balthica (Schroter) has been considered a species<br />

with high intraspecific variability, possibly related<br />

to climatic changes, and, therefore, a potential<br />

indicator of paleoclimate in the Mediterranean<br />

Sea. However, a stable and characteristic morphology<br />

very different from the syntype of the species<br />

can be observed in specimens from the Sea<br />

of Marmara. By identification and documentation<br />

of this morphology and a subsequent comparison<br />

to specimens similar to the type species, clear<br />

differences between the two groups have been established.<br />

Hyalinea marmarica n. sp. is proposed<br />

as an example of possible environment- related<br />

speciation in benthic foraminifera. It differs from<br />

H. balthica in having less numerous chambers in<br />

the last whorl (maximum of eight), depressed sutures<br />

at least in the last four chambers, a moderate<br />

increase in chamber size as added, a subacute<br />

profile and accessory apertures on the peripheral<br />

margin. Speciation could have occurred between<br />

14 and 12 ka. At this time, increasingly efficient<br />

connections were progressively established between<br />

the Sea of Marmara and the Eastern Mediterranean<br />

Sea, allowing Hyalinea balthica to migrate<br />

into the Sea of Marmara. Here this species<br />

might have modified its morphology in response<br />

to the extreme environmental conditions.<br />

Journal of Foraminiferal Research, 2007, V37, N4,<br />

OCT, pp 309-317.<br />

08.1-371<br />

Mesolithic agriculture in Switzerland? A critical<br />

review of the evidence<br />

Tinner W, Nielsen E H, Lotter A F<br />

Switzerland, Netherlands<br />

Paleontology , Agriculture, Soil Sciences , Plant<br />

Sciences , Ecology<br />

Accumulating palaeobotanical evidence points to<br />

agricultural activity in Central Europe well before<br />

the onset of the Neolithic, commonly dated at ca<br />

5500-5200 cal BC. We reinvestigated an existing<br />

pollen profile from Soppensee with refined taxonomical<br />

resolution by further subdividing the<br />

Cerealia pollen type into Triticum t. and Avena t.<br />

because the sediments at this site currently provide<br />

the highest temporal resolution and precision<br />

for the period of interest among all sites in<br />

Switzerland. Our new results are in agreement<br />

with previous high-resolution investigations from<br />

Switzerland showing scattered but consistent<br />

presence of pollen of Cerealia, Plantago lanceolata,<br />

and other cultural plants or weeds during<br />

the late Mesolithic period (6700-5500 cal BC).<br />

Chronologically, this palynological evidence for<br />

sporadic agricultural activities coincides with a<br />

major break in material culture at ca 6700 cal BC<br />

(i.e. the transition from early to late Mesolithic).<br />

Here, we review possible arguments against palaeobotanical<br />

evidences of Mesolithic agriculture<br />

(e.g. chronological uncertainties, misidentification,<br />

contamination, long-distance transport)<br />

and conclude that none of these can explain the<br />

consistent pollen pattern observed at several sites.<br />

<strong>The</strong> palynological evidence can, of course, not<br />

prove the existence of pre-ceramic agriculture in<br />

Central Europe. However, it is so coherent that<br />

this topic should be addressed by systematic archaeolbotanical<br />

analyses in future archaeological<br />

studies. If our interpretation should turn out to<br />

be true, our conclusions would have fundamental<br />

implications for the Neolithic history of Europe.<br />

Currently, it is intensely debated whether Central<br />

European agriculture developed locally under the<br />

influence of incoming ideas from areas where<br />

Neolithic farming had already developed earlier<br />

(e.g. southeastern Europe) or whether it was in-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

troduced by immigrating farmers. On the basis<br />

of our results, we suggest that agriculture developed<br />

locally throughout the late Mesolithic and<br />

Neolithic. Mesolithic trading networks connecting<br />

Southern and Central Europe also support the<br />

hypothesis of a slow and gradual change towards<br />

sessile agriculture, probably as a result of incoming<br />

ideas and regional cultural transformation<br />

Quaternary Science Reviews, 2007, V26, N9-10,<br />

MAY, pp 1416-1431.<br />

08.1-372<br />

Signal strength and climate calibration of a<br />

European tree-ring isotope network<br />

Treydte K, Frank D, Esper J, Andreu L, Bednarz Z,<br />

Berninger F, Boettger T, Dalessandro C M, Etien N,<br />

Filot M, Grabner M, Guillemin M T, Gutierrez E,<br />

Haupt M, Helle G, Hilasvuori E, Jungner H, Kalela<br />

Brundin M, Krapiec M, Leuenberger M, Loader<br />

N J, Masson Delmotte V, Pazdur A, Pawelczyk S,<br />

Pierre M, Planells O, Pukiene R, Reynolds Henne<br />

C E, Rinne K T, Saracino A, Saurer M, Sonninen<br />

E, Stievenard M, Switsur V R, Szczepanek M,<br />

Szychowska Krapiec E, Todaro L, Waterhouse J S,<br />

Weigl M, Schleser G H<br />

Switzerland, Spain, Poland, Canada, Germany, Italy,<br />

France, Austria, Finland, Sweden, Wales, Lithuania,<br />

England<br />

Plant Sciences , Instruments & Instrumentation ,<br />

Paleontology<br />

We present the first European network of tree ring<br />

delta C-13 and delta O-18, containing 23 sites from<br />

Finland to Morocco. Common climate signals are<br />

found over broad climatic-ecological ranges. In temperate<br />

regions we find positive correlations with<br />

summer maximum temperatures and negative<br />

correlations with summer precipitation and Palmer<br />

Drought Severity Indices (PDSI) with no obvious<br />

speciesspecific differences. Regional delta C-13 and<br />

delta O-18 chronologies share high common variance<br />

in year-to-year variations. Long-term variations,<br />

however, exhibit differences that may reflect<br />

spatial variability in environmental forcings, age<br />

trends and/or plant physiological responses to increasing<br />

atmospheric CO 2 concentration. Rotated<br />

principal component analysis (RPCA) and climate<br />

field correlations enable the identification of four<br />

sub- regions in the delta O-18 network - northern<br />

and eastern Central Europe, Scandinavia and the<br />

western Mediterranean. Regional patterns in the<br />

delta C-13 network are less clear and are timescale<br />

dependent. Our results indicate that future reconstruction<br />

efforts should concentrate on delta O-18<br />

data in the identified European regions.<br />

Geophysical Research Letters, 2007, V34, N24, DEC<br />

19 ARTN: L24302.<br />

179<br />

08.1-373<br />

Oncoid growth and distribution controlled<br />

by sea-level fluctuations and climate (Late<br />

Oxfordian, <strong>Swiss</strong> Jura Mountains)<br />

Vedrine S, Strasser A, Hug W<br />

Switzerland<br />

Paleontology , Meteorology & Atmospheric Sciences<br />

, Geology<br />

Abundant lagoonal oncoids occur in the Late Oxfordian<br />

Hauptmumienbank Member of the <strong>Swiss</strong><br />

Jura Mountains. Four oncoid types are observed<br />

in the studied sections and classified according to<br />

the oncoid surface morphology, the structure and<br />

composition of the cortex, and the texture and fauna<br />

of the encasing sediment. Micrite-dominated<br />

oncoids (types 1 and 2) have a smooth surface. Type<br />

1 has a rather homogeneous cortex and occurs in<br />

moderate-energy environments. Type 2 presents<br />

continuous or discontinuous micritic laminae. It<br />

is associated with a low-diversity fauna and occurs<br />

in high-energy facies. Bacinella and Lithocodium<br />

oncoids (types 3 and 4) display a lobate surface.<br />

<strong>The</strong>y are dominated by microencrusters (Bacinella<br />

irregularis and Lithocodium aggregatum) and are<br />

found in low-energy facies. <strong>The</strong> stratigraphic and<br />

spatial distribution of these oncoid types shows a<br />

correlation with the sequence-stratigraphic evolution<br />

of the studied interval, and thus with relative<br />

sea-level fluctuations. It can be shown that<br />

these sea-level fluctuations were controlled by<br />

orbital cycles with 100- and 20-kyr periodicities.<br />

At the scale of 100- and 20-kyr sequences, types<br />

1 and 2 oncoids are preferentially found around<br />

sequence boundaries and in transgressive deposits,<br />

while types 3 and 4 oncoids are preferentially<br />

found around maximum floodings and in highstand<br />

deposits. This implies that changes of water<br />

energy and water depth were direct controlling<br />

factors. Discrepancies in oncoid distribution<br />

point to additional controlling factors. Platform<br />

morphology defines the distribution and type of<br />

the lagoon where the oncoids flourished. A low<br />

accumulation rate is required for oncoid growth.<br />

Additionally, humidity changes in the hinterland<br />

act on the terrigenous influx, which modifies water<br />

transparency and trophic level and thus plays<br />

a role in the biotic composition and diversity in<br />

the oncoid cortex.<br />

Facies, 2007, V53, N4, NOV, pp 535-552.


180 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

08.1-374<br />

Interactions between climate and vegetation<br />

during the Lateglacial period as recorded by<br />

lake and mire sediment archives in Northern<br />

Italy and Southern Switzerland<br />

Vescovi E, Ravazzi C, Arpenti E, Finsinger W, Pini R,<br />

Valsecchi V, Wick L, Ammann B, Tinner W<br />

Switzerland, Italy, Netherlands<br />

Cryology / Glaciology , Geology , Paleontology ,<br />

History<br />

We reconstruct the vegetational history of the<br />

southern side of the Alps at 18,000-10,000 cal yr BP<br />

using previous and new ANIS-dated stratigraphic<br />

records of pollen, stomata, and macrofossils. To address<br />

potential effects of climatic change on vegetation,<br />

we compare our results with independent<br />

paleoclimatic series (e.g. isotope and chironomid<br />

records from the Alps and the Alpine forelands).<br />

<strong>The</strong> period before 16,000 cal yr BP is documented<br />

only at the lowland sites. <strong>The</strong> previous studies<br />

used for comparison with our new Palughetto<br />

record, however, shows that Alpine deglaciation<br />

must have started before 18,000-17,500 cal yr BP<br />

south of the Alps and that deglaciated sites were<br />

colonized by open woods and shrublands (Juniperits,<br />

tree Betula, Larix, Pinus cembra) at ca 17,500<br />

cal yr BP. <strong>The</strong> vegetational history of a new site<br />

(Palughetto, 1040 m a.s.l.) is consistent with that<br />

of previous investigations in the study region.<br />

Our results show three conspicuous vegetational<br />

shifts delimited by statistically significant pollen<br />

zones, at ca 14,800-14,400, 13,300-12,800 and<br />

11,600-11,200 cal yr BP. At sites situated above 1000<br />

m a.s.l. (e.g. Palughetto, Pian di Gembro) forests<br />

expanded in alpine environments at ca 14,500 cal<br />

yr BP (onset of Bolling period, GI-1 in the Greenland<br />

ice record). At the same time, rather closed<br />

treeline communities of the lowlands were replaced<br />

by dense stands of Pinus sylvestris and Betula.<br />

<strong>The</strong>se early forests and shrublands consisted<br />

of Larix, P. cembra, Juniperus, P. sylvestris, Pinus<br />

mugo, and Betula, and had become established<br />

at ca 16,000 cal yr BP, probably in response to a<br />

temperature increase. If combined with other records<br />

from the Southern Alps, our data suggest<br />

that treeline ascended by ca 800-1000 m in a few<br />

centuries at most, probably as a consequence of<br />

climatic warming at the beginning of the Bolling<br />

period. At 13,100-12,800 cal yr BP the onset of a<br />

long- lasting decline of P. sylvestris was accompanied<br />

by the expansion of Quercus and other thermophilous<br />

tree taxa below ca 600 m a.s.l. This vegetational<br />

change was probably induced by a shift<br />

to warmer climatic conditions before the onset of<br />

the Younger Dryas, as indicated by independent<br />

paleoclimatic records. Only a few centuries later,<br />

at ca 12,700-12,500calyr BP, an expansion of herbaceous<br />

taxa occurred in the lowlands as well as<br />

at higher altitudes, documenting an opening of<br />

forested habitats. This change coincided with the<br />

beginning of the Younger Dryas cooling (GS-1),<br />

which according to the paleoclimatic series (e.g.<br />

oxygen isotope series), started at 12,700-12,600<br />

cal yr BP and lasted for about 1000 years. Environments<br />

south of the Alps responded markedly to<br />

climatic warming at the onset of the Holocene<br />

(11,600-11,500 cal yr BP). <strong>The</strong>rmophilous trees that<br />

had declined during the Younger Dryas re-expanded<br />

very rapidly in the lowlands and reached the<br />

high altitude sites below ca 1500 m a.s.l. within a<br />

few centuries at most. Our study implies that the<br />

synchronous vegetational changes observed over<br />

wide areas were probably a consequence of abrupt<br />

climatic shifts at the end of the Last Glacial Maximum<br />

(LGM) and during the Lateglacial. We emphasize<br />

that important vegetational changes such<br />

as the expansion of forests occurred millennia before<br />

the onset of similar processes in northwestern<br />

and central Europe.<br />

Quaternary Science Reviews, 2007, V26, N11-12,<br />

JUN, pp 1650-1669.<br />

08.1-375<br />

Primary carbonates and Ca-chloride brines as<br />

monitors of a paleo- hydrological regime in<br />

the Dead Sea basin<br />

Waldmann N, Starinsky A, Stein M<br />

Israel, Switzerland<br />

Paleontology , Geology , Meteorology & Atmospheric<br />

Sciences<br />

Lakes Samra, Lisan and the Dead Sea occupied the<br />

Dead Sea basin during the Last Interglacial (similar<br />

to 140-75ka BP), last glacial (similar to 70-14 ka<br />

BP) and Holocene periods, respectively. <strong>The</strong> age<br />

of Lake Lisan and Samra was determined by U-Th<br />

dating of primary aragonites comprising parts of<br />

the lacustrine sedimentary sequences. <strong>The</strong> lakes<br />

have periodically deposited sequences of layered<br />

calcitic marls (Lake Sarnra) or laminated primary<br />

aragonite (Lake Lisan). <strong>The</strong> deposition of aragonite<br />

as the primary carbonate phase reflects the contribution<br />

of the incoming freshwater (loaded with<br />

bi-carbonate) and high Mg-, Ca-chloride brine that<br />

originated from the subsurface vicinity of the<br />

Dead Sea basin. Deposition of calcitic marls suggests<br />

a minor effect of the brines. <strong>The</strong> Ca-chloride<br />

subsurface brine has been migrating in and out<br />

of the wall rocks of the Dead Sea basin, reflecting<br />

the regional hydrological conditions. During<br />

most of the last glacial period and during the late<br />

Holocene, sufficient precipitation above the Judea<br />

Mountains pushed the subsurface Cachloride


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

brines into the lakes causing the deposition of<br />

aragonite. During the Last Interglacial period the<br />

rain that precipitated above the Judea Mountains<br />

was insufficient to induce brine flow toward Lake<br />

Samra. It appears that sporadic floods provided<br />

calcium, bicarbonate and detritus to produce the<br />

Samra calcitic marls. Travertines deposited at the<br />

Samra-Lisan boundary indicate the early stage in<br />

the resumption of groundwater (springs) activity<br />

that led to the resurgence of Ca-chloride brine<br />

and rise of Lake Lisan. Similar variations in the<br />

regional rain precipitation and hydrological activity<br />

probably characterized the long-term geochetnical<br />

evolution of Pleistocene lacustrine waterbodies<br />

in the Dead Sea basin, enabling the use of<br />

the carbonates as paleo-hydrological monitors.<br />

Quaternary Science Reviews, 2007, V26, N17-18,<br />

SEP, pp 2219-2228.<br />

08.1-376<br />

16 000 years of vegetation and settlement history<br />

from Egelsee (Menzingen, central Switzerland)<br />

Wehrli M, Tinner W, Ammann B<br />

Switzerland<br />

Paleontology , History , Meteorology & Atmospheric<br />

Sciences , Plant Sciences<br />

Past vegetation dynamics and human impact from<br />

the Lateglacial to the present are reconstructed<br />

by pollen analysis of a core 12 in long from the<br />

raised bog Egelsee, central Switzerland (770 in<br />

a.s.l.). <strong>The</strong> depth-age model of the core is based on<br />

29 AMS C-14 dates. <strong>The</strong> oldest dated macrofinssil<br />

has an age of 13 080 +/- 105 radiocarbon yr BP (15<br />

370 cal. yr BP); extrapolation leads to a basal age<br />

of the core of 16 200 cal. yr BP. <strong>The</strong> biostratigraphy<br />

shows a typical vegetation development for<br />

Central Europe from open pioneer vegetation to<br />

Betula-Pinus forests in the Lateglacial, thermophilous<br />

mixed deciduous forests in the early Holocene,<br />

then mesophilous Abies-Fagus forests, and<br />

finally to the present cultural landscape. <strong>The</strong> initial<br />

population expansion of Abies alba may have<br />

coincided with climatic change at c. 8500 cal. yr<br />

BP. <strong>The</strong> mass expansion of Abies alba at 8 100 cal.<br />

yr BP may have been triggered by the 8.2-ka event<br />

and coincided with the empirical limit of Fagus<br />

silvatica, indicating initial population expansions.<br />

<strong>The</strong> succession of ecosystems with different<br />

plant composition is confirmed by detrended<br />

correspondence analysis (DCA): the main changes<br />

in the DCA axis I and 2 correspond to the transition<br />

phases between the different ecosystems.<br />

DCA axis I has an eigenvalue of lambda(1) = 0.46<br />

and is significantly correlated (r = 0.82) to the<br />

non-arboreal pollen percentage curve. Rarefac-<br />

181<br />

tion analysis shows a high pollen diversity in the<br />

Lateglacial, lower pollen diversity in the Holocene<br />

before human impact, and increasing pollen diversity<br />

correlated with increasing human impact.<br />

Very little is known about the archaeology of the<br />

montane belt in central Switzerland. This study<br />

provides new data concerning human impact and<br />

settlement history in this area. Human activities<br />

are indicated by cereal pollen (earliest Hordeum/<br />

Triticum type at 4700 cal. yr BP). Distinct pulses of<br />

anthropogenic forest clearances can be observed<br />

from the Neolithic period onwards.<br />

Holocene, 2007, V17, N6, SEP, pp 747-761.<br />

08.1-377<br />

Surface topography and ice flow in the vicinity<br />

of the EDML deep- drilling site, Antarctica<br />

Wesche C, Eisen O, Oerter H, Schulte D,<br />

Steinhage D<br />

Germany, Switzerland<br />

Cryology / Glaciology , Geomorphology ,<br />

Paleontology<br />

Interpretation of ice-core records requires accurate<br />

knowledge of the past and present surface<br />

topography and stress-strain fields. <strong>The</strong> European<br />

Project for Ice Coring in Antarctica (EPICA) drilling<br />

site (75.0025 degrees S, 0.0684 degrees E; 2891.7 m)<br />

in Dronning Maud Land, Antarctica, is located in<br />

the immediate vicinity of a transient and forking<br />

ice divide. A digital elevation model is determined<br />

from the combination of kinematic GPS measurements<br />

with the GLAS12 datasets from the ICESat.<br />

Based on a network of stakes, surveyed with static<br />

GPS, the velocity field around the drilling site is<br />

calculated. <strong>The</strong> annual mean velocity magnitude<br />

of 12 survey points amounts to 0.74 m a(-1). Flow<br />

directions mainly vary according to their distance<br />

from the ice divide. Surface strain rates are determined<br />

from a pentagon-shaped stake network<br />

with one center point close to the drilling site.<br />

<strong>The</strong> strain field is characterized by along-flow<br />

compression, lateral dilatation and vertical layer<br />

thinning.<br />

Journal of Glaciology, 2007, V53, N182,<br />

pp 442-448.<br />

08.1-378<br />

Leaf area index for northern and eastern<br />

North America at the Last Glacial Maximum: a<br />

data-model comparison<br />

Williams J W, Gonzales L M, Kaplan J O<br />

USA, Switzerland<br />

Paleontology , Plant Sciences , Modelling , Meteorology<br />

& Atmospheric Sciences<br />

Aim To estimate the effects of full-glacial atmospheric<br />

CO 2 concentrations and climate upon


182 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

leaf area index (LAI), using both global vegetation<br />

models and palaeoecological data. Prior simulations<br />

indicate lowered LAIs at the Last Glacial<br />

Maximum (LGM), but this is the first attempt to<br />

corroborate predictions against observations. Location<br />

Eastern North America and eastern Beringia.<br />

Methods Using a dense surface pollen data set<br />

and remotely sensed LAIs from the Moderate Resolution<br />

Imaging Spectroradiometer (MODIS) instrument,<br />

we evaluate the ability of analogue-based<br />

techniques to reconstruct modern LAIs from pollen<br />

data. We then apply analogue techniques to<br />

LGM pollen records, calculate the ratio of LGM to<br />

modern LAIs (RLAI) and compare reconstructed<br />

RLAIs to RLAIs simulated by BIOME4. Sensitivity<br />

experiments with BIOME4 distinguish the effects<br />

of CO 2 and climate on glacial LAIs. Results Modern<br />

LAIs are skilfully predicted (r(2) = 0.83). Data<br />

and BIOME4 indicate that LAIs at the LGM were up<br />

to 12% lower than modern values in eastern North<br />

America and 60-94% lower in Beringia. In eastern<br />

North America, LGM climates partially counteracted<br />

CO 2-driven decreases in LAI, while in Beringia<br />

both contributed to lowered LAIs. Main conclusions<br />

In both regions climate is the primary<br />

driver of LGM LAIs. <strong>The</strong> decline in eastern North<br />

America LAIs is smaller than previously reported,<br />

so regional vegetation feedbacks to LGM climate<br />

may have been less significant than previously<br />

supposed. CO 2 exerts both physiological and community<br />

effects upon LAI, by regulating resource<br />

availability for leaf production and by influencing<br />

the competitive balance among species and hence<br />

the composition and structure of plant communities.<br />

Pollen-based reconstructions using analogue<br />

methods do not incorporate the physiological effect<br />

and so are upper estimates of full-glacial LAIs.<br />

BIOME4 sensitivity experiments indicate that the<br />

community and physiological effects together<br />

caused 10% to 20% decrease in LAIs at the LGM, so<br />

simulated RLAIs that are 80-100% of reconstructed<br />

RLAIs are regarded as consistent with data.<br />

<strong>Global</strong> Ecology and Biogeography, 2008, V17, N1,<br />

JAN, pp 122-134.<br />

08.1-379<br />

A matter of divergence: Tracking recent warming<br />

at hemispheric scales using tree ring data<br />

Wilson R, D’arrigo R, Buckley B, Büntgen U, Esper J,<br />

Frank D, Luckman B, Payette S, Vose R, Youngblut D<br />

Scotland, USA, Switzerland, Canada<br />

Paleontology , Meteorology & Atmospheric Sciences<br />

, Plant Sciences , Forestry<br />

No current tree ring (TR) based reconstruction of<br />

extratropical Northern Hemisphere (ENH) temperatures<br />

that extends into the 1990s captures the<br />

full range of late 20th century warming observed<br />

in the instrumental record. Over recent decades,<br />

a divergence between cooler reconstructed and<br />

warmer instrumental large-scale temperatures<br />

is observed. We hypothesize that this problem is<br />

partly related to the fact that some of the constituent<br />

chronologies used for previous reconstructions<br />

show divergence against local temperatures<br />

in the recent period. In this study, we compiled TR<br />

data and published local /regional reconstructions<br />

that show no divergence against local temperatures.<br />

<strong>The</strong>se data have not been included in other<br />

large-scale temperature reconstructions. Utilizing<br />

this data set, we developed a new, completely<br />

independent reconstruction of ENH annual temperatures<br />

(1750-2000). This record is not meant to<br />

replace existing reconstructions but allows some<br />

degree of independent validation of these earlier<br />

studies as well as demonstrating that TR data can<br />

better model recent warming at large scales when<br />

careful selection of constituent chronologies is<br />

made at the local scale. Although the new series<br />

tracks the increase in ENH annual temperatures<br />

over the last few decades better than any existing<br />

reconstruction, it still slightly under predicts<br />

values in the post-1988 period. We finally discuss<br />

possible reasons why it is so difficult to model<br />

post- mid-1980s warming, provide some possible<br />

alternative approaches with regards to the instrumental<br />

target and detail several recommendations<br />

that should be followed in future large-scale<br />

reconstruction attempts that may result in more<br />

robust temperature estimates.<br />

Journal of Geophysical Research Atmospheres,<br />

2007, V112, ND17, SEP 11 ARTN: D17103.<br />

08.1-380<br />

Relation between rock uplift and denudation<br />

from cosmogenic nuclides in river sediment in<br />

the Central Alps of Switzerland<br />

Wittmann H, von Blanckenburg F, Kruesmann T,<br />

Norton K P, Kubik P W<br />

Switzerland, Germany<br />

Geology , Paleontology , Cryology / Glaciology<br />

A north-south traverse through the <strong>Swiss</strong> Central<br />

Alps reveals that denudation rates correlate with<br />

recent rock uplift rates in both magnitude and<br />

spatial distribution. This result emerges from a<br />

study of in situ-produced cosmogenic Be-10 in riverborne<br />

quartz in Central Alpine catchments. As a<br />

prerequisite, we took care to investigate the potential<br />

influence of shielding from cosmic rays due<br />

to snow, glaciers, and topographic obstructions;<br />

to calculate a possible memory from Last Glacial<br />

Maximum (LGM) glaciation; and to identify a<br />

watershed size that is appropriate for systematic


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Past <strong>Global</strong> <strong>Change</strong>s<br />

sampling. Mean denudation rates are 0.27 +/- 0.14<br />

mm/ a for the Alpine foreland and 0.9 +/- 0.3 mm/<br />

a for the crystalline Central Alps. <strong>The</strong> measured<br />

cosmogenic nuclide-derived denudation rates<br />

are in good agreement with post-LGM lake infill<br />

rates and are about twice as high as denudation<br />

rates from apatite fission track ages that record<br />

denudation from 9 to 5 Ma. In general, denudation<br />

rates are high in areas of high topography<br />

and high crustal thickness. <strong>The</strong> similarity in the<br />

spatial distribution and magnitude of denudation<br />

rates and those of rock uplift rates can be interpreted<br />

in several ways: (1) Postglacial rebound or<br />

climate change has introduced a transient change<br />

in which both uplift and denudation follow each<br />

other with a short lag time; (2) the amplitude of<br />

glacial to interglacial changes in both is small and<br />

is contained in the scatter of the data; (3) both are<br />

driven by ongoing convergence where their similarity<br />

might hint at some form of long-term quasi<br />

steady state; or (4) enhanced continuous Quaternary<br />

erosion and isostatic compensation of the<br />

mass removed accounts for the distribution of<br />

present-day rock uplift.<br />

Journal of Geophysical Research Earth Surface,<br />

2007, V112, NF4, NOV 29 ARTN: F04010.<br />

183<br />

08.1-381<br />

<strong>The</strong> prelude of the end-Permian mass extinction<br />

predates a postulated bolide impact<br />

Yin H, Feng Q, Baud A, Xie S, Benton M J, Lai X,<br />

Bottjer D J<br />

Peoples R China, Switzerland, England, USA<br />

Paleontology , Geology<br />

<strong>The</strong> mass extinction at the Permian-Triassic<br />

Boundary (PTB) is said to have been abrupt and<br />

probably caused by an extraterrestrial impact.<br />

However, evidence from the <strong>Global</strong> Stratotype Section<br />

and Point (GSSP) of the base of the Induan<br />

at Meishan, China, shows that the biotic crisis began<br />

prior to the level, in beds 25 and 26 at which<br />

the postulated impact event occurred. Evidence<br />

of such an earlier biotic crisis occurs in other sections<br />

in South China, and in central and western<br />

Tethyan regions. This event is characterized by<br />

the extinction of a range of faunas, including corals,<br />

deep-water radiolarians, most fusulinids and<br />

pseudotirolitidammonoids, and many Permian<br />

brachiopods. In all sections, this extinction level<br />

is usually a few decimeters to meters below that<br />

of the main mass extinction in the event beds (25<br />

and 26) at Meishan, and their correlatives elsewhere.<br />

This earlier extinction event happened before<br />

the postulated bolide impact at the level of<br />

beds 25 and 26, and constrains interpretation of<br />

the mechanisms that brought about this greatest<br />

mass extinction.<br />

International Journal of Earth Sciences, 2007, V96,<br />

N5, OCT, pp 903-909.


184 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Human Dimensions<br />

3 Human Dimensions<br />

08.1-382<br />

Linking extreme climate events and economic<br />

impacts: Examples from the <strong>Swiss</strong> Alps<br />

Beniston M<br />

Switzerland<br />

Modelling , Economics , Meteorology & Atmospheric<br />

Sciences<br />

This paper focuses upon topics related to current<br />

and possible future extreme weather events<br />

in order to highlight the links between climatic<br />

change and its economic impacts. Most of the examples<br />

given here are drawn from observations<br />

in Switzerland and the Alpine region that have<br />

a wealth of climatic, environmental and socioeconomic<br />

data. <strong>The</strong>se enable detailed studies to<br />

be undertaken on trends in mean and extreme<br />

climates and their impacts. Model simulations for<br />

a “greenhouse climate” suggest that risks associated<br />

with various forms of extreme events that<br />

affect the Alps may increase in the future, which<br />

could lead to high damage costs. In addition to the<br />

direct impacts of extremes, it is also necessary to<br />

take into account the increasing economic value<br />

of infrastructure located in zones potentially at<br />

risk. <strong>The</strong> final part of the paper addresses some of<br />

the issues that are related to fully integrated modeling<br />

approaches that are aimed at assessing the<br />

costs of damage in the wake of an extreme event.<br />

(C) 2007 Elsevier Ltd. All rights reserved.<br />

Energy Policy, 2007, V35, N11, NOV, pp<br />

5384-5392.<br />

08.1-383<br />

Reduced exposure to PM10 and attenuated<br />

age-related decline in lung function<br />

Downs S H, Schindler C, Liu L J S, Keidel D, Bayer<br />

Oglesby L, Brutsche M H, Gerbase M W, Keller<br />

R, Kuenzli N, Leuenberger P, Probst Hensch N M,<br />

Tschopp J M, Zellweger J P, Rochat T, Schwartz J,<br />

Ackermann Liebrich U<br />

Switzerland, USA, Spain<br />

Human & Public Health , Medicine , Meteorology &<br />

Atmospheric Sciences<br />

Background Air pollution has been associated<br />

with impaired health, including reduced lung<br />

function in adults. Moving to cleaner areas has<br />

been shown to attenuate adverse effects of air<br />

pollution on lung function in children but not<br />

in adults. Methods We conducted a prospective<br />

study of 9651 adults (18 to 60 years of age) randomly<br />

selected from population registries in 1990<br />

and assessed in 1991, with 8047 participants reassessed<br />

in 2002. <strong>The</strong>re was complete information<br />

on lung volumes and flows (e. g., forced vital capacity<br />

(FVC), forced expiratory volume in 1 second<br />

(FEV1), FEV1 as a percentage of FVC, and forced<br />

expiratory flow between 25 and 75% of the FVC<br />

(FEF25-75)), smoking habits, and spatially resolved<br />

concentrations of particulate matter that was<br />

less than 10 µm in aerodynamic diameter (PM10)<br />

from a validated dispersion model assigned to<br />

residential addresses for 4742 participants at<br />

both the 1991 and the 2002 assessments and in<br />

the intervening years. Results Overall exposure<br />

to individual home outdoor PM10 declined over<br />

the 11-year follow-up period (median, -5.3 µg per<br />

cubic meter; interquartile range, -7.5 to -4.2). In<br />

mixed-model regression analyses, with adjustment<br />

for confounders, PM10 concentrations at<br />

baseline, and clustering within areas, there were<br />

significant negative associations between the decrease<br />

in PM10 and the rate of decline in FEV1 (P<br />

= 0.045), FEV1 as a percentage of FVC (P = 0.02),<br />

and FEF25-75 (P = 0.001). <strong>The</strong> net effect of a decline<br />

of 10 µg of PM10 per cubic meter over an 11-year<br />

period was to reduce the annual rate of decline in<br />

FEV1 by 9% and of FEF25-75 by 16%. Cumulative<br />

exposure in the interval between the two examinations<br />

showed similar associations. Conclusions<br />

Decreasing exposure to airborne particulates appears<br />

to attenuate the decline in lung function related<br />

to exposure to PM10. <strong>The</strong> effects are greater<br />

in tests reflecting small-airway function.<br />

New England Journal of Medicine, 2007, V357,<br />

N23, DEC 6, pp 2338-2347.<br />

08.1-384<br />

Climate change-related health impacts in the<br />

Hindu Kush-Himalayas<br />

Ebi K L, Woodruff R, von Hildebrand A, Corvalan C<br />

USA, Australia, India, Switzerland<br />

Human & Public Health , Social Sciences<br />

Our goal was to identify the climate change-related<br />

health risks and vulnerable populations specific<br />

to the mountainous regions of the Hindu Kush-<br />

Himalayas. We reviewed published information of<br />

the likely health consequences of climate change<br />

in mountain regions, especially the findings of a<br />

workshop for countries in the Hindu Kush-Himalaya<br />

region, organized by the World Health Organization,<br />

World Meteorological Organization, United<br />

Nations Environment Programme, and United Nations<br />

Development Programme. <strong>The</strong> main climaterelated<br />

risks in the Hindu Kush-Himalaya region<br />

include the expansion of vector-borne diseases as<br />

pathogens take advantage of new habitats in altitudes<br />

that were formerly unsuitable. Diarrheal diseases<br />

could become more prevalent with changes<br />

in freshwater quality and availability. More extreme<br />

rainfall events are likely to increase the<br />

number of floods and landslides with consequent<br />

death and injuries. A unique risk is sudden floods


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Human Dimensions<br />

from high glacier lakes, which cause substantial<br />

destruction and loss of life. Because glaciers are the<br />

main source of freshwater for upland regions and<br />

downstream countries, the long-term reduction in<br />

annual glacier snowmelt is expected to heighten<br />

existing water insecurity in these areas. Climate<br />

change also is bringing some benefits to mountain<br />

populations, including milder winters and longer<br />

growing seasons. Populations in mountain regions<br />

have unique combinations of vulnerabilities to<br />

climate change. <strong>The</strong> extent of the health impacts<br />

experienced will depend on the effectiveness of<br />

public health efforts to identify and implement<br />

low-cost preparedness and response measures, and<br />

on the speed at which emissions of greenhouse gas<br />

emissions can be reduced.<br />

Ecohealth, 2007, V4, N3, SEP, pp 264-270.<br />

08.1-385<br />

Lasting management of the countryside. <strong>The</strong><br />

lessons that new regional natural parks must<br />

take from the experience of old communities<br />

Gerber J D, Rodewald R, Knoepfel P<br />

Switzerland<br />

Ecology , Social Sciences<br />

Le paysage est de plus en plus perçu comme une<br />

ressource. À ce titre, il est nécessaire de trouver<br />

des instruments juridiques, politiques ou<br />

économiques susceptibles de gérer cette « ressource-paysage<br />

» sur le long terme. Le gouvernement<br />

suisse a introduit récemment l’instrument<br />

des parcs naturels régionaux, organisés selon le<br />

modèle français, dans sa législation de protection<br />

de la nature et du paysage. Une mise en regard<br />

des nouveaux parcs avec des structures de gestion<br />

beaucoup plus anciennes, les bourgeoisies et les<br />

corporations, permet de mettre en évidence les<br />

forces et les faiblesses de chacun de ces instruments<br />

dans leur contribution à résoudre les rivalités<br />

d’usage entre acteurs utilisant ou influençant<br />

la ressource paysage. Cette comparaison permet<br />

de formuler des recommandations pratiques concernant<br />

la gestion de cette ressource.<br />

Revue de Geographie Alpine Journal of Alpine<br />

Research, 2007, V95, N3, SEP, pp 53-62.<br />

08.1-386<br />

<strong>The</strong> sustainable management of the landscape:<br />

the lessons the new regional nature<br />

parks must draw from the experience of the<br />

old corporations<br />

Gerber J D, Rodewald R, Knoepfel P<br />

Switzerland<br />

Social Sciences , Ecology<br />

<strong>The</strong> landscape is increasingly perceived as a resource.<br />

For this reason, it is necessary to find le-<br />

185<br />

gal, political and economic instruments that will<br />

succeed in managing this > in the long term. <strong>The</strong> <strong>Swiss</strong> government recently<br />

introduced the instrument of regional nature<br />

parks into the legislation governing nature<br />

and landscape preservation; the proposed parks<br />

are organized on the basis of the French model.<br />

<strong>The</strong> examination of the new parks from the perspective<br />

of much older management structures,<br />

i.e. the civic municipalities (bourgeoisies) and<br />

corporations, makes it possible to demonstrate<br />

the strengths and weaknesses of each of these instruments<br />

in their contribution to die resolution<br />

of use rivalries between actors who use or influence<br />

the resource landscape. This comparison<br />

also enables the formulation of practical recommendations<br />

regarding the management of this<br />

resource.<br />

Revue de Geographie Alpine Journal of Alpine<br />

Research, 2007, V95, N3, SEP, pp 63-74.<br />

08.1-387<br />

Recognising the complexities of ecosystem<br />

management and the ecosystem service concept<br />

Ghazoul J<br />

Switzerland<br />

Forestry , Plant Sciences , Social Sciences<br />

Ecosystem management emphasises ecosystem<br />

service concepts in order to improve land management<br />

and to justify nature conservation. This<br />

approach rests on the assumption that conserving<br />

ecosystem services can deliver net benefits<br />

for human welfare in terms of economic development.<br />

To retain credibility, the advocates of<br />

ecosystem service concepts must acknowledge<br />

the constraints that may limit the reliability of<br />

this assumption, including trade-offs with other<br />

land- use benefits. <strong>The</strong> fact that ecosystem service<br />

concepts have not been well integrated into management<br />

implies that such initiatives have not<br />

been persuasive among land managers and agriculturalists.<br />

I argue that this is due to the combination<br />

of a failure by scientists, conservationists,<br />

and other advocates of the ecosystem management<br />

approach to account for the trade-offs and<br />

opportunity costs inherent in land management,<br />

and a lack of willingness to accept that managing<br />

for ecosystem services may place constraints on<br />

future management options. However, the ecosystem<br />

service concept has the opportunity to make<br />

substantial contributions toward more effective<br />

management by influencing thinking among policy<br />

makers, land managers, and the wider public.<br />

Gaia Ecological Perspectives For Science and Society,<br />

2007, V16, N3, pp 215-221.


186 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Human Dimensions<br />

08.1-388<br />

Sink or Swim? Water security for growth and<br />

development<br />

Grey D, Sadoff C W<br />

India, Sri Lanka, Switzerland<br />

Economics , Social Sciences , Water Resources<br />

Achieving basic water security, both harnessing<br />

the productive potential of water and limiting<br />

its destructive impact, has always been a societal<br />

priority. To capture this duality, water security<br />

is defined here as the availability of an acceptable<br />

quantity and quality of water for health,<br />

livelihoods, ecosystems and production, coupled<br />

with an acceptable level of water-related risks to<br />

people, environments and economies. This paper<br />

looks broadly at those countries that have<br />

achieved water security, the paths they chose and<br />

the costs they paid, and those countries that have<br />

not achieved water security and how this constrains<br />

economies and societies. It defines three<br />

typologies: countries that have harnessed hydrology,<br />

those hampered by hydrology and those that<br />

are hostage to hydrology. It finds that countries<br />

remaining hostage to hydrology are typically<br />

among the world’s poorest. <strong>The</strong>y face “difficult”<br />

hydrologies often characterized by high inter- and<br />

intra-annual rainfall and runoff variability, where<br />

the level of institutional and infrastructure investment<br />

needed is very high and the ability to invest<br />

is low. This paper seeks to capture the dynamics<br />

of achieving water security in a hypothetical water<br />

and growth “S-curve”, which illustrates how a<br />

minimum platform of investments in water institutions<br />

and infrastructure can produce a tipping<br />

point beyond which water makes an increasingly<br />

positive contribution to growth and how that tipping<br />

point will vary in different circumstances.<br />

As there are inevitable trade-offs, achieving water<br />

security is never without social and environmental<br />

costs; in some countries these are significant,<br />

often unforeseen and even unacceptable. This<br />

brief analysis suggests that the only historically<br />

demonstrated path to achieving water security<br />

at the national level has been through investment<br />

in an evolving balance of complementary<br />

institutions and infrastructure, but that lessons<br />

exist for following this basic path in more sustainable<br />

and balanced ways. Insights are provided for<br />

balancing and sequencing investments, adapting<br />

to changing values and priorities, and pushing<br />

down the social and environmental costs. <strong>The</strong><br />

paper concludes that most water-insecure countries<br />

today face far greater challenges than those<br />

that achieved water security in the last century<br />

and are wealthy countries today. <strong>The</strong>y face more<br />

difficult hydrologies and a greater understanding<br />

of and therefore greater responsibility for, the social<br />

and environment trade-offs inherent in water<br />

management. As the costs of poor countries not<br />

achieving water security, in terms of human suffering,<br />

sustained poverty, constrained growth and<br />

social unrest, would be very high, achieving water<br />

security is a challenge that must be recognized<br />

and must be met.<br />

Water Policy, 2007, V9, N6, pp 545-571.<br />

08.1-389<br />

Carbon constraints in the fourteenth and<br />

twenty-first centuries<br />

Hoffmann V, Busch T<br />

Switzerland<br />

Economics , History<br />

Journal of Industrial Ecology, 2007, V11, N3, SUM,<br />

pp 4-6.<br />

08.1-390<br />

Assessing psycho-social effects of participatory<br />

landscape planning<br />

Höppner C, Frick J, Buchecker M<br />

Switzerland<br />

Social Sciences<br />

Participation has become an important issue in<br />

landscape planning. Within the relevant literature,<br />

an increasing number of authors emphasise<br />

the meaning of psycho-social effects such as the<br />

building of trust and engagement for planning<br />

projects. Yet, empirical studies examining psycho-social<br />

effects of participatory techniques in<br />

landscape planning are still an exception and are<br />

often conceptually and methodologically limited.<br />

<strong>The</strong> present paper addresses these gaps by adapting<br />

a mixed method design consisting of repeated<br />

measurement (n = 35) and qualitative interviews<br />

(n = 11). In the course of a municipal Landscape<br />

Development Concept (LDC) in Switzerland, short-<br />

term effects were assessed regarding participants’<br />

(a) trust in other persons involved, (b) confidence<br />

in the outcomes of the LDC, and (c) intention to<br />

participate. Significant changes were found on<br />

trust in involved persons and on the confidence<br />

in the general benefit of the LDC. <strong>The</strong> intention<br />

to participate did not change significantly. Information<br />

events had no significant effect on participants,<br />

whereas workshops had a significant effect<br />

on participants’ trust. Trust of workshop attendees<br />

decreased during the planning process, which<br />

may partly represent a shift from enthusiastic expectations<br />

to a more realistic view, and must not<br />

be regarded as a negative outcome, since it prevents<br />

participants from serious frustration. <strong>The</strong><br />

paper concludes that a long-term participation<br />

strategy, providing different participatory arenas


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Human Dimensions<br />

and settings, is essential in order to comprehensively<br />

affect all dimensions of trust and to foster<br />

engagement.<br />

Landscape and Urban Planning, 2007, V83, N2-3,<br />

NOV 19, pp 196-207.<br />

08.1-391<br />

Local learning-networks on energy efficiency<br />

in industry - Successful initiative in Germany<br />

Jochem E, Gruber E<br />

Switzerland, Germany<br />

Energy & Fuels , Political Sciences , Economics<br />

Profitable energy-efficiency potentials are often<br />

not exploited in industry since management<br />

tends not to focus on energy issues. Sharing experiences<br />

between companies reveals possibilities<br />

for reducing the transaction costs involved. For<br />

this purpose, regionally or locally-organised learning<br />

networks of companies have been established.<br />

Social mechanisms are used to motivate management<br />

to pay more attention to energy efficiency in<br />

Switzerland and Germany. <strong>The</strong> main elements of<br />

the activities include initial consultation for each<br />

company with an experienced engineer, agreement<br />

on a common target for energy-efficiency<br />

improvement, regular meetings with technical<br />

presentations and an exchange of experiences,<br />

yearly control of energy consumption and CO 2<br />

emissions as well as scientific monitoring and<br />

evaluation of the process. <strong>The</strong> results of some evaluations<br />

show that substantial progress has been<br />

made in implementing organisational measures<br />

and investments in energy efficiency in the participating<br />

companies. <strong>The</strong> reasons for these achievements<br />

are discussed and conclusions drawn about<br />

the opportunities and limits of this instrument.<br />

Finally, a recommendation is made to implement<br />

this instrument on a broader level.<br />

Applied Energy, 2007, V84, N7-8, JUL-AUG, pp<br />

806-816.<br />

08.1-392<br />

Objectives of public participation: Which actors<br />

should be involved in the decision making<br />

for river restorations?<br />

Junker B, Buchecker M, Müller Böker U<br />

Switzerland<br />

Political Sciences , Water Resources , Hydrology<br />

(1) River restoration as a measure to improve both<br />

flood protection and ecological quality has become<br />

a common practice in river management.<br />

This new practice, however, has also become a<br />

source of conflicts arising from a neglect of the<br />

social aspects in river restoration projects. <strong>The</strong>refore<br />

appropriate public involvement strategies<br />

have been recommended in recent years as a way<br />

187<br />

of coping with these conflicts. However, an open<br />

question remains: Which stakeholders should be<br />

involved in the decision-making process? This, in<br />

turn, raises the question of the appropriate objectives<br />

of public participation. This study aims to<br />

answer these questions drawing on two case studies<br />

of <strong>Swiss</strong> river restoration projects and a related<br />

representative nationwide survey. Our findings<br />

suggest that public involvement should not be restricted<br />

to a small circle of influential stakeholder<br />

groups. As restoration projects have been found<br />

to have a substantial impact on the quality of life<br />

of the local population, avoiding conflicts is only<br />

one of several objectives of the involvement process.<br />

Including the wider public provides a special<br />

opportunity to promote social objectives, such as<br />

trust building and identification of people with<br />

their local environment.<br />

Water Resources Research, 2007, V43, N10, OCT<br />

31 ARTN: W10438.<br />

08.1-393<br />

Portfolio screening to support the mainstreaming<br />

of adaptation to climate change<br />

into development assistance<br />

Klein R J T, Eriksen S E H, Naess L O, Hammill A,<br />

Tanner T M, Robledo C, O’brien K L<br />

Sweden, Norway, England, Switzerland<br />

Meteorology & Atmospheric Sciences , Economics ,<br />

Political Sciences<br />

<strong>The</strong> need to mainstream adaptation to climate<br />

change into development planning and ongoing<br />

sectoral decision-making is increasingly recognised,<br />

and several bilateral and multilateral development<br />

agencies are starting to take an interest.<br />

Over the past years at least six development agencies<br />

have screened their project portfolios, generally<br />

with two goals in mind: (1) to ascertain the<br />

extent to which existing development projects<br />

already consider climate risks or address vulnerability<br />

to climate variability and change, and (2) to<br />

identify opportunities for incorporating climate<br />

change explicitly into future projects. As each<br />

portfolio screening was conducted independently,<br />

the broader lessons emerging from the screenings<br />

have not been systematically analysed. In this<br />

paper we assess the screening activities to date,<br />

focusing on both the results and the methods<br />

applied. Based on this assessment we identify opportunities<br />

for development agencies to expand<br />

their current focus on the links between climate<br />

and development. Most agencies already consider<br />

climate change as a real but uncertain threat<br />

to future development, but they have given less<br />

thought to how different development patterns<br />

might affect vulnerability to climate change. <strong>The</strong>


188 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Human Dimensions<br />

screenings undertaken have shown the need to<br />

take a comprehensive approach to adaptation and<br />

its integration into development planning and<br />

sectoral decision-making, and a number of policy<br />

initiatives have been taken to promote such integration.<br />

We provide some initial guidance as to<br />

how portfolio screening can be carried out in a<br />

way that would allow agencies to assess systematically<br />

the relevance of climate change to their<br />

ongoing and planned development projects.<br />

Climatic <strong>Change</strong>, 2007, V84, N1, SEP, pp 23-44.<br />

08.1-394<br />

A MERGE model with endogenous technological<br />

change and the cost of carbon stabilization<br />

Kypreos S<br />

Switzerland<br />

Modelling , Economics , Meteorology & Atmospheric<br />

Sciences<br />

Two stylized backstop systems with endogenous<br />

technological learning (ETL) are introduced in the<br />

“model for evaluating regional and global effects”<br />

(MERGE): one for the electric and the other for the<br />

non- electric markets. <strong>The</strong>n the model is applied to<br />

analyze the impacts of ETL on carbon-mitigation<br />

policy, contrasting the resulting impacts with the<br />

situation without ETL. We model research and development<br />

(R&D) spending and learning subsidies<br />

for the demonstration and deployment stage as<br />

control variables, and we investigate the ability of<br />

this extra spending to create path-dependent experience<br />

and knowledge to aid in the implementation<br />

of carbon-free technologies. Based on model<br />

estimations and sensitivity analyses, we conclude<br />

that increased commitments for the development<br />

of new technologies to advance along their learning<br />

curves has a potential for substantial reductions<br />

in the cost of mitigating climate change and<br />

thereby helping to reach safe concentrations of<br />

carbon in the atmosphere. (<br />

Energy Policy, 2007, V35, N11, NOV, pp<br />

5327-5336.<br />

08.1-395<br />

Characterization of source-specific air pollution<br />

exposure for a large population-based<br />

<strong>Swiss</strong> Cohort (SAPALDIA)<br />

Liu L J S, Curjuric I, Keidel D, Heldstab J, Künzli N,<br />

Bayer Oglesby L, Ackermann Liebrich U, Schindler C<br />

Switzerland, USA, Spain<br />

Human & Public Health , Medicine<br />

BACKGROUND: Although the dispersion model approach<br />

has been used in some epidemiologic studies<br />

to examine health effects of traffic- specific air<br />

pollution, no study has evaluated the model predictions<br />

vigorously. METHODS: We evaluated total<br />

and traffic-specific particulate matter < 10 and < 2.5<br />

pm in aerodynamic diameter (PM10, PM2.5), nitrogren<br />

dioxide, and nitrogen oxide concentrations<br />

predicted by Gaussian dispersion models against<br />

fixed-site measurements at different locations,<br />

including traffic-impacted, urban-background,<br />

and alpine settings between and across cities. <strong>The</strong><br />

model predictions were then used to estimate<br />

individual subjects’ historical and cumulative exposures<br />

with a temporal trend model. RESULTS:<br />

Modeled PM10 and NO 2 predicted at least 55%<br />

and 72% of the variability of the measured PM10<br />

and NO 2, respectively. Traffic- specific pollution<br />

estimates correlated with the NOx measurements<br />

(R-2 >= 0.77) for background sites but not for traffic<br />

sites. Regional background PM10 accounted for<br />

most PM10 mass in all cities. Whereas traffic PM10<br />

accounted for < 20% of the total PM10, it varied<br />

significantly within cities. <strong>The</strong> modeling error for<br />

PM10 was similar within and between cities. Traffic<br />

NOx accounted for the majority of NOx mass in<br />

urban areas, whereas background NOx accounted<br />

for the majority of NOx in rural areas. <strong>The</strong> within-city<br />

NO 2 modeling error was larger than that<br />

between cities. CONCLUSIONS: <strong>The</strong> dispersion<br />

model predicted well the total PM10, NOx, and<br />

NO 2 and traffic-specific pollution at background<br />

sites. However, the model underpredicted traffic<br />

NOx and NO 2 at traffic sites and needs refinement<br />

to reflect local conditions. <strong>The</strong> dispersion model<br />

predictions for PM10 are suitable for examining<br />

individual exposures and health effects within<br />

and between cities.<br />

Environmental Health Perspectives, 2007, V115,<br />

N11, NOV, pp 1638-1645.<br />

08.1-396<br />

Climate risks and peak oil: Challenge for the<br />

trans disciplinary research<br />

Maibach M, Guyer M, Kläy A<br />

Switzerland<br />

Economics , Meteorology & Atmospheric Sciences ,<br />

Multidisciplinary Sciences<br />

Gaia Ecological Perspectives For Science and Society,<br />

2007, V16, N3, pp 229-231.<br />

08.1-397<br />

Does climate policy promote development?<br />

Michaelowa A, Michaelowa K<br />

Switzerland<br />

Political Sciences , Economics , Meteorology &<br />

Atmospheric Sciences<br />

Climatic <strong>Change</strong>, 2007, V84, N1, SEP, pp 1-4.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Human Dimensions<br />

08.1-398<br />

Climate or development: is ODA diverted from<br />

its original purpose?<br />

Michaelowa A, Michaelowa K<br />

Switzerland<br />

Meteorology & Atmospheric Sciences , Economics ,<br />

Political Sciences<br />

We analyze the interaction of climate and development<br />

policy that has taken place since the early<br />

1990s. Increasing dissatisfaction about the results<br />

of traditional development cooperation and the appeal<br />

of climate policy as a new policy field led to a<br />

rapid reorientation of aid flows. At the turn of the<br />

century, over 7% of aid flows were spent on greenhouse<br />

gas emissions mitigation. However, the contribution<br />

of emissions mitigation projects to the<br />

central development objective of poverty reduction<br />

as specified in the Millennium Development Goals<br />

is limited and other project types are likely to be<br />

much more effective. Adaptation to climate change<br />

can be expected to have higher synergies with poverty<br />

alleviation than mitigation, primarily through<br />

its impact on health, the conservation of arable<br />

land and the protection against natural disasters.<br />

An analysis of the Clean Development Mechanism<br />

shows that projects addressing the poor directly<br />

are very rare; even small renewable energy projects<br />

in rural areas tend to benefit rich farmers and<br />

the urban population. Use of development aid for<br />

CDM projects and / or their preparation via capacity<br />

building is thus clearly not warranted. We further<br />

analyze whether the use of development aid for climate<br />

policy could be justified as a countermeasure<br />

against the emission increase related to successful<br />

development itself. However, countries that are<br />

achieving an improvement of human development<br />

from a low level are unlikely to increase their energy<br />

consumption substantially. Only at a level where the<br />

middle class expands rapidly, energy consumption<br />

and greenhouse gas emissions soar. Thus targeting<br />

middle class energy consumption by appliance efficiency<br />

standards and public transport-friendly<br />

urban planning are the most effective measures to<br />

address developing country emissions. Rural renewable<br />

energy provision in poor countries has a much<br />

higher impact on poverty, but a much lower impact<br />

on greenhouse gas emissions. We conclude that<br />

while there are valid reasons for long-term collaboration<br />

with emerging economies on greenhouse gas<br />

mitigation, there should be a separate budget line<br />

for such activities to avoid “obfuscation” of a decline<br />

of resources aimed at poverty alleviation. Nevertheless,<br />

mitigation will remain attractive for donors because<br />

it ensures quick disbursements and relatively<br />

simple measures of success. Moreover, mitigation activities<br />

in developing countries provide politicians<br />

189<br />

in industrialized countries with a welcome strategy<br />

to divert the attention of their constituencies from<br />

the lack of success in reducing greenhouse gas emissions<br />

domestically.<br />

Climatic <strong>Change</strong>, 2007, V84, N1, SEP, pp 5-21.<br />

08.1-399<br />

Phenology of Ixodes ricinus and infection<br />

with Borrelia burgdorferi sensu lato along a<br />

North- and South-facing altitudinal gradient<br />

on Chaumont Mountain, Switzerland<br />

Moran Cadenas F, Rais O, Jouda F, Douet V, Humair<br />

P F, Moret J, Gern L<br />

Switzerland<br />

Zoology , Medicine , Meteorology & Atmospheric<br />

Sciences<br />

Questing Ixodes ricinus L. ticks were collected<br />

monthly from 2003 to 2005 on the north- and southfacing<br />

slopes of Chaumont Mountain in Neuchatel,<br />

Switzerland, at altitudes varying from 620 to 1,070<br />

in. On the south-facing slope, questing tick density<br />

was higher than on the north-facing slope, and it<br />

decreased with altitude. Density tended to increase<br />

with altitude on the north-facing slope. Saturation<br />

deficit values higher than 10 mmHg and lasting<br />

for >2 mo were often recorded on the south-facing<br />

slope, explaining seasonal patterns of questing tick<br />

activity. <strong>The</strong> overall prevalence of Borrelia burgdorferi<br />

sensu lato was 22.4%, and prevalence differed<br />

according to exposure and among years. No difference<br />

was noticed between nymphs and adults. Four<br />

Borrelia species were identified. Mixed infections<br />

were detected in 52 ticks, B. garinii and B. valaisiana<br />

(n = 21) and B. afzelii and B. burgdorferi s.s. (n<br />

= 20) were the most frequent associations observed.<br />

<strong>The</strong> density of infected ticks varied from 3.6 to 78.7<br />

infected nymphs per 1 00 m(2) and from 0.6 to 16.9<br />

infected adults per 100 m(2), both slopes combined.<br />

<strong>The</strong> study on the south-facing slope was a followup<br />

of a previous study carried out at the same location<br />

during 1999-2001. Comparison of climatic<br />

data between the two periods showed a marked<br />

increase in saturation deficit. Substantial differences<br />

in density and phenology of ticks also were<br />

observed. At high elevations, ticks were significantly<br />

more abundant during the current study. This<br />

can be explained by rising temperatures recorded<br />

during summer at altitude, reaching values similar<br />

to those registered in the first study beneath.<br />

At the lowest altitude, adults were significantly less<br />

abundant, probably due to long-lasting high saturation<br />

deficits that impaired nymphal survival. <strong>The</strong><br />

density of Borrelia-infected ticks was higher than<br />

in the previous study.<br />

Journal of Medical Entomology, 2007, V44, N4,<br />

JUL, pp 683-693.


190 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Human Dimensions<br />

08.1-400<br />

Integrated assessment of global climate<br />

change with learning-by-doing and energyrelated<br />

research and development<br />

Müller Fürstenberger G, Stephan G<br />

Germany, Switzerland<br />

Meteorology & Atmospheric Sciences , Economics ,<br />

Energy & Fuels<br />

This paper presents a small-scale version of an Integrated<br />

Assessment Model (IAM) of global climate<br />

change, which is based on a global, regionally differentiated<br />

computable general equilibrium (CGE)<br />

model with endogenous technological change.<br />

This model can be viewed as a basic framework<br />

for analyzing a broad range of economic issues related<br />

to climate change, in particular since technological<br />

change is represented in two ways: on<br />

the one hand, there is learning-by- doing (LbD) in<br />

non-fossil energy supply technologies, and on the<br />

other hand there is research and development<br />

(R&D)-driven energy- saving technical progress<br />

in production. Computational experiments are<br />

added for illustrating the role of technological<br />

innovation in a world both with and without cooperation<br />

in the solution of the global climate<br />

problem.<br />

Energy Policy, 2007, V35, N11, NOV,<br />

pp 5298-5309.<br />

08.1-401<br />

CDM potential of bagasse cogeneration in<br />

India<br />

Purohita P, Michaelowa A<br />

Germany, Switzerland<br />

Engineering , Energy & Fuels , Economics<br />

So far, the cumulative capacity of renewable energy<br />

systems such as bagasse cogeneration in India<br />

is far below their theoretical potential despite<br />

government subsidy programmes. One of the major<br />

barriers is the high investment cost of these<br />

systems. <strong>The</strong> Clean Development Mechanism<br />

(CDM) provides industrialized countries with an<br />

incentive to invest in emission reduction projects<br />

in developing countries to achieve a reduction in<br />

CO 2 emissions at lowest cost that also promotes<br />

sustainable development in the host country. Bagasse<br />

cogeneration projects could be of interest<br />

under the CDM because they directly displace<br />

greenhouse gas emissions while contributing<br />

to sustainable rural development. This study assesses<br />

the maximum theoretical as well as the<br />

realistically achievable CDM potential of bagasse<br />

cogeneration in India. Our estimates indicate<br />

that there is a vast theoretical potential of CO 2<br />

mitigation by the use of bagasse for power generation<br />

through cogeneration process in India.<br />

<strong>The</strong> preliminary results indicate that the annual<br />

gross potential availability of bagasse in India is<br />

more than 67 million tonnes (MT). <strong>The</strong> potential<br />

of electricity generation through bagasse cogeneration<br />

in India is estimated to be around 34TWh<br />

i.e. about 5575MW in terms of the plant capacity.<br />

<strong>The</strong> annual CER potential of bagasse cogeneration<br />

in India could theoretically reach 28 MT. Under<br />

more realistic assumptions about diffusion of<br />

bagasse cogeneration based on past experiences<br />

with the government-run programmes, annual<br />

CER volumes by 2012 could reach 20 26 million.<br />

<strong>The</strong> projections based on the past diffusion trend<br />

indicate that in India, even with highly favorable<br />

assumptions, the dissemination of bagasse cogeneration<br />

for power generation is not likely to reach<br />

its maximum estimated potential in another 20<br />

years. CDM could help to achieve the maximum<br />

utilization potential more rapidly as compared to<br />

the current diffusion trend if supportive policies<br />

are introduced. (C) 2007 Elsevier Ltd. All rights reserved.<br />

Energy Policy, 2007, V35, N10, OCT,<br />

pp 4779-4798.<br />

08.1-402<br />

<strong>The</strong> economic potential of bagasse cogeneration<br />

as CDM projects in Indonesia<br />

Restuti D, Michaelowa A<br />

Germany, Switzerland<br />

Economics , Energy & Fuels<br />

Surplus bagasse in Indonesian sugar mills is potential<br />

for arid- connected electricity-generating<br />

projects under Clean Development Mechanism<br />

(CDM) scheme. In addition, it is further perceived<br />

to considerably support the efforts to address<br />

prevailing crises in domestic sugar industry and<br />

power generation sector. This paper aims at analyzing<br />

the economic potential of bagasse cogeneration<br />

as CDM projects in Indonesia with the<br />

main deliverables of total emission reductions<br />

per year and Certified Emission Reduction (CFR)<br />

earnings. <strong>The</strong> analysis was made by following the<br />

applicable methodologies and based on publicly<br />

available data from official and other sources on<br />

the websites. <strong>The</strong> results show that with the electricity<br />

displacement potential at 260,253 MWh,<br />

Indonesia could generate Greenhouse Gas (GHG)<br />

emission reductions as much as 240,774 (large<br />

scale) or 198,177 tCO(2) (small scale) per annum<br />

from the recently-employed low efficiency cogeneration<br />

leading to the earnings of about US$1.36<br />

or 1.12 million, respectively. Out of 6 regional<br />

grids where the electricity from the project activities<br />

can be grid-connected, the primary emission<br />

reductions potentials are encountered in Java-Bali


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Human Dimensions<br />

and Southern Sumatera grids. Additionally, various<br />

barriers in technical, institutional, financial,<br />

and other aspects have been identified as the justifications<br />

to pass the additionality test.<br />

Energy Policy, 2007, V35, N7, JUL, pp 3952-3966.<br />

08.1-403<br />

Short-term effects of carbon monoxide on<br />

mortality: An analysis within the APHEA<br />

project<br />

Samoli E, Touloumi G, Schwartz J, Anderson H R,<br />

Schindler C, Forsberg B, Vigotti M A, Vonk J, Kosnik<br />

M, Skorkovsky J, Katsouyanni K<br />

Greece, USA, England, Switzerland, Sweden, Italy,<br />

Netherlands, Slovenia, Czech Republic<br />

Medicine , Human & Public Health<br />

OBJECTIVES: We investigated the short-term effects<br />

of carbon monoxide on total and cardiovascular<br />

mortality in 19 European cities participating<br />

in the APHEA-2 (Air Pollution and Health: A European<br />

Approach) project. METHODS: We examined<br />

the association using hierarchical models implemented<br />

in two stages. In the first stage, data from<br />

each city were analyzed separately, whereas in the<br />

second stage the city- specific air pollution estimates<br />

were regressed on city-specific covariates<br />

to obtain overall estimates and to explore sources<br />

of possible heterogeneity. We evaluated the sensitivity<br />

of our results by applying different degrees<br />

of smoothing for seasonality control in the cityspecific<br />

analysis. RESULTS: We found significant<br />

associations of CO with total and cardiovascular<br />

mortality. A 1-mg/m(3) increase in the 2-day mean<br />

of CO, levels was associated with a 1.20% (95% confidence<br />

interval (CI), 0.63-1.77%) increase in total<br />

deaths and a 1.25% (95% CI, 0.30-2.21%) increase<br />

in cardiovascular deaths. <strong>The</strong>re was indication of<br />

confounding with black smoke and nitrogen dioxide,<br />

but the pollutant- adjusted effect of CO on<br />

mortality remained at least marginally statistically<br />

significant. <strong>The</strong> effect of CO on total and cardiovascular<br />

mortality was observed mainly in western<br />

and southern European cities and was larger<br />

when the standardized mortality rate was lower.<br />

CONCLUSIONS: <strong>The</strong> results of this large study are<br />

consistent with an independent effect of CO on<br />

mortality. <strong>The</strong> heterogeneity found in the effect<br />

estimates among cities may be explained partly by<br />

specific city characteristics.<br />

Environmental Health Perspectives, 2007, V115,<br />

N11, NOV, pp 1578-1583.<br />

191<br />

08.1-404<br />

A synopsis of land use, land-use change and<br />

forestry (LULUCF) under the Kyoto Protocol<br />

and Marrakech Accords<br />

Schlamadinger B, Bird N, Johns T, Brown S,<br />

Canadell J, Ciccarese L, Dutschke M, Fiedler J,<br />

Fischlin A, Fearnside P, Forner C, Freibauer A, Frumhoff<br />

P, Hoehne N, Kirschbaum M U F, Labat A, Marland<br />

G, Michaelowa A, Montanarella L, Moutinho<br />

P, Murdiyarso D, Pena N, Pingoud K, Rakonczay Z,<br />

Rametsteiner E, Rock J, Sanz M J, Schneider U A,<br />

Shuidenko A, Skutsch M, Smith P, Somogyi Z, Trines<br />

E, Ward M, Yamagata Y<br />

Austria, USA, Australia, Italy, Germany, Switzerland,<br />

Brazil, Indonesia, Luxembourg, Finland, Belgium,<br />

Spain, Netherlands, Scotland, Hungary, New Zealand,<br />

Japan<br />

Agriculture, Soil Sciences , Political Sciences , International<br />

Relations , Meteorology & Atmospheric<br />

Sciences<br />

<strong>The</strong> complexities inherent in land use, land-use<br />

change and forestry (LULUCF) activities have led<br />

to contentious and prolonged debates about the<br />

merits of their inclusion in the 2008-2012 first<br />

commitment period of the Kyoto Protocol. Yet the<br />

inclusion of these activities played a key role in<br />

agreement on the general framework of the Kyoto<br />

Protocol, and LULUCF will likely continue to play<br />

a substantial part in negotiations on national<br />

commitments post-2012. <strong>The</strong> Marrakech Accords<br />

dictate which LULUCF activities are to be included<br />

under the Kyoto Protocol and provide rules on how<br />

they are to be accounted in the first commitment<br />

period. However, these rules have limitations and<br />

drawbacks that may be avoided in the structure<br />

of future commitments beyond 2012. Through<br />

adherence to the objectives of the United Nations<br />

Framework Convention on Climate. <strong>Change</strong> (UN-<br />

FCCC), and the incorporation of several critical<br />

features, a future framework can more effectively<br />

address the mitigation challenges and opportunities<br />

of this sector.<br />

Environmental Science Policy, 2007, V10, N4, JUN,<br />

pp 271-282.<br />

08.1-405<br />

How is climate change perceived in relation<br />

to other socioeconomic and environmental<br />

threats in Nairobi, Kenya?<br />

Shisanya C A, Khayesi M<br />

Kenya, Switzerland<br />

Social Sciences , Economics , Meteorology & Atmospheric<br />

Sciences<br />

This article examines the perception of climate<br />

change, in relation to 21 other socioeconomic<br />

and environmental problems, on the part of 132


192 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Human Dimensions<br />

respondents to a survey conducted in the city of<br />

Nairobi, Kenya. Factor analysis, used to condense<br />

these interrelated problems into a few dimensions,<br />

identified two overriding threats: the first being to<br />

socioeconomic security, and the second to the physical<br />

environment. Threats to socioeconomic security<br />

explained 76.6% of the variance in the rating of environmental<br />

and socioeconomic problems facing Nairobi,<br />

with very high factor loadings from corruption,<br />

unemployment, crime, street children, garbage,<br />

transport, poverty, pollution of Nairobi River, HIV/<br />

AIDS and immorality/promiscuity. Threats to the<br />

physical and living environment explained 22.2% of<br />

the variance in the rating of environmental and socioeconomic<br />

problems facing Nairobi. We were led<br />

to conclude that the respondents did not perceive<br />

climate change as being a significant problem in<br />

Nairobi. <strong>The</strong> global concern about climate change<br />

appeared like a mere drop in the oceanic context<br />

pervaded by problems of poverty, unemployment,<br />

crime and corruption, etc. which Nairobi faces, as<br />

does Kenya as a whole. Our conclusion is partially reflected<br />

in the priorities of the Kenyan government,<br />

which focus on poverty alleviation, the fight against<br />

crime and graft, improved access to education, and<br />

on addressing health problems; it also poses a challenge<br />

to the climate change community to find ways<br />

to making interventions relevant to local socioeconomic<br />

reality facing a developing country city like<br />

Nairobi. <strong>The</strong>re may be a need to reconsider ‘whose<br />

reality counts’ (borrowing from Robert Chambers,<br />

Whose reality counts? Putting the first last, Intermediate<br />

Technology Publications, London, p 122, 1997)<br />

in addressing climate change: should protracted<br />

Kyoto protocol negotiations be given priority or<br />

should a long lasting solution be sought to socioeconomic<br />

problems facing developing world cities such<br />

as Nairobi? We recommend that the ongoing efforts<br />

at integrating climate risk management, as components<br />

of climate-sensitive sustainable development,<br />

be studied in many settings, with a focus on the<br />

developing world which is the most vulnerable, in<br />

order to inform decision-making and development<br />

of intervention measures.<br />

Climatic <strong>Change</strong>, 2007, V85, N3-4, DEC,<br />

pp 271-284.<br />

08.1-406<br />

<strong>The</strong> future of the <strong>Swiss</strong> Alps: A participatory<br />

sustainability assessment of agricultural and<br />

landscape scenarios<br />

Soliva R<br />

Switzerland<br />

Agriculture, Soil Sciences , Social Sciences , Ecology<br />

In the <strong>Swiss</strong> Alps, as in other European Alpine<br />

regions, agricultural decline is leading to land<br />

abandonment and natural reforestation, which<br />

may have wider implications for a sustainable<br />

development of these areas. A sustainability assessment<br />

of three scenarios involving discussions<br />

with a local stakeholder group was performed<br />

as part of a case study in the <strong>Swiss</strong> canton of<br />

Grisons. <strong>The</strong> first scenario, called “liberalisation”,<br />

assumed withdrawal of all agricultural support.<br />

A second scenario, called “biodiversity”, assumed<br />

full replacement of agricultural support by biodiversity<br />

payments. <strong>The</strong>se two scenarios were compared<br />

with a “trend” scenario, i.e., continuation<br />

of current trends. <strong>The</strong> liberalisation scenario was<br />

found to have the most negative consequences<br />

on livelihoods as well as social and environmental<br />

aspects, and it was completely rejected by the<br />

local stakeholder group. <strong>The</strong> trend scenario was<br />

best received, although it does not substantially<br />

contribute to sustainable development. <strong>The</strong> biodiversity<br />

scenario was the most controversial<br />

scenario, with positive environmental outcomes<br />

but negative cultural and social consequences.<br />

Using scenarios in a participatory sustainability<br />

assessment was found helpful both as a research<br />

technique and for stimulating a debate about the<br />

future of European mountain areas.<br />

Gaia Ecological Perspectives For Science and Society,<br />

2007, V16, N2, pp 122-129.<br />

08.1-407<br />

Output and abatement effects of allocation<br />

readjustment in permit trade<br />

Sterner T, Müller A<br />

Sweden, USA, Switzerland<br />

Economics , Political Sciences , International Relations<br />

In permit trading systems, free initial allocation<br />

is common practice. A recent example is the European<br />

Union Greenhouse Gas Emission Trading<br />

Scheme (EU-ETS). We investigate effects of different<br />

free allocation schemes on incentives and<br />

identify significant perverse effects on abatement<br />

and output employing a simple multi- period<br />

model. Firms have incentives for strategic action<br />

if allocation in one period depends on their actions<br />

in previous ones and thus can be influenced<br />

by them. <strong>The</strong>se findings play a major role where<br />

trading schemes become increasingly popular<br />

as environmental or resource use policy instruments.<br />

This is of particular relevance in the EU-<br />

ETS where the current period is a trial-period<br />

before the first commitment period of the Kyoto<br />

protocol. Finally, this paper fills a gap in the literature<br />

by establishing a consistent terminology for<br />

initial allocation.<br />

Climatic <strong>Change</strong>, 2008, V86, N1-2, JAN, pp 33-49.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Human Dimensions<br />

08.1-408<br />

Does the current Clean Development Mechanism<br />

(CDM) deliver its sustainable development<br />

claim? An analysis of officially registered<br />

CDM projects<br />

Sutter C, Parreno J C<br />

Switzerland<br />

Economics , Meteorology & Atmospheric Sciences<br />

This article presents an analytical framework for<br />

analyzing Clean Development Mechanism (CDM)<br />

projects in terms of their contribution to employment<br />

generation, equal distribution of CDM<br />

returns, and improvement of local air quality. It<br />

assesses 16 officially registered CDM projects with<br />

regard to whether they fulfill the two objectives<br />

required by the Kyoto Protocol: greenhouse gas<br />

emission reductions and contribution to sustainable<br />

development in the host country. While a<br />

large part (72%) of the total portfolio’s expected<br />

Certified Emission Reductions (CERs) are likely to<br />

represent real and measurable emission reductions,<br />

less than 1% are likely to contribute significantly<br />

to sustainable development in the host<br />

country. According to our analysis, there are currently<br />

no UNFCCC registered CDM projects that<br />

are likely to fulfill the Kyoto Protocol’s twofold objective<br />

of simultaneously delivering greenhouse<br />

gas (GHG) emission reduction and contributing to<br />

sustainable development.<br />

Climatic <strong>Change</strong>, 2007, V84, N1, SEP, pp 75-90.<br />

08.1-409<br />

Technology in climate policy and climate models<br />

- Introduction<br />

Thalmann P<br />

Switzerland<br />

Modelling , Instruments & Instrumentation , Meteorology<br />

& Atmospheric Sciences , Political Sciences<br />

Energy Policy, 2007, V35, N11, NOV,<br />

pp 5263-5266.<br />

08.1-410<br />

Perceptions and evaluations of biosphere<br />

reserves by local residents in Switzerland and<br />

Ukraine<br />

Wallner A, Bauer N, Hunziker M<br />

Switzerland<br />

Social Sciences , Ecology<br />

In a cross-cultural study perceptions of local<br />

people living in the surroundings of biosphere reserves<br />

in Switzerland and Ukraine were examined<br />

using the method of qualitative interviews. In<br />

the UNESCO Biosphere Entlebuch in Switzerland<br />

people stated that they hoped for a better regional<br />

economic development due to the existence of<br />

the biosphere reserve. However, at the same time<br />

193<br />

people feared further restrictions regarding landuse.<br />

In the Carpathian Biosphere Reserve located<br />

in Transcarpathia/Ukraine people tended to connect<br />

certain conditions - such as the high price for<br />

wood - directly to the existence of the biosphere<br />

reserve, when in fact these conditions and the<br />

biosphere reserve were separate, parallel developments.<br />

In both case studies three key-categories<br />

influencing local residents’ perceptions and evaluations<br />

of biosphere reserves could be identified.<br />

<strong>The</strong>se categories are (1) the economic situation, (2)<br />

the history of nature protection, and (3) the power<br />

balance between the involved stakeholders. Paying<br />

close attention to those three categories will<br />

help planners and managers of protected areas to<br />

better understand the reasoning of local residents<br />

for or against a biosphere reserve in their area.<br />

Landscape and Urban Planning, 2007, V83, N2-3,<br />

NOV 19, pp 104-114.<br />

08.1-411<br />

<strong>The</strong> concept of sustainable development - consequences<br />

for social theory. Research desiderata<br />

and a proposal for a research strategy in<br />

social geography<br />

Zierhofer W<br />

Switzerland<br />

Economics , Social Sciences<br />

<strong>The</strong> concept of sustainable development - consequences<br />

for social theory. Research desiderata and<br />

a proposal for a research strategy in social geography<br />

According to the mainstream of modern<br />

social sciences, nature and environment are opposed<br />

to the social and not regarded as part of the<br />

disciplinary object field. This view is profoundly<br />

challenged by the regulative idea of sustainable<br />

development, since it urges reconciliation of ecological,<br />

economic and social demands. This paper<br />

discusses the state of the art of integrating nature,<br />

environment or the biophysical world into<br />

the basics of social theory. It shows further that<br />

so far the relations between society and environment<br />

have so far not been sufficiently conceptualized<br />

on the level of collective or aggregated interactions,<br />

and thus the macro-level of social theory.<br />

In respect of this research desideratum, the paper<br />

presents a research strategy, which sets out from<br />

the concept of “ecological regimes”.<br />

Erdkunde, 2007, V61, N3, JUL-SEP, pp 239-247.


194 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Mitigation and Adaptation Technologies<br />

4 Mitigation and Adaptation Technologies<br />

08.1-412<br />

<strong>The</strong>rmo-economic optimization of a solid oxide<br />

fuel cell, gas turbine hybrid system<br />

Autissier N, Palazzi F, Marechal F, van Herle J, Favrat D<br />

Switzerland<br />

Engineering , Energy & Fuels<br />

Large scale power production benefits from the<br />

high efficiency of gas-steam combined cycles.<br />

fit the lower power range, fuel cells are a good<br />

candidate to combine with gas turbines. Such<br />

systems can achieve efficiencies exceeding 60%.<br />

High-temperature solid oxide fuel cells SOFC) offer<br />

good opportunities for this coupling. In this<br />

paper a systematic method to select a design according<br />

to user specifications is presented. <strong>The</strong><br />

most attractive configurations of this technology<br />

coupling art? identified using a thermoeconomic<br />

multi-objective optimization approach. <strong>The</strong> SOFC<br />

model includes detailed computation of losses of<br />

the electrodes and thermal management. <strong>The</strong> system<br />

is integrated using pinch based methods. A<br />

thermo-econonnic approach is then used to compute<br />

the integrated system performances, size,<br />

and cost. This allows to perform the optimization<br />

of the system with regard to two objectives:<br />

minimize the specific cost and maximize the efficiency<br />

Optimization results prove the existence<br />

of designs with costs from 2400 $ / kW for a 44%<br />

efficiency to 6700 $ /kW for a 70% efficiency. Several<br />

design options are analyzed regarding, among<br />

others fuel processing, pressure ratio, or turbine<br />

inlet temperature. <strong>The</strong> model of a pressurized<br />

SOFC-mu GT hybrid cycle combines a state-of-theart<br />

planar SOFC with a high- speed micro-gas turbine<br />

sustained by air bearings.<br />

Journal of Fuel Cell Science and Technology, 2007,<br />

V4, N2, MAY, pp 123-129.<br />

08.1-413<br />

Effect of pressure and fuel-air unmixedness<br />

on NOx emissions from industrial gas turbine<br />

burners<br />

Biagioli F, Güthe F<br />

Switzerland<br />

Energy & Fuels , Engineering<br />

<strong>The</strong> effect of fuel-air unmixedness on NOx emissions<br />

from industrial lean premixed gas turbine<br />

burners fueled with natural gas is analyzed in the<br />

pressure range from 1 to 30 bar. <strong>The</strong> analysis is<br />

based on a model where NOx production is split,<br />

according to a Darnkohler number criterion, into<br />

a “prompt” (fast) contribution generated within<br />

the very narrow instantaneous heat release region<br />

(flamelet) and a “postflame” (slow) one, generated<br />

in the combustion products. Using GRIM<br />

chemical kinetics, it is found that (a) the prompt<br />

NOx contribution is approximately a factor of<br />

3 less sensitive to adiabatic flame temperature<br />

variations than postflame NOx and (b) prompt<br />

and postflame NOx change with pressure respectively<br />

according to an exponent alpha(PR) similar<br />

or equal to -0.45 and alpha(PF) similar or equal to<br />

0.67. It is shown that total NOx emissions change<br />

from being mostly of prompt type at 1 bar to being<br />

mostly of postflame type at 30 bar, so that the<br />

effect of fuel-air unmixedness on NOx emissions<br />

significantly increases with increasing pressure.<br />

<strong>The</strong> combination of these findings yields a negative<br />

NOx pressure exponent under fully premixed<br />

conditions across a rather large range of equivalence<br />

ratios but a positive one for levels of fuel-air<br />

unmixedness typical of industrial burners. This<br />

result is confirmed by the application of the NOx<br />

model in the large eddy simulation of the ALSTOM<br />

EV double cone burner, which gives, in line with<br />

experimental data, an NOx pressure exponent<br />

growing, with equivalence ratio, from similar or<br />

equal to 0.1 to similar or equal to 0.67.<br />

Combustion and Flame, 2007, V151, N1-2, OCT,<br />

pp 274-288.<br />

08.1-414<br />

Consumption and efficiency of a passenger car<br />

with a hydrogen/oxygen PEFC based hybrid<br />

electric drivetrain<br />

Büchi F N, Paganelli G, Dietrich P, Laurent D, Tsukada<br />

A, Varenne P, Delfino A, Koetz R, Freunberger<br />

S A, Magne P A, Walser D, Olsommer D<br />

Switzerland<br />

Meteorology & Atmospheric Sciences, Engineering,<br />

Energy & Fuels<br />

<strong>The</strong> main factors for reducing the consumption<br />

of a vehicle are reduction of curb weight, air drag<br />

and increase in the drivetrain efficiency. Highly<br />

efficient drivetrains can be developed based on<br />

PEFC technology and curb weight may be limited<br />

by an innovative vehicle construction. In this paper,<br />

data on consumption and efficiency of a fourplace<br />

passenger vehicle with a curb weight of 1<br />

850 kg and an H-2/O-2 fed PEFC/Supercap hybrid<br />

electric powertrain are presented. Hydrogen consumption<br />

in the New European Driving Cycle is<br />

0.67 kg H-2/100 km, which corresponds to a gasoline<br />

equivalent cosumption of 2.51/100 km. When<br />

including the energy needed to supply pure oxygen,<br />

the calculated consumption increases from<br />

0.67 to 0.69-0.79 kg H-2/100 km, depending on the<br />

method of oxygen production.<br />

Fuel Cells, 2007, V7, N4, AUG, pp 329-335.


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Mitigation and Adaptation Technologies<br />

08.1-415<br />

Flame-synthesized LaCoO3-supported Pd 2.<br />

Catalytic behavior in the reduction of NO by<br />

H-2 under lean conditions<br />

Chiarello G L, Ferri D, Grunwaldt J D, Forni L, Baiker A<br />

Italy, Switzerland<br />

Engineering , Meteorology & Atmospheric Sciences<br />

A 0.5 wt% Pd/LaCoO3, prepared by flame-spray pyrolysis<br />

(FP), was tested as catalyst for the low-temperature<br />

selective reduction of NO by H-2 in the<br />

presence of excess O-2. In particular, the effect of<br />

the precalcination and prereduction temperature<br />

on catalytic activity was compared with that of a<br />

similar Pd/LaCoO3 sample prepared by impregnation<br />

with a Pd solution of FP-prepared LaCoO3.<br />

<strong>The</strong> FP-made catalyst allowed full NO conversion<br />

at 150 degrees C, with 78% selectivity to N-2, thus<br />

outperforming the catalytic behavior of the corresponding<br />

sample prepared by impregnation.<br />

<strong>The</strong> higher activity of the FP-made catalyst has<br />

been attributed to the formation of segregated Co<br />

metal particles, not present in the impregnated<br />

sample, formed during the precalcination at 800<br />

degrees C, followed by reduction at 300 degrees C.<br />

Two reaction mechanisms can be deduced from<br />

the temperature-programmed experiments. <strong>The</strong><br />

first of these, occurring at lower temperatures, indicates<br />

cooperation between the Pd and Co metal<br />

particles, with formation of active nitrates on cobalt,<br />

successively reduced by hydrogen spillover<br />

from Pd. <strong>The</strong> second, occurring at higher temperature,<br />

allows 50% conversion of NO, with >90% selectivity<br />

to N-2, and involves N adatoms formed by<br />

dissociative NO adsorption over Pd. Prereduction<br />

at 600 degrees C led to a slight increase in catalytic<br />

activity, due to the formation of a Pd-Co alloy,<br />

which is more stable on reoxidization compared<br />

with Pd alone. Moreover, the cooperative reaction<br />

mechanism seems to be favored by the proximity<br />

of Co and Pd in metal particles.<br />

Journal of Catalysis, 2007, V252, N2, DEC 10,<br />

pp 137-147.<br />

08.1-416<br />

Flame-synthesized LaCoO3-supported Pd 1.<br />

Structure, thermal stability and reducibility<br />

Chiarello G L, Grunwaldt J D, Ferri D, Krumeich R,<br />

Oliva C, Forni L, Baiker A<br />

Italy, Switzerland<br />

Engineering , Meteorology & Atmospheric Sciences<br />

Nanosized LaCoO3 (LCO) and 0.5 wt% Pd/LaCoO3<br />

(PdLCO) were synthesized in a single step by<br />

flame-spray pyrolysis (FP) and characterized by<br />

N-2 adsorption-desorption at 77 K (BET), electron<br />

microscopy (HRTEM, STEM-EDXS), in situ XRD, in<br />

situ fluorescence XANES and EXAFS (around the<br />

195<br />

Pd K-edge), EPR, and H-2 TGA-TPR. <strong>The</strong> stability<br />

of the perovskite structure under different treatments<br />

and the location of Pd were addressed by<br />

calcination at 600 and 800 degrees C and successive<br />

reduction in 10% H-2/He to 300 and 600 degrees<br />

C. <strong>The</strong> as-prepared Pd LCO exhibited a high<br />

surface area (ca. 100 m(2)/g). Palladium appeared<br />

to be finely dispersed on the FP material and was<br />

partially incorporated in the perovskite lattice.<br />

Calcination at 800 degrees C caused sintering and<br />

substantial incorporation of Pd at the B-site of the<br />

ABO(3) framework. EXAFS revealed that the Pd-O<br />

distance was shorter than in PdO and further decreased<br />

with increasing calcination temperature,<br />

simultaneously with the appearance of a Pd-La<br />

contribution. <strong>The</strong> reduction process involved<br />

both Pd and Co. In the 100-300 degrees C range,<br />

the reduction of Co3+ to Co2+ (from LaCoO3 to<br />

La2CO 2O 5) and the segregation of Pd in the form<br />

of metal particles occurred. <strong>The</strong> reduction of Co<br />

was already reversible at 120 degrees C, and the<br />

perovskite structure was restored after exposure<br />

to oxygen. In contrast, Pd remained in the metallic<br />

state. <strong>The</strong>refore, the final structure of PdLCO<br />

after mild reoxidation consisted of Pd and Co particles<br />

supported on LaCoO3- In contrast, reduction<br />

at 600 degrees C led to the formation of a Pd-Co<br />

alloy. <strong>The</strong> composition of PdLCO reduced at different<br />

temperatures is likely to strongly influence<br />

the catalytic processes involved in combustion exhaust<br />

after treatment.<br />

Journal of Catalysis, 2007, V252, N2, DEC 10,<br />

pp 127-136.<br />

08.1-417<br />

Increase of passenger car engine efficiency<br />

with low engine-out emissions using hydrogen-natural<br />

gas mixtures: A thermodynamic<br />

analysis<br />

Dimopoulos P, Rechsteiner C, Soltic P, Laemmle C,<br />

Boulouchos K<br />

Switzerland<br />

Engineering , Energy & Fuels<br />

In this study a state of the art passenger car natural<br />

gas engine was optimised for hydrogen natural<br />

gas mixtures and high exhaust gas recirculation<br />

(EGR) rates in the part load domain. With optimal<br />

combinations of spark timing (ST) and EGR<br />

rate the achievements are significant efficiency<br />

increase with substantially lower engine-out NOx<br />

while total unburned hydrocarbons or CO-engineout<br />

emissions are not affected. Comprehensive investigations<br />

of the parameter space using design<br />

of experiments (DoE) algorithms provided a complete<br />

picture of the potential of such applications.<br />

Combustion analysis on the other hand allowed to


196 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Mitigation and Adaptation Technologies<br />

identify improvements on the basis of accelerated<br />

combustion caused by the hydrogen as well as the<br />

reduced gas exchange losses due to EGR and associated<br />

less required throttling for a given engine<br />

output. <strong>The</strong> best combinations of EGR rate, hydrogen-fraction<br />

in the fuel and ST exhibited optimal<br />

in- cylinder pressure characteristics accompanied<br />

by moderate combustion peak temperatures and<br />

low expansion cylinder temperatures. (c) 2007 International<br />

Association for Hydrogen Energy.<br />

International Journal of Hydrogen Energy, 2007,<br />

V32, N14, SI, SEP, pp 3073-3083.<br />

08.1-418<br />

Multi-regional long-term electricity supply<br />

scenarios with fusion<br />

Gnansounou E, Bednyagin D<br />

Switzerland<br />

Energy & Fuels , Engineering<br />

This paper examines the global potential for deployment<br />

of fusion power through elaboration<br />

of multi-regional long-term electricity market<br />

scenarios for the time horizon 2100. <strong>The</strong> probabilistic<br />

simulation dynamic programming model<br />

PLANELEC-Pro was applied in order to determine<br />

the expansion plans of the power generation systems<br />

in different world regions that adequately<br />

meet the projected electricity demand at minimum<br />

cost given the quality-of-service and CO 2<br />

emissions constraints. It was found that the deployment<br />

of total 330 - 950 GWe of fusion power<br />

world-wide could allow for reducing 1.8 - 4.3 % of<br />

global CO 2 emissions from electricity generation,<br />

while entailing a slight increase of levelized system<br />

electricity cost (by approx. 0.1 - 0.4 is an element<br />

of(cents)/ kWh). By the end of century, the<br />

estimated share of fusion in regional electricity<br />

mixes varies from 1.5 to 23% depending on the<br />

region. It is concluded that economic analysis of<br />

fusion technology should be complemented with<br />

the evaluation of the whole fusion RTD program<br />

in terms of social rate of return taking into account<br />

its external “spillover” benefits.<br />

Fusion Science and Technology, 2007, V52, N3,<br />

OCT, pp 388-392.<br />

08.1-419<br />

Carbothermal reduction of alumina: <strong>The</strong>rmochemical<br />

equilibrium calculations and<br />

experimental investigation<br />

Halmann M, Frei A, Steinfeld A<br />

Israel, Switzerland<br />

Engineering , Energy & Fuels<br />

<strong>The</strong> production of aluminum by the electrolytic<br />

Hall-Heroult process suffers from high energy<br />

requirements, the release of perfluorocarbons,<br />

and vast greenhouse gas emissions. <strong>The</strong> alternative<br />

carbothermic reduction of alumina, while<br />

significantly less energy- intensive, is complicated<br />

by the formation of aluminum carbide and oxycarbides.<br />

In the present work, the formation of Al,<br />

as well as Al 2OC, Al 4O 4C, and Al 4C 3 was proven by<br />

experiments on mixtures of Al 2O 3 and activated<br />

carbon in an Ar atmosphere submitted to heat<br />

pulses by an induction furnace. <strong>The</strong>rmochemical<br />

equilibrium calculations indicate that the<br />

Al 2O 3-reduction using carbon as reducing agent is<br />

favored in the presence of limited amounts of oxygen.<br />

<strong>The</strong> temperature threshold for the onset of<br />

aluminum production is lowered, the formation<br />

of Al 4C 3 is decreased, and the yield of aluminum<br />

is improved. Significant further enhancement in<br />

the carbothermic reduction of Al 2O 3 is predicted<br />

by using CH 4 as the reducing agent, again in the<br />

presence of limited amounts of oxygen. In this<br />

case, an important by-product is syngas, with a<br />

H-2/CO molar ratio of about 2, suitable for methanol<br />

or Fischer-Tropsch syntheses. Under appropriate<br />

temperature and stoichiometry of reactants,<br />

the process can be designed to be thermo-neutral.<br />

Using alumina, methane, and oxygen as reagents,<br />

the co-production of aluminum with syngas, to<br />

be converted to methanol, predicts fuel savings of<br />

about 68% and CO 2 emission avoidance of about<br />

91%, vis-A-vis the conventional production of Al<br />

by electrolysis and of methanol by steam reforming<br />

of CH 4. When using carbon (such as coke or<br />

petcoke) as reducing agent, fuel savings of 66%<br />

and CO 2 emission avoidance of 15% are predicted.<br />

Preliminary evaluation for the proposed process<br />

indicates favorable economics, and the required<br />

high temperatures process heat is readily attainable<br />

using concentrated solar energy.<br />

Energy, 2007, V32, N12, DEC, pp 2420-2427.<br />

08.1-420<br />

Secondarv effects of catalytic diesel particulate<br />

filters: Copper- induced formation of<br />

PCDD/Fs<br />

Heeb N V, Zennegg M, Gujer E, Honegger P, Zeyer<br />

K, Gfeller U, Wichser A, Kohler M, Schmid P,<br />

Emmenegger L, Ulrich A, Wenger D, Petermann J L,<br />

Czerwinski J, Mosimann T, Kasper M, Mayer A<br />

Switzerland<br />

Engineering, Meteorology & Atmospheric Sciences,<br />

Human & Public Health<br />

Potential risks of a secondary formation of polychlorinated<br />

dibenzodioxins/furans (PCDD/Fs) were<br />

assessed for two cordierite- based, wall-through<br />

diesel particulate filters (DPFs) for which soot<br />

combustion was either catalyzed with an iron- or<br />

a copper-based fuel additive. A heavy duty diesel


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Mitigation and Adaptation Technologies<br />

engine was used as test platform, applying the<br />

eightstage ISO 8178/4 C1 cycle. DPF applications<br />

neither affected the engine performance, nor did<br />

they increase NO, NO 2, CO, and CO 2 emissions.<br />

<strong>The</strong> latter is a metric for fuel consumption. THC<br />

emissions decreased by about 40% when deploying<br />

DPFs. PCDD/F emissions, with a focus on tetra-<br />

to octachlorinated congeners, were compared under<br />

standard and worst case conditions (enhanced<br />

chlorine uptake). <strong>The</strong> iron-catalyzed DPF neither<br />

increased PCDD/F emissions, nor did it change the<br />

congener pattern, even when traces of chlorine<br />

became available. In case of copper, PCDD/F emissions<br />

increased by up to 3 orders of magnitude<br />

from 22 to 200 to 12 700 pg I-TEO./L with fuels of<br />

< 2, 14, and 110 µg/g chlorine, respectively. Mainly<br />

lower chlorinated DD/Fs were formed. Based on<br />

these substantial effects on PCDD/F emissions, the<br />

copper-catalyzed DPF system was not approved for<br />

workplace applications, whereas the iron system<br />

fulfilled all the specifications of the <strong>Swiss</strong> procedures<br />

for DPF approval (VERT).<br />

Environmental Science Technology, 2007, V41,<br />

N16, AUG 15, pp 5789-5794.<br />

08.1-421<br />

Towards multi-source multi-product energy<br />

systems<br />

Hemmes K, Zachariah Wolff J L, Geidl M, Andersson<br />

G<br />

Netherlands, Switzerland<br />

Energy & Fuels , Engineering , Modelling<br />

Historically, energy conversion was seen as a onedimensional<br />

system, in the sense that one form<br />

of energy was converted into another form. Byproducts<br />

of the conversions such as heat were<br />

disregarded and/or treated as waste. Cogeneration<br />

is a first step towards system improvement since<br />

the ‘waste heat’ is recovered and used as a valuable<br />

product. Trigeneration systems, which take<br />

the concept even further, are proposed for the simultaneous<br />

production of chemicals, power, and<br />

heat, and are integrated into larger systems, such<br />

as chemical plants, to achieve increased overall<br />

performance. In these systems electricity may just<br />

be a by-product. However, co- and trigeneration<br />

systems are still characterized by a single input.<br />

In this paper we further extend this concept and<br />

explore the potential role of multi-source multiproduct<br />

(MSMP) systems.<br />

International Journal of Hydrogen Energy, 2007,<br />

V32, N10-11, JUL-AUG, pp 1332-1338.<br />

197<br />

08.1-422<br />

An energy management method for the food<br />

industry<br />

Müller D C A, Marechal F M A, Wolewinski T,<br />

Roux P J<br />

Switzerland<br />

Economics , Energy & Fuels , Engineering<br />

This article presents a method aimed at tracking<br />

energy saving opportunities in the food-processing<br />

industry through a combination of top-down<br />

and bottom-up approaches. On the one hand, the<br />

top-down modelling method aims at correlating<br />

the measured energy consumptions with the final<br />

products and auxiliaries as well as at allocating<br />

the energy bills among major consumers. This<br />

approach will, therefore, set priorities for energy<br />

saving actions. On the other hand, the bottom-up<br />

approach, which is based on the thermodynamic<br />

requirements of the process operations, is used to<br />

define the energy requirements of these consumers.<br />

A comparison of the measured consumptions<br />

and the energy requirements enables the identification<br />

of energy saving opportunities. In the case<br />

study presented in this article, these opportunities<br />

have been evaluated using thermo-economic<br />

modelling tools and range from good housekeeping<br />

measures and optimised process operations to<br />

energy saving investments.<br />

Applied <strong>The</strong>rmal Engineering, 2007, V27, N16,<br />

NOV, pp 2677-2686.<br />

08.1-423<br />

H 2O-splitting thermochemical cycle based on<br />

ZnO/Zn-redox: Quenching the effluents from<br />

the ZnO dissociation<br />

Müller R, Steinfeld A<br />

Switzerland<br />

Geochemistry & Geophysics , Engineering<br />

<strong>The</strong> production of zinc by thermal dissociation of<br />

zinc oxide has been experimentally investigated<br />

in the range of 1700-1950 K using a 10 kW solar<br />

chemical reactor directly exposed to concentrated<br />

solar radiation. <strong>The</strong> gaseous products Zn(g) and<br />

O-2 exiting the reactor underwent rapid cooling<br />

by flowing through an annular water-cooled<br />

quench unit and by injection of Ar. XRD analysis<br />

along with SEM and TEM images of the solid products<br />

deposited at the quenching zone revealed<br />

the formation of spherical particles of sizes in the<br />

0.1-30 µm range, with their surface covered with<br />

smaller edged structures, which are characteristic<br />

of Zn(g) undergoing condensation followed by<br />

Zn(l)/Zn(s) oxidation and coalescence.<br />

Chemical Engineering Science, 2008, V63, N1, JAN,<br />

pp 217-227.


198 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Mitigation and Adaptation Technologies<br />

08.1-424<br />

Towards an improved architectural quality<br />

of building integrated solar thermal systems<br />

(BIST)<br />

Munari Probst M C , Roecker C<br />

Switzerland<br />

Engineering , Energy & Fuels<br />

Architectural integration is a major issue in the<br />

development and spreading of solar thermal technologies.<br />

Yet the architectural quality of most<br />

existing building integrated solar thermal systems<br />

(BIST) is quite poor, which often discourages<br />

potential new users. In this paper, the results of<br />

a large web survey on architectural quality, addressed<br />

to more than 170 European architects<br />

and other building professionals are presented<br />

and commented. Integration criteria and design<br />

guidelines established and confirmed through<br />

the analysis of these results are proposed. Subsequently,<br />

a novel methodology to design future<br />

solar thermal collectors systems suited to building<br />

integration is described, showing a new range<br />

of design possibilities. <strong>The</strong> methodology focuses<br />

on the essential teamwork between architects and<br />

engineers to ensure both energy efficiency and<br />

architectural integrability, while playing with<br />

the formal characteristics of the collectors (size,<br />

shape, colour, etc.). Finally a practical example of<br />

such a design process conducted within the European<br />

project SOLABS is given; the resulting collector<br />

is described, and integration simulations are<br />

presented.<br />

Solar Energy, 2007, V81, N9, SI, pp 1104-1116.<br />

08.1-425<br />

Biofuels must deliver on their promise of sustainability<br />

Opal C<br />

Switzerland<br />

Energy & Fuels , Engineering<br />

Power Engineer, 2007, V21, N3, JUN-JUL, p 18.<br />

08.1-426<br />

A methodology for thermo-economic modeling<br />

and optimization of solid oxide fuel cell<br />

systems<br />

Palazzi F, Autissier N, Marechal F M A, Favrat D<br />

Switzerland<br />

Modelling , Energy & Fuels , Engineering<br />

In the context of stationary power generation, fuel<br />

cell-based systems are being foreseen as a valuable<br />

alternative to thermodynamic cycle-based power<br />

plants, especially in small scale applications. As<br />

the technology is not yet established, many aspects<br />

of fuel cell development are currently investigated<br />

worldwide. Part of the research focuses on<br />

integrating the fuel cell in a system that is both<br />

efficient and economically attractive. To address<br />

this problem, we present in this paper a thermoeconomic<br />

optimization method that systematically<br />

generates the most attractive configurations of<br />

an integrated system. In the developed methodology,<br />

the energy flows are computed using conventional<br />

process simulation software. <strong>The</strong> system is<br />

integrated using the pinch based methods that<br />

rely on optimization techniques. This defines the<br />

minimum of energy required and sets the basis to<br />

design the ideal heat exchanger network. A thermo-economic<br />

method is then used to compute the<br />

integrated system performances, sizes and costs.<br />

This allows performing the optimization of the<br />

system with regard to two objectives: minimize<br />

the specific cost and maximize the efficiency. A<br />

solid oxide fuel cell (SOFC) system of 50 kW integrating<br />

a planar SOFC is modeled and optimized<br />

leading to designs with efficiencies ranging from<br />

34% to 44%. <strong>The</strong> multi- objective optimization<br />

strategy identifies interesting system configurations<br />

and their performance for the developed<br />

SOFC system model. <strong>The</strong> methods proves to be<br />

an attractive tool to be used both as an advanced<br />

analysis tool and as support to decision makers<br />

when designing new systems.<br />

Applied <strong>The</strong>rmal Engineering, 2007, V27, N16,<br />

NOV, pp 2703-2712.<br />

08.1-427<br />

Dynamics of a solar thermochemical reactor<br />

for steam-reforming of methane<br />

Petrasch J, Steinfeld A<br />

Switzerland<br />

Engineering , Modelling , Plant Sciences<br />

A nonlinear dynamic model is developed for a<br />

steam/methane-reforming reactor that uses concentrated<br />

solar radiation as the source of high-<br />

temperature process heat. <strong>The</strong> model incorporates<br />

a set of lumped- parameter reservoirs for mass and<br />

energy. For each reservoir, the unsteady mass and<br />

energy conservation equations are formulated,<br />

which couple conduction, convection, and radiation<br />

heat transfer with the temperature dependent<br />

chemical conversion. Radiative exchange,<br />

the dominant heat transfer mode at above 800 K,<br />

is solved by a band- approximation Monte Carlo<br />

technique. <strong>The</strong> dynamic model is applied to predict<br />

the transient behavior of a 400kW prototype<br />

solar reformer in operational modes of purging,<br />

thermal testing, startup, chemical reaction, shutdown,<br />

and cyclical operation. Time constants vary<br />

between 2 s for species transport and 1 x 10(5) s for<br />

thermal energy transport through ceramic insulation.<br />

Validation is accomplished by comparing


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Mitigation and Adaptation Technologies<br />

modeled and experimentally measured outlet gas<br />

temperatures obtained from reactor tests in a solar<br />

tower facility.<br />

Chemical Engineering Science, 2007, V62, N16,<br />

AUG, pp 4214-4228.<br />

08.1-428<br />

Development steps for parabolic trough solar<br />

power technologies with maximum impact on<br />

cost reduction<br />

Pitz P R, Dersch J, Milow B, Tellez F, Ferriere A,<br />

Langnickel U, Steinfeld A, Karni J, Zarza E, Popel O<br />

Germany, Spain, France, Switzerland, Israel, Russia<br />

Energy & Fuels , Engineering<br />

Besides continuous implementation of concentrating<br />

solar power plants (CSP) in Europe, which<br />

stipulate cost reduction by mass production effects,<br />

further R&D activities are necessary to<br />

achieve the cost competitiveness to fossil power<br />

generation. <strong>The</strong> European Concentrated Solar<br />

<strong>The</strong>rmal Roadmap (ECOSTAR) study that was conducted<br />

by European research institutes in the field<br />

of CSP intends to stipulate the direction for R&D<br />

activities in the context of cost reduction. This paper<br />

gives an overview about the methodology and<br />

the results for one of the seven different CSP system<br />

concepts that are currently under promotion<br />

worldwide and considered within ECOSTAR. <strong>The</strong><br />

technology presented here is the Parabolic trough<br />

with direct steam generation (DSG), which may be<br />

considered as an evolution of the existing parabolic<br />

systems with thermal oil as heat transfer<br />

fluid. <strong>The</strong> methodology is explained using this exemplary<br />

system, and the technical improvements<br />

are evaluated according to their cost- reduction<br />

potential using a common approach, based on an<br />

annual performance model. Research priorities<br />

are given based on the results. <strong>The</strong> simultaneous<br />

implementation of three measures is required in<br />

order to achieve the cost-reduction target: Technical<br />

improvement by R&D, upscaling of the unit<br />

size, and mass production of the equipment.<br />

Journal of Solar Energy Engineering Transactions of<br />

the Asme, 2007, V129, N4, NOV, pp 371-377.<br />

08.1-429<br />

Optimum battery size for fuel cell hybrid electric<br />

vehicle - Part I<br />

Sundstrom O, Stefanopoulou A<br />

Switzerland, USA<br />

Energy & Fuels , Engineering<br />

This study explores different hybridization levels<br />

of a midsized vehicle powered by a polymer<br />

electrolyte membrane fuel cell stack. <strong>The</strong> energy<br />

buffer considered is a lead-acid-type battery. <strong>The</strong><br />

effects of the battery size on the overall energy<br />

199<br />

losses for different drive cycles are determined<br />

when dynamic programming determines the optimal<br />

current drawn from the fuel cell system.<br />

<strong>The</strong> different hybridization levels are explored<br />

for two cases: (i) when the batter), is only used<br />

to decouple the fuel cell system from the voltage<br />

and current demands from the traction motor to<br />

allow the, fuel cell system to operate as close to<br />

optimally as possible and (ii) when regenerative<br />

braking is included in the vehicle with different<br />

efficiencies. <strong>The</strong> optimal power-split policies are<br />

analyzed to quantify all the energy losses and<br />

their paths in an effort to clarify the hybridization<br />

needs for a fuel cell vehicle. Results show that<br />

without any regenerative braking, hybridization<br />

will not decrease, fuel consumption unless the<br />

vehicle is driving in a mild drive cycle (city drive<br />

with low speeds) . However, when the efficiency of<br />

the regenerative braking increases, the fuel consumption<br />

(total energy losses) can be significantly<br />

lowered by choosing an optimal battery size.<br />

Journal of Fuel Cell Science and Technology, 2007,<br />

V4, N2, MAY, pp 167-175.<br />

08.1-430<br />

Optimum Battery Size for Fuel Cell Hybrid<br />

Electric Vehicle With Transient Loading Consideration—Part<br />

II<br />

Sundstrom O, Stefanopoulou A<br />

Switzerland, USA<br />

Engineering , Energy & Fuels<br />

This study presents a simplified model of a midsized<br />

vehicle powered by a polymer electrolyte<br />

membrane fuel cell stack together with a leadacid<br />

battery as an energy buffer. <strong>The</strong> model is<br />

used with dynamic programming in order to<br />

find the optimal coordination of the two power<br />

sources while penalizing transient excursions<br />

in oxygen concentration in the fuel cell and the<br />

state of charge in the battery. <strong>The</strong> effects of the<br />

battery size on the overall energy losses for different<br />

drive cycles are determined, and the optimal<br />

power split policies are analyzed to quantify<br />

all the energy losses and their paths in an ‘effort<br />

to clarify the hybridization needs for a fuel cell<br />

vehicle with constraints on dynamically varying<br />

variables. Finally, a causal nonpredictive controller<br />

is presented. <strong>The</strong> battery sizing results from<br />

the dynamic programming optimizations and the<br />

causal controller are compared.<br />

Journal of Fuel Cell Science and Technology, 2007,<br />

V4, N2, MAY, pp 176-184.


200 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | General Topics<br />

5 General Topics<br />

08.1-431<br />

What is a green solvent? A comprehensive<br />

framework for the environmental assessment<br />

of solvents<br />

Capello C, Fischer U, Hungerbühler K<br />

Switzerland<br />

Economics<br />

Solvents define a major part of the environmental<br />

performance of processes in chemical industry<br />

and also impact on cost, safety and health issues.<br />

<strong>The</strong> idea of “green’’ solvents expresses the goal<br />

to minimize the environmental impact resulting<br />

from the use of solvents in chemical production.<br />

Here the question is raised of how to measure how<br />

“green’’ a solvent is. We propose a comprehensive<br />

framework for the environmental assessment of<br />

solvents that covers major aspects of the environmental<br />

performance of solvents in chemical production,<br />

as well as important health and safety<br />

issues. <strong>The</strong> framework combines the assessment<br />

of substance-specific hazards with the quantification<br />

of emissions and resource use over the full<br />

life-cycle of a solvent. <strong>The</strong> proposed framework<br />

is demonstrated on 26 organic solvents. Results<br />

show that simple alcohols (methanol, ethanol) or<br />

alkanes (heptane, hexane) are environmentally<br />

preferable solvents, whereas the use of dioxane,<br />

acetonitrile, acids, formaldehyde, and tetrahydrofuran<br />

is not recommendable from an environmental<br />

perspective. Additionally, a case study is<br />

presented in which the framework is applied for<br />

the assessment of various alcohol -water or pure<br />

alcohol mixtures used for solvolysis of p-methoxybenzoyl<br />

chloride. <strong>The</strong> results of this case study<br />

indicate that methanol - water or ethanol -water<br />

mixtures are environmentally favourable compared<br />

to pure alcohol or propanol water mixtures.<br />

<strong>The</strong> two applications demonstrate that the presented<br />

framework is a useful instrument to select<br />

green solvents or environmentally sound solvent<br />

mixtures for processes in chemical industry. <strong>The</strong><br />

same framework can also be used for a comprehensive<br />

assessment of new solvent technologies as<br />

soon as the present lack of data can be overcome.<br />

Green Chemistry, 2007, V9, N9, pp 927-934.<br />

08.1-432<br />

Effect of solar water disinfection (SODIS) on<br />

model microorganisms under improved and<br />

field SODIS conditions<br />

Dejung S, Fuentes I, Almanza G, Jarro R, Navarro L,<br />

Arias G, Urquieta E, Torrico A, Fenandez W, Iriarte<br />

M, Birrer C, Stahel W A, Wegelin M<br />

Switzerland<br />

Water Resources , Microbiology , Modelling ,<br />

Engineering<br />

SODIS is a solar water disinfection process which<br />

works by exposing untreated water to the sun in<br />

plastic bottles. Field experiments were carried<br />

out in Cochabamba, Bolivia, to obtain standard<br />

UV-A (320-405 nm) dose values required to inactivate<br />

non-spore forming bacteria, spores of Bacillus<br />

subtilis, and wild type coliphages. inactivation<br />

kinetics for non-spore forming bacteria are<br />

similar under SODIS conditions, exhibiting dose<br />

values ranging between 15 and 30 Wh m(-2) for 1<br />

log(10) (90%) inactivation, 45 to 90 Wh m(-2) for 3<br />

log(10) (99.9%), and 90 to 180 Wh m(-2) for 6 log(10)<br />

(99.9999%) inactivation. Pseudomonas aeruginosa<br />

was found to be the most resistant and Salmonella<br />

typhi, the most sensitive of the non- sporulating<br />

organisms studied here. Phages and spores serve<br />

as model organisms for viruses and parasite cysts.<br />

A UV-A dose of 85 to 210 wh m(-2) accumulated<br />

during one to two days was enough to inactivate 1<br />

log(10) (90%) of these strong biological structures.<br />

<strong>The</strong> process of SODIS depended mainly on the radiation<br />

dose (Wh m(-2)) an organism was exposed<br />

to. An irradiation intensity exceeding some 12 W<br />

m(-2) did not increase the inactivation constant. A<br />

synergistic effect of water temperatures below 50<br />

degrees C was not observed. Data plotting from<br />

various experiments on a single graph proved to<br />

be a reliable alternative method for analysis. inactivation<br />

rates determined by this method were revealed<br />

to be within the same range as individual<br />

analysis.<br />

Journal of Water Supply Research and Technology<br />

Aqua, 2007, V56, N4, JUN, pp 245-256.<br />

08.1-433<br />

Cumulative energy extraction from the natural<br />

environment (CEENE): a comprehensive life<br />

cycle impact assessment method for resource<br />

accounting<br />

Dewulf J, Bosch M E, de Meester B, van der Vorst<br />

G, van Langenhove H, Hellweg S, Huijbregts M A J<br />

Belgium, Switzerland, Netherlands<br />

Energy & Fuels , Ecology<br />

<strong>The</strong> objective of the paper is to establish a comprehensive<br />

resource- based life cycle impact assessment<br />

(LCIA) method which is scientifically<br />

sound and that enables to assess all kinds of resources<br />

that are deprived from the natural ecosystem,<br />

all quantified on one single scale, free of<br />

weighting factors. <strong>The</strong> method is based on the<br />

exergy concept. Consistent exergy data on fossils,<br />

nuclear and metal ores, minerals, air, water, land<br />

occupation, and renewable energy sources were<br />

elaborated, with well defined system boundaries.<br />

Based on these data, the method quantifies the exergy<br />

“taken away” from natural ecosystems, and is


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | General Topics<br />

thus called the cumulative exergy extraction from<br />

the natural environment (CEENE). <strong>The</strong> acquired<br />

data set was coupled with a state-of-the art life<br />

cycle inventory database, ecoinvent. In this way,<br />

the method is able to quantitatively distinguish<br />

eight categories of resources withdrawn from the<br />

natural environment: renewable resources, fossil<br />

fuels, nuclear energy, metal ores, minerals, water<br />

resources, land resources, and atmospheric resources.<br />

Third, the CEENE method is illustrated<br />

for a number of products that are available in ecoinvent,<br />

and results are compared with common<br />

resource oriented LCIA methods. <strong>The</strong> application<br />

to the materials in the ecoinvent database showed<br />

that fossil resources and land use are of particular<br />

importance with regard to the total CEENE score,<br />

although the other resource categories may also<br />

be significant.<br />

Environmental Science Technology, 2007, V41,<br />

N24, DEC 15, pp 8477-8483.<br />

08.1-434<br />

<strong>The</strong> environmental relevance of capital goods<br />

in life cycle assessments of products and<br />

services<br />

Frischknecht R, Althaus H J, Bauer C, Doka G, Heck<br />

T, Jungbluth N, Kellenberger D, Nemecek T<br />

Switzerland<br />

Economics<br />

Goal and Scope. Many life cycle assessment case<br />

studies neglect the production of capital goods<br />

that are necessary to manufacture a good or to<br />

provide a service. In ISO standards 14040 and<br />

14044 the capital goods are explicitly part of the<br />

product system. Thus, it is doubtful if capital<br />

goods can be excluded per se as has been done<br />

in quite a number of case studies and LCA databases.<br />

<strong>The</strong>re is yet no clear idea about if and when<br />

capital goods play an important role in life cycle<br />

assessments. <strong>The</strong> present paper evaluates the contribution<br />

of capital goods in a large number and<br />

variety of product and service systems. A classification<br />

of product and service groups is proposed<br />

to give better guidance on when and where capital<br />

goods should be included or can be neglected.<br />

Methods. <strong>The</strong> life cycle inventory database ecoinvent<br />

data v1.2 forms the basis for the assessment<br />

of the environmental importance of capital goods.<br />

<strong>The</strong> importance is assessed on the basis of several<br />

hundreds of cradle-to-gate LCAs of heat and electricity<br />

supply systems, of materials extraction<br />

and production, of agricultural products, and of<br />

transport and waste management services. <strong>The</strong><br />

importance within product (and service) groups is<br />

evaluated with statistical methods by comparing<br />

the LCA results including and excluding capital<br />

201<br />

goods. <strong>The</strong> assessment is based on characterised<br />

cumulative LCI results using the CML baseline<br />

characterisation factors of the impact categories<br />

of global warming, acidification, eutrophication,<br />

human toxicity, freshwater acquatic toxicity, terrestrial<br />

ecotoxicity, ionising radiation, and land<br />

competition, based on proxy indicators (fossil and<br />

nuclear) cumulative energy demand, and based<br />

on the endpoint indicators Eco-indicator 99 (H,<br />

A) mineral resources, human health, eco system<br />

quality and totals. Results. <strong>The</strong> analysis confirms<br />

the fact that capital goods cannot be excluded per<br />

se. On one hand, toxicity related environmental<br />

impacts such as freshwater ecotoxicity or human<br />

toxicity are more sensitive towards an inclusion<br />

or exclusion of capital goods. On the other, certain<br />

products like photovoltaic and wind electricity<br />

are very much or even completely affected by<br />

capital goods contributions, no matter which<br />

indicator is chosen. Nuclear electricity, agricultural<br />

products and processes, and transport services<br />

often behave differently (showing a higher<br />

or lower share of capital goods contribution) than<br />

products from other sectors. Discussions. Some<br />

indicators analysed in this paper show a rather<br />

similar behaviour across all sectors analysed. This<br />

is particularly true for ‘mineral resources’, and<br />

- to a lesser extent - for ‘Eco- indicator 99 total’,<br />

‘acidification’ and ‘climate change’. On the other<br />

hand, ‘land use’ and ‘freshwater ecotoxicity’ show<br />

the most contrasting behaviour with shares of<br />

capital goods’ impacts between less than 1% and<br />

more than 98%. Recommendations. Capital goods<br />

must be included in the assessment of climate<br />

change impacts of non-fossil electricity, agricultural<br />

products and processes, transport services<br />

and waste management services. <strong>The</strong>y must be<br />

included in any sector regarding the assessment<br />

of toxic effects. Energy analyses (quantifying the<br />

non- renewable cumulative energy demand) of<br />

agricultural products and processes, of wooden<br />

products and of transport services should include<br />

capital goods as well. <strong>The</strong> mixing of datasets including<br />

and excluding capital goods is no problem<br />

as long as their share on total impacts is low<br />

and partial omissions do not lead to a significant<br />

imbalance in comparative assertions. Perspectives.<br />

If in doubt whether or not to include capital<br />

goods, it is recommended to check two things:<br />

(1) whether maintenance and depreciation costs<br />

of capital equipment form a substantial part of<br />

the product price (Heijungs et al. 1992a), and (2)<br />

whether actual environmental hot spots occur<br />

along the capital goods’ supply chain.<br />

International Journal of Life Cycle Assessment,<br />

2007, V12, 1, AUG, pp 7-17.


202 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | General Topics<br />

08.1-435<br />

New concepts of Be-10 AMS at low energies<br />

Grajcar M, Döbeli M, Kubik P W, Synal H A,<br />

Wacker L, Suter M<br />

Switzerland<br />

Instruments & Instrumentation , Engineering ,<br />

Paleontology , Geochemistry & Geophysics<br />

Isotopic ratios of Be-10/Be-9 with a background<br />

sensitivity of 2 x 10 (-14) can now be measured<br />

with the 0.6 MV Tandem accelerator of PST /ETH<br />

Zürich using BeF2 instead of BeO as sample material<br />

and injecting BeF- to suppress the boron<br />

detector count rate. A new, high-resolution gas<br />

ionization detector with a thin silicon nitride<br />

entrance window and special preamplifier design<br />

are essential in order to achieve this sensitivity. A<br />

particle transmission of 50% is possible for charge<br />

state 1+. Due to the maximum count rate that<br />

can be accepted by the detector the BeF- currents<br />

are limited to a few hundred nA. Measurements<br />

of Be-10 in rainwater samples performed under<br />

these conditions at the low terminal voltage of<br />

0.6 MV with the new compact AMS system show<br />

good agreement with results using the conventional<br />

Be-10 measurement setup on the 6 MV facility.<br />

Thus, this type of small scale equipment can<br />

now also be applied for Be-10 AMS as long as Be-10/<br />

Be-9 ratios are sufficiently high and measurement<br />

time is not a limiting factor. Instead, using BeO<br />

and the degrader foil technique with a silicon<br />

nitride membrane the boron count rate can also<br />

be suppressed sufficiently but the Be-10/Be-9 background<br />

level is limited to 10 (-13) by scattered Be-9<br />

and the overall transmission is less than 5%.<br />

Nuclear Instruments Methods in Physics Research<br />

Section B Beam Interactions with Materials and<br />

Atoms, 2007, V259, N1, JUN, pp 173-177.<br />

08.1-436<br />

Terrestrial ecotoxicity and effect factors of<br />

metals in life cycle assessment (LCA)<br />

Haye S, Slaveykova V I, Payet J<br />

Switzerland<br />

Ecology , Agriculture, Soil Sciences , Toxicology<br />

Life cycle impact assessment aims to translate the<br />

amounts of substance emitted during the life cycle<br />

of a product into a potential impact on the environment,<br />

which includes terrestrial ecosystems.<br />

This work suggests some possible improvements in<br />

assessing the toxicity of metals on soil ecosystems<br />

in life cycle assessment (LCA). <strong>The</strong> current available<br />

data on soil ecotoxicity allow one to calculate the<br />

chronic terrestrial HC50(EC50) (hazardous concentration<br />

affecting 50% of the species at their EC50<br />

level, i.e. the level where 50% of the individuals of<br />

the species are affected) of nine metals and metal-<br />

loids (As(III) or (V), Be(II), Cr(III) or (VI), Sb(III) or (V),<br />

Pb(II), Cu(II), Zn(II) and Ni(II)). Contrarily to what is<br />

generally advised in LCIA, the terrestrial HC50 of<br />

metals shall not be extrapolated from the aquatic<br />

HC50, using the Equilibrium Partitioning method<br />

since the partition coefficient (Kd) of metals is<br />

highly variable. <strong>The</strong> experimental ecotoxicology<br />

generally uses metallic salts to contaminate artificial<br />

soils but the comparison of the EC50 or NOEC<br />

obtained for the same metal with different salts<br />

reveals that the kind of salt used insignificantly<br />

influences these values. In contrast, depending<br />

on the metallic fraction of concern, the EC50 may<br />

vary, as for cadmium: the EC50 of Folsotnia candida,<br />

expressed as free Cd in pore water is almost<br />

2.5 orders of magnitude lower than that expressed<br />

as total metal. A similar result is obtained with<br />

Eisenia fetida, confirming the importance of metals<br />

speciation in assessing their impact on soils.<br />

By ranking the metals according to the difference<br />

between their terrestrial and aquatic HC50 values,<br />

two groups are distinguished, which match the<br />

hard soft acids and bases (HSAB) concept. This allows<br />

to estimate their affinity for soil components<br />

and potential toxicity according to their chemical<br />

characteristics.<br />

Chemosphere, 2007, V68, N8, JUL, pp 1489-1496.<br />

08.1-437<br />

Challenges for forestry and forest research<br />

- How to promote effective cooperation between<br />

science and practice?<br />

Jäger J, Pluess A, Klank C, Ghazoul J<br />

Canada, Switzerland<br />

Forestry , Plant Sciences , Social Sciences<br />

Wie vielerorts steht in der Schweiz das Waldmanagement<br />

angesichts des Klimawandels und<br />

gesellschaftlicher Änderungen vor großen Herausforderungen.<br />

Die verschiedenen Ansprüche an<br />

den Wald wie rentable Holznutzung, Risikominderung,<br />

Freizeit oder Erhaltung der Biodiversität<br />

bergen ein Konfliktpotenzial. Wie können und<br />

sollen Forstwirtschaft und forstliche Forschung<br />

die Probleme angehen?<br />

Gaia Ecological Perspectives For Science and Society,<br />

2007, V16, N4, pp 261-266.<br />

08.1-438<br />

Environmental impacts of conventional and<br />

sustainable investment funds compared using<br />

input-output life-cycle assessment<br />

Köllner T, Suh S, Weber O, Moser C, Scholz R W<br />

Switzerland<br />

Modelling , Economics , Ecology<br />

This study compares equity funds that are managed<br />

according to sustainability goals with con-


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | General Topics<br />

ventionally managed funds with respect to their<br />

environmental impacts. Overlap in the portfolios<br />

of sustainable equity funds and conventional equity<br />

funds can be very large. Further, the sector<br />

allocation of both types of funds is generally very<br />

similar, because portfolio managers follow a chosen<br />

benchmark to minimize risk. <strong>The</strong>se two effects<br />

may result in no difference existing between<br />

the two types of funds in terms of their environmental<br />

impact and damage (null hypothesis of<br />

this research). This study comparatively assesses<br />

the environmental impact of portfolios of 26 investment<br />

funds: 13 sustainable investment funds<br />

and 13 conventional funds, which are managed<br />

according to the benchmark MSCI World. <strong>The</strong><br />

study applies input output life-cycle assessment<br />

(IO-LCA) in combination with a simulation of company-<br />

specific environmental performance. <strong>The</strong><br />

environmental impact is evaluated per functional<br />

unit for each fund, measured as the risk- adjusted<br />

financial performance. <strong>The</strong> statistical analysis<br />

showed that the analyzed sustainable investment<br />

funds performed better with respect to environmental<br />

impact assessment but worse in economic<br />

risk-adjusted performance (RAP) over the period<br />

2000-2004. In 2004, however, the RAP of the selected<br />

sustainable investment funds showed better<br />

performance. Both samples considerably overlap<br />

for the environmental and economic parameters.<br />

<strong>The</strong> results suggest that the environmental impact<br />

of sustainable investment funds in the sample is<br />

slightly less than that of conventional funds.<br />

Journal of Industrial Ecology, 2007, V11, N3, SUM,<br />

pp 41-60.<br />

08.1-439<br />

Problem-oriented environmental research: <strong>The</strong><br />

view of geography and landscape ecology on<br />

science and application<br />

Leser H<br />

Switzerland<br />

Ecology , Modelling<br />

Environmental research is a broad field of study. On<br />

the one hand, environmental research is carried<br />

out on the basis of specialised approaches and on<br />

the other, on an integrative (i.e. holistic) approach.<br />

In this contribution about environmental research,<br />

landscape ecology is understood as a man-naturespace<br />

system, the subject of which is the functional<br />

connection of nature, technology and society, according<br />

to Ernst Neef. Landscape ecology defines it<br />

as the so-called “landscape ecosystem”. This model<br />

comprises the three very complex subsystems: the<br />

geosystem, biosystem, and anthroposystem. This<br />

complex subject of environmental research can only<br />

be adequately examined if the approach is integra-<br />

203<br />

tive. This in turn means that the various sciences<br />

must scrutinise their approaches and methods, so<br />

that they do not over-specialise, and that they cooperate<br />

on a transdisciplinary basis. <strong>The</strong> results of<br />

this transdisciplinary research work are directed to<br />

the various sciences as well as the different fields of<br />

practice.<br />

Gaia Ecological Perspectives For Science and Society,<br />

2007, V16, N3, pp 200-207.<br />

08.1-440<br />

Linking models of land use, resources, and<br />

economy to simulate the development of<br />

mountain regions (ALPSCAPE)<br />

Lundstroem C, Kytzia S, Walz A, Gret Regamey A,<br />

Bebi P<br />

Switzerland<br />

Modelling , Agriculture, Soil Sciences , Economics<br />

We present a framework of a scenario-based model<br />

that simulates the development of the municipality<br />

of Davos (<strong>Swiss</strong> Alps). ‘We illustrate our method<br />

with the calculation of the scenario for 2050 “Decrease<br />

in subsidies for mountoin agriculture and<br />

liberalization of markets.” <strong>The</strong> main objective was<br />

to link submodels of land-use allocation (regression-based<br />

approach), material and energy flows<br />

submodels (Material and Energy Flux Analysis),<br />

and economic submodels (Input- Output Analysis).<br />

Letting qualitative and quantitative information<br />

flow from one SUbmodel to the next, following the<br />

storyline describing a scenario, has proven to be<br />

suitable for linking submodels. <strong>The</strong> succession of<br />

the submodels is then strongly dependent on the<br />

scenario. Qualitative information flows are simulated<br />

with microsimulations of actor choices. Links<br />

between the submodels show different degrees of<br />

robustness: although the links involving microsimulations<br />

are the weakest, the uncertainty introduced<br />

by the land-use allocation model is actually<br />

advantageous because it allows one possible change<br />

in the landscape in the future to be simulated. <strong>The</strong><br />

modeling results for the scenario here presented<br />

show that the disappearance of agriculture only<br />

marginally affects the region’s factor income, but<br />

that the consequences for the self-sufficiency rate,<br />

for various landscape-related indicators and ecosystem<br />

services, and for the economy in the long term<br />

may be considerable. <strong>The</strong>se benefits compensate<br />

for agriculture’s modest direct economic value.<br />

<strong>The</strong> framework presented can potentially be applied<br />

to any region and scenario. This framework<br />

provides a basis for a learning package that allows<br />

potential detrimental consequences of regional development<br />

to be anticipated at an early stage.<br />

Environmental Management, 2007, V40, N3, SEP,<br />

pp 379-393.


204 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | General Topics<br />

08.1-441<br />

Occurrence, behavior and effects of nanoparticles<br />

in the environment<br />

Nowack B, Bucheli T D<br />

Switzerland<br />

Engineering<br />

<strong>The</strong> increasing use of engineered nanoparticles<br />

(NP) in industrial and household applications<br />

will very likely lead to the release of such materials<br />

into the environment. Assessing the risks of<br />

these NP in the environment requires an understanding<br />

of their mobility, reactivity, ecotoxicity<br />

and persistency. This review presents an overview<br />

of the classes of NP relevant to the environment<br />

and summarizes their formation, emission, occurrence<br />

and fate in the environment. <strong>The</strong> engineered<br />

NP are thereby compared to natural products<br />

such as soot and organic colloids. To date only<br />

few quantitative analytical techniques for measuring<br />

NP in natural systems are available, which results<br />

in a serious lack of information about their<br />

occurrence in the environment. Results from ecotoxicological<br />

studies show that certain NP have<br />

effects on organisms under environmental conditions,<br />

though mostly at elevated concentrations.<br />

<strong>The</strong> next step towards an assessment of the risks<br />

of NP in the environment should therefore be to<br />

estimate the exposure to the different NP. It is<br />

also important to notice that most NP in technical<br />

applications are functionalized and therefore<br />

studies using pristine NP may not be relevant for<br />

assessing the behavior of the NP actually used.<br />

Environmental Pollution, 2007, V150, N1, NOV,<br />

pp 5-22.<br />

08.1-442<br />

Life cycle assessment in the telecommunication<br />

industry: A review<br />

Scharnhorst W<br />

Switzerland<br />

Economics , Engineering<br />

Background, Goal and Scope. Today, after the technologically<br />

and commercially successful breakthrough<br />

of electronic telecommunication facilities,<br />

rapid and globally untrammelled information<br />

exchange has become an indispensable service in<br />

daily life. Associated with the tremendous growth<br />

in electronic telecommunication hardware (GS-<br />

MAssociation 2005), however, was and continues<br />

to be an increasing awareness of the environmental<br />

effects related to both the operation and the<br />

production, as well as the End-of-Life (EoL) treatment<br />

of such communication equipment. Environmental<br />

concerns, for example, have resulted<br />

in various governmental regulations such as the<br />

WEEE- (CEC 2003b) and the RoHS-directives (CEC<br />

2003a). To analyse, interpret and improve the environmental<br />

performance of electronic telecommunication<br />

equipment, life cycle assessment (LCA) is<br />

increasingly recognised as one promising analytical<br />

tool. Based on a thorough review of the scientific<br />

work and by discussing industrial views, this<br />

paper is intended to determine the key milestones<br />

achieved, to analyse the current research situation<br />

and to outline the key challenges concerning<br />

LCA and electronic telecommunication industries.<br />

Method. Starting with a brief reflection of<br />

the LCA approach, the particularities in context<br />

with telecommunication products’ are discussed.<br />

Exemplary for various stakeholders participating<br />

in the supply chain of telecommunication means<br />

recent industry perspectives are also presented.<br />

Results. In the core section of the proposed paper,<br />

the pertinent scientific literature on LCA and electronic<br />

telecommunication means is reviewed and<br />

the most impressive achievements are documented.<br />

Particular attention is dedicated to subcomponents<br />

of individual electronic telecommunication<br />

devices (e.g. Printed Wiring Board Assemblies<br />

(PWBA) of mobile phones), components of mobile<br />

communication networks (e.g. Base Transceiver<br />

Stations (BTS)) and entire networks concentrating<br />

on product comparisons, inventory approaches,<br />

impact assessment method development, result<br />

interpretations and presentation, and usability<br />

of LCA in decision- making. Discussion. From the<br />

reviewed scientific literature and industry views,<br />

it was found that telecommunication products,<br />

in general, represent complex objects requiring<br />

a well thought-out performance of the LCA tool.<br />

It has been shown that today there is a lack of<br />

stakeholder involvement resulting in LCA studies<br />

which only partly fulfil the expectations of<br />

the contractors. In this spirit it was recognised, at<br />

present, that most of the LCA studies on telecommunication<br />

equipment result in bulky and stakeholder<br />

unspecific compilations of findings impossible<br />

to be used in rapid decision-making. This<br />

aspect may explain why LCA so far is not or only<br />

partly integrated into decision-making of globally<br />

integrated industries, such as in telecommunication<br />

industries. Conclusions. In summary, it can<br />

be stated that LCA represents a promising alternative<br />

to analyse, to interpret and essentially to adjust<br />

the environmental performance of electronic<br />

telecommunication products. <strong>The</strong> review showed<br />

that there is a need to focus research efforts in<br />

order to arrive at sound improvements of the<br />

LCA methodology. Perspectives. <strong>The</strong> conclusions<br />

from the presented review suggest concentrating<br />

in particular on further development of the LCA<br />

methodology with respect to efficiency, effectivity


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | General Topics<br />

and flexibility. This challenge is associated with<br />

the need for LCA to be understood as a process<br />

rather than a discontinuously applicable tool,<br />

attending industrial processes, in essence to contribute<br />

to improved environmental performances<br />

of products. In this context, particular attention<br />

should be paid to proper stakeholder involvement<br />

and continuous exchange of concentrated information<br />

relevant for the respective stakeholder.<br />

International Journal of Life Cycle Assessment,<br />

2008, V13, N1, JAN, pp 75-86.<br />

08.1-443<br />

Agricultural decline, landscape change, and<br />

outmigration: Debating the sustainability of<br />

three scenarios for a <strong>Swiss</strong> mountain region<br />

Soliva R<br />

Switzerland<br />

Agriculture, Soil Sciences , Multidisciplinary Sciences<br />

, Political Sciences , Economics<br />

As in many other mountain areas, peripheral regions<br />

of the <strong>Swiss</strong> Alps are experiencing outmigration,<br />

especially of younger people, due to lack of<br />

opportunities. Winter tourism, often the backbone<br />

of regional economies, is declining in many small-<br />

and medium-sized resorts. At the same time, agricultural<br />

decline is leading to land abandonment<br />

and natural reforestation, which may have implications<br />

for the sustainability of development in<br />

these areas. In a case study of the European Union<br />

(EU) BioScene research project, 3 agricultural and<br />

land use scenarios were developed for the Surses<br />

valley in the Canton of Grisons and assessed with<br />

respect to their sustainability implications, including<br />

discussions with a local stakeholder group. In<br />

mitigating outmigration from this peripheral area,<br />

it is important that local people can identify with<br />

the development taking place in their region, and<br />

with the landscape in which they live. Based on the<br />

discussion of the scenarios with local stakeholders<br />

and the sustainability assessment, it was possible<br />

to formulate policy recommendations.<br />

Mountain Research and Development, 2007, V27,<br />

N2, MAY, pp 124-129.<br />

08.1-444<br />

Advances in particle identification in AMS at<br />

low energies<br />

Suter M, Döbeli M, Grajcar M, Müller A, Stocker M,<br />

Sun G, Synal H A, Wacker L<br />

Switzerland<br />

Instruments & Instrumentation , Engineering , Paleontology<br />

, Geochemistry & Geophysics<br />

Special gas ionisation detectors have been developed<br />

for ANIS at low energies (0.3-3 MeV). By using<br />

very thin silicon nitride foils as entrance windows<br />

205<br />

and low-noise preamplifiers, significant improvements<br />

in the performance has been obtained. In<br />

addition, electronic noise has been reduced by a<br />

compact design which minimises cable length<br />

and input capacitance. <strong>The</strong> resolution has been<br />

systematically studied as a function of energy for<br />

various projectiles ranging from protons to uranium.<br />

Energy straggling in the thin entrance foil is<br />

only a minor contribution to the total energy resolution.<br />

For heavier ions z(p) > 6 the resolution is<br />

limited by the statistical nature of the ionisation<br />

process in the counter gas. For light elements, the<br />

electronic noise is the dominant contribution to<br />

the resolution. Particle identification with Delta<br />

E - E techniques has been studied as well. Good<br />

isobar separation for Be-10-B-10 can be obtained<br />

in the energy range of 0.3-0.8 MeV. Also isobaric<br />

molecules such as BeH and CH can be identified<br />

in the energy range of I MeV. <strong>The</strong>se advances in<br />

detector performance represent an essential step<br />

forward in the development of multi-isotope AMS<br />

facilities at low energies. <strong>The</strong> detector development<br />

has also a potential for application in other<br />

fields of research where good energy resolution<br />

and particle identification is needed.<br />

Nuclear Instruments Methods in Physics Research<br />

Section B Beam Interactions with Materials and<br />

Atoms, 2007, V259, N1, JUN, pp 165-172.<br />

08.1-445<br />

MICADAS: A new compact radiocarbon AMS<br />

system<br />

Synal H A, Stocker M, Suter M<br />

Switzerland<br />

Instruments & Instrumentation , Engineering ,<br />

Paleontology , Geochemistry & Geophysics<br />

A novel tabletop AMS system with overall dimensions<br />

of only 2.5 x 3 m (2) has been built and tested.<br />

<strong>The</strong> mini radiocarbon dating System (MICADAS) is<br />

based on a vacuum insulated acceleration unit that<br />

uses a commercially available 200 kV power supply<br />

to generate acceleration fields in a tandem configuration.<br />

At the high-energy end, ions in charge<br />

state 1(+) are selected and interfering molecules of<br />

mass 14 amu are destroyed in multiple collisions.<br />

<strong>The</strong> new system is now fully operational. It is the<br />

prototype of a new generation of radiocarbon spectrometers<br />

which fulfill the requirements for radiocarbon<br />

dating applications as well as for the less<br />

demanding C-14/C-12 isotopic ratio measurements<br />

as needed, e.g. in biomedical applications. A detailed<br />

description of the system is given and results<br />

of performance tests are discussed.<br />

Nuclear Instruments Methods in Physics Research<br />

Section B Beam Interactions with Materials and<br />

Atoms, 2007, V259, N1, JUN, pp 7-13.


206 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | General Topics<br />

08.1-446<br />

Restoring dense vegetation can slow mountain<br />

erosion to near natural benchmark levels<br />

Vanacker V, von Blanckenburg F, Govers G, Molina<br />

A, Poesen J, Deckers J, Kubik P W<br />

Germany, Belgium, Switzerland<br />

Geomorphology , Geology , Agriculture, Soil<br />

Sciences<br />

Tropical mountain areas may undergo rapid land<br />

degradation as demographic growth and intensified<br />

agriculture cause more people to migrate<br />

to fragile ecosystems. To assess the extent of the<br />

resulting damage, an erosion rate benchmark<br />

against which changes in erosion can be evaluated<br />

is required. Benchmarks reflecting natural<br />

erosion rates are usually not provided by conventional<br />

sediment fluxes, which are often biased due<br />

to modern land use change, and also miss large,<br />

episodic events within the measuring period. To<br />

overcome this, we combined three independent<br />

assessment tools in the southern Ecuadorian Andes,<br />

an area that is severely affected by soil erosion.<br />

First, denudation rates from cosmogenic nuclides<br />

in river sediment average over time periods<br />

of 1-100 k.y. and establish a natural benchmark of<br />

only 150 +/- 100 t km(-2) yr(-1). Second, we find that<br />

land use practices have increased modern sediment<br />

yields as derived from reservoir sedimentation<br />

rates, which average over periods of 10-100 yr<br />

to as much as 15 x 10(3) t km(-2)yr(-1). Third, our<br />

land cover analysis has shown us that vegetation<br />

cover exerts first-order control over present-day<br />

erosion rates at the catchment scale. Areas with<br />

high vegetation density erode at rates that are<br />

characteristically similar to those of the natural<br />

benchmark, regardless of whether the type of<br />

vegetation is native or anthropogenic. <strong>The</strong>refore,<br />

our data suggest that even in steep mountain environments<br />

sediment fluxes can slow to near their<br />

natural benchmark levels with suitable revegetation<br />

programs. A set of techniques is now in place<br />

to evaluate the effectiveness of erosion mitigation<br />

strategies.<br />

Geology, 2007, V35, N4, APR, pp 303-306.<br />

08.1-447<br />

Wooden building products in comparative LCA<br />

Werner F, Richter K<br />

Switzerland<br />

Engineering , Energy & Fuels<br />

Background, Aim and Scope. We revised the results<br />

of approx. 20 years of international research<br />

on the environmental impact of the life cycle of<br />

wood products used in the building sector compared<br />

to functionally equivalent products from<br />

other materials. Main Features. Original studies<br />

either technical reports or scientific papers in<br />

English or German were considered. This literature<br />

was obtained via an extensive literature review<br />

(February 2006), via a consultation of compilations<br />

of life cycle assessments (LCA) of wood<br />

products (e.g. elaborated during the COST action<br />

E9) and from secondary literature. <strong>The</strong> resulting<br />

list of literature is considered to be quite complete<br />

and therefore covers the most relevant original<br />

comparative LCA studies of wood products in the<br />

building sector in Europe, Northern America and<br />

Australia. <strong>The</strong> documentation of the studies differs<br />

considerably in terms of completeness (life<br />

cycle stages included, assessment methods), transparency<br />

(description of methodological assumptions,<br />

characteristics of the products, available<br />

data, etc.) and scientific rigor (e.g. related to the<br />

functional equivalency). All encountered original<br />

studies are cited and their scope and transparency<br />

is shortly described. For the environmental ranking<br />

of wood products compared to functionally<br />

equivalent products, only quantitative, transparently<br />

described studies with no obvious methodological<br />

flaws were included, preferably covering<br />

the whole life cycle and conducted according to<br />

the ISO series of standards 14’040ff. For the assessment,<br />

the contribution of each product to<br />

an impact category was compared to the mean<br />

of all functionally equivalent products included<br />

in a study. Results and Discussion. Among the<br />

most important results are: fossil fuel consumption,<br />

potential contributions to the greenhouse<br />

effect and quantities of solid waste tend to be<br />

minor for wood products compared to competing<br />

products; impregnated wood products tend to<br />

be more critical than comparative products with<br />

respect to toxicological effects and/or photosmog<br />

depending on the type of preservative; incineration<br />

of wood products can cause higher impacts<br />

of acidification and eutrophication than other<br />

products, whereas thermal energy can be recovered;<br />

although composed wood products such as<br />

particle board or fibreboard make use of a larger<br />

share of wood of a tree compared to products out<br />

of solid wood, there is a high consumption of fossil<br />

energy associated with the production of fibres<br />

and particles/chips as well as with the production<br />

of glues, resins, etc. In LCAs of whole buildings,<br />

the materials used outside the areas of applicability<br />

of wood dominate the environmental<br />

profile of the building; current methods used for<br />

the impact assessment do not allow to consider<br />

(also favourable) impacts of forests, such as land<br />

occupation, impacts on biodiversity, purification<br />

of air, etc. Conclusions. Wood products that have<br />

been installed and are used in an appropriate way


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | General Topics<br />

tend to have a favourable environmental profile<br />

compared to functionally equivalent products<br />

from other materials. For the dispersion and application<br />

of these conclusions, it is necessary to<br />

adapt LCA to a form, which can be used on a regular<br />

basis for the decision making of different actors<br />

in the construction sector. Perspectives. LCA<br />

methodology in general (the series of standards<br />

ISO 14’040ff) and for the environmental assessment<br />

of wood products in particular have been developed<br />

and consolidated considerably in Europe<br />

and Northern America during the last decade;<br />

the more and more representative and reliable<br />

LCI data for wood products and competing products<br />

has become available. For the future use of<br />

the environmental value of wood products within<br />

sustainable development, the general perception<br />

of the beneficiary use of wood products has to be<br />

increased at various stages of decision-making.<br />

International Journal of Life Cycle Assessment,<br />

2007, V12, N7, NOV, pp 470-479.<br />

207


208<br />

Index of Authors<br />

Aaltonen V 08.1-70<br />

Abbaspour K C 08.1-287 , 08.1-288<br />

Abdaladze O 08.1-108<br />

Abdelmoula M 08.1-192<br />

Abed R M M 08.1-261<br />

Aciego S M 08.1-307<br />

Ackermann Liebrich U 08.1-383 , 08.1-395<br />

Acuna V 08.1-235<br />

Adatte T 08.1-356 , 08.1-357<br />

Adrian R 08.1-239 , 08.1-283<br />

Aebischer A 08.1-291<br />

Aeschlimann D 08.1-216<br />

Aguilar E 08.1-11<br />

Ahlholm J 08.1-128<br />

Akimoto H 08.1-68<br />

Akiyoshi H 08.1-24<br />

Al Subary A 08.1-368<br />

Albrecht M 08.1-80 , 08.1-81<br />

Alewell C 08.1-204<br />

Alfarra M R 08.1-1 , 08.1-14 ,<br />

08.1-79<br />

Alföldi T 08.1-143<br />

Algeo T J 08.1-308<br />

Alioth L 08.1-199<br />

Allaart M 08.1-39 , 08.1-60<br />

Allan J D 08.1-79<br />

Allen P A 08.1-363<br />

Allman D J 08.1-62<br />

Almanza G 08.1-432<br />

Alonso A 08.1-152<br />

Alsum E M 08.1-171<br />

Althaus H J 08.1-434<br />

Amado R 08.1-143<br />

Amelung W 08.1-297<br />

Ammann A 08.1-263<br />

Ammann B 08.1-374 , 08.1-376<br />

Ammann C 08.1-96 , 08.1-302<br />

Ammann H 08.1-182<br />

Ammann M 08.1-66 , 08.1-224<br />

Ammann W 08.1-142<br />

Amundson N R 08.1-2<br />

An S I 08.1-69<br />

Anastasio C 08.1-224<br />

Ancellet G 08.1-60<br />

Andersen M B 08.1-236<br />

Andersen S B 08.1-39 , 08.1-60<br />

Anderson H R 08.1-403<br />

Andersson G 08.1-421<br />

Andersson P S 08.1-236<br />

Andreani Aksoyoglu S 08.1-40 , 08.1-44<br />

Andreu L 08.1-181 , 08.1-372<br />

Andrews E 08.1-70<br />

Andrews J E 08.1-309<br />

Andriambololonera S 08.1-101<br />

Angelibert S 08.1-241 , 08.1-264<br />

Annis J L 08.1-10<br />

Anselmetti F S 08.1-196 , 08.1-237<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Aoki T 08.1-220<br />

Aonghusa Caitriona N 08.1-239<br />

Appenzeller C 08.1-41<br />

Archer E 08.1-82<br />

Arey J S 08.1-244<br />

Arias G 08.1-432<br />

Ariztegui D 08.1-196<br />

Arlettaz R 08.1-166 , 08.1-167 ,<br />

08.1-291<br />

Arnaldos R 08.1-102 , 08.1-103<br />

Arnold U 08.1-130<br />

Arp H P H 08.1-3<br />

Arpenti E 08.1-374<br />

Arvola L 08.1-283<br />

Aschwanden J 08.1-83<br />

Ashley K I 08.1-259<br />

Assigbetse K 08.1-134<br />

Astorga Llorens C 08.1-44<br />

Attie J L 08.1-28<br />

Augenstein I 08.1-107<br />

Aumont O 08.1-301<br />

Austin J 08.1-24<br />

Autissier N 08.1-412 , 08.1-426<br />

Aviron S 08.1-84 , 08.1-85<br />

Bacchi B 08.1-58<br />

Backman L 08.1-18<br />

Badot P M 08.1-147<br />

Bae M S 08.1-4<br />

Bahlmann E 08.1-222<br />

Bahreini R 08.1-79<br />

Baiker A 08.1-415 , 08.1-416<br />

Bailey D 08.1-107<br />

Bakayoko A 08.1-152<br />

Baker A C 08.1-270<br />

Baker M B 08.1-5<br />

Balinga M P B 08.1-152<br />

Ball W P 08.1-208 , 08.1-297<br />

Ballantyne C K 08.1-310<br />

Baltensperger U 08.1-1 , 08.1-6 ,<br />

08.1-14 , 08.1-16 ,<br />

08.1-52 , 08.1-71<br />

Baltes B 08.1-282<br />

Barbante C 08.1-222 , 08.1-325<br />

Barnola J M 08.1-338 , 08.1-350 ,<br />

08.1-359 , 08.1-364<br />

Barr A G 08.1-135 , 08.1-300<br />

Barrie L A 08.1-29 , 08.1-38<br />

Bartelt P 08.1-225<br />

Basilyan A E 08.1-329<br />

Baskaran M 08.1-236<br />

Bassin S 08.1-86<br />

Battipaglia G 08.1-87<br />

Baud A 08.1-308 , 08.1-381<br />

Bauder A 08.1-226<br />

Bauer C 08.1-434<br />

Bauer N 08.1-410<br />

Bauerfeind M 08.1-61


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors 209<br />

Baumann Stanzer K 08.1-23<br />

Baur A 08.1-88<br />

Baur B 08.1-88 , 08.1-89<br />

Baur P 08.1-119<br />

Bayer Oglesby L 08.1-383 , 08.1-395<br />

Bazeley White E 08.1-126<br />

Beagley S R 08.1-24<br />

Bebi P 08.1-159 , 08.1-440<br />

Becagli S 08.1-325 , 08.1-367<br />

Beckstein C 08.1-300<br />

Bednarz Z 08.1-372<br />

Bednyagin D 08.1-418<br />

Beer J 08.1-294 , 08.1-329 ,<br />

08.1-345 , 08.1-359 ,<br />

08.1-364<br />

Beer R 08.1-311 , 08.1-312<br />

Beffrey G 08.1-23<br />

Beier C 08.1-305<br />

Beierkuhnlein C 08.1-126<br />

Beine H J 08.1-224<br />

Belalcazar L C 08.1-78<br />

Beltman B 08.1-238<br />

Benech B 08.1-23<br />

Beniston M 08.1-7 , 08.1-182 ,<br />

08.1-183 , 08.1-382<br />

Benito J L 08.1-108<br />

Benson L 08.1-313<br />

Benton M J 08.1-381<br />

Berg C 08.1-148<br />

Berg G 08.1-148<br />

Bergamaschi P 08.1-305<br />

Bergamini A 08.1-90<br />

Berger H 08.1-23<br />

Bergh N G 08.1-314<br />

Bergin M 08.1-224<br />

Bergmann H 08.1-143<br />

Bernard N 08.1-147<br />

Bernasconi S M 08.1-285 , 08.1-321 ,<br />

08.1-347 , 08.1-348 ,<br />

08.1-349 , 08.1-360<br />

Berner Z 08.1-356 , 08.1-357<br />

Berninger F 08.1-372<br />

Berthelin J 08.1-134<br />

Besnard G 08.1-358<br />

Best A S 08.1-91<br />

Bey I 08.1-28<br />

Bhartia P K 08.1-60<br />

Biagioli F 08.1-413<br />

Biedermann R 08.1-127<br />

Biggs J 08.1-240<br />

Bigler C 08.1-92 , 08.1-315<br />

Bigler M 08.1-325 , 08.1-364<br />

Biksham G 08.1-93<br />

Bilenko V 08.1-228<br />

Billeter R 08.1-94 , 08.1-107<br />

Binnie S 08.1-310<br />

Binzenhöfer B 08.1-127<br />

Bird N 08.1-404<br />

Birrer C 08.1-432<br />

Bjorck S 08.1-345<br />

Black T A 08.1-135<br />

Blackard J A 08.1-194<br />

Blass A 08.1-315 , 08.1-316<br />

Blenckner T 08.1-239 , 08.1-283<br />

Blindheim S 08.1-70<br />

Blinov A V 08.1-329<br />

Blum H 08.1-216<br />

Blunier T 08.1-343 , 08.1-350 ,<br />

08.1-359 , 08.1-364<br />

Bodeker G E 08.1-24 , 08.1-39 ,<br />

08.1-60<br />

Boettger T 08.1-372<br />

Böhmer A 08.1-297<br />

Bohn B 08.1-66<br />

Bojkov B 08.1-39 , 08.1-60<br />

Bolius D 08.1-351<br />

Boller M 08.1-64<br />

Bolliger J 08.1-90 , 08.1-175<br />

Bollschweiler M 08.1-95<br />

Boltshauser A 08.1-100<br />

Bonani G 08.1-333 , 08.1-365<br />

Bond W J 08.1-314<br />

Bongers F 08.1-152<br />

Bonilla J L 08.1-168<br />

Bonnard Ch 08.1-201<br />

Bontadina F 08.1-166<br />

Boone A 08.1-67<br />

Borel J L 08.1-108<br />

Borrmann S 08.1-79<br />

Bosch M E 08.1-433<br />

Bossard P 08.1-250<br />

Böttcher M E 08.1-285<br />

Bottenheim J 08.1-224<br />

Bottjer D J 08.1-381<br />

Boulouchos K 08.1-417<br />

Boumard F 08.1-8<br />

Bourdon B 08.1-203<br />

Boutron C 08.1-222 , 08.1-325<br />

Boville B A 08.1-24<br />

Bower K 08.1-71 , 08.1-79<br />

Bower K N 08.1-14 , 08.1-52<br />

Boxe C S 08.1-224<br />

Boyd I 08.1-34 , 08.1-63<br />

Bozem H 08.1-304<br />

Braathen G O 08.1-44<br />

Braesicke P 08.1-24<br />

Brandner R 08.1-335<br />

Brandt J 08.1-97<br />

Braswell B H 08.1-300<br />

Braun L 08.1-258<br />

Brayard A 08.1-328<br />

Breitenmoser U 08.1-193<br />

Breitenmoser Wursten C 08.1-193<br />

Brenner M 08.1-196


210<br />

Brenninkmeijer C A M 08.1-8<br />

Breon F M 08.1-28<br />

Brito O 08.1-100<br />

Brodbeck S 08.1-130<br />

Brodowski S 08.1-297<br />

Brönnimann S 08.1-9 , 08.1-10 ,<br />

08.1-73<br />

Brooker R 08.1-108<br />

Brookfield M 08.1-308<br />

Brown S 08.1-404<br />

Brueggemann N 08.1-305<br />

Brühl C 08.1-24<br />

Brunet M 08.1-11 , 08.1-20<br />

Brunner A 08.1-96<br />

Brunner B 08.1-285<br />

Brunner F 08.1-277<br />

Brutsche M H 08.1-383<br />

Buchecker M 08.1-390 , 08.1-392<br />

Bucheli T D 08.1-441<br />

Bucher H 08.1-328 , 08.1-355<br />

Büchi F N 08.1-414<br />

Buchmann B 08.1-74<br />

Buchmann N 08.1-86 , 08.1-113<br />

Buckley B 08.1-379<br />

Buentgen U 08.1-323<br />

Bugmann H 08.1-157 , 08.1-188 ,<br />

08.1-306<br />

Bühler R 08.1-237<br />

Bühler S A 08.1-12<br />

Bunce R G H 08.1-97<br />

Büntgen U 08.1-379<br />

Burel F 08.1-85<br />

Burga C 08.1-333<br />

Burgess P J 08.1-151<br />

Bürgi M 08.1-98 , 08.1-175 ,<br />

08.1-176<br />

Burns S J 08.1-368<br />

Burtscher H 08.1-26 , 08.1-46<br />

Busch T 08.1-389<br />

Buser T 08.1-273<br />

Bussotti F 08.1-99<br />

Butchart N 08.1-24<br />

Butterbach Bahl K 08.1-305<br />

Caballero R 08.1-100<br />

Caboussat A 08.1-2<br />

Cachorro V E 08.1-70<br />

Caffrey P 08.1-72<br />

Cairns B J 08.1-186<br />

Cairns W 08.1-222<br />

Calanca P 08.1-182 , 08.1-183 ,<br />

08.1-293 , 08.1-305<br />

Caldeira K 08.1-301<br />

Caldeira M C 08.1-126<br />

Calderoni G 08.1-354<br />

Callmander M W 08.1-101<br />

Calpini B 08.1-39 , 08.1-60<br />

Campanelli M 08.1-70<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Campbell C L 08.1-305<br />

Canadell J 08.1-404<br />

Canagaratna M R 08.1-79<br />

Capello C 08.1-431<br />

Capotondi L 08.1-321<br />

Carmichael C A 08.1-244<br />

Carraro G 08.1-312<br />

Carron G 08.1-265<br />

Carver G 08.1-224<br />

Casassa G 08.1-221<br />

Cascio C 08.1-99<br />

Caspersen J P 08.1-177<br />

Castella E 08.1-265 , 08.1-270<br />

Castellano E 08.1-325 , 08.1-359 ,<br />

08.1-364 , 08.1-367<br />

Casty C 08.1-317<br />

Cattani O 08.1-338<br />

Cedhagen T 08.1-266<br />

Cellier P 08.1-305<br />

Cereghino R 08.1-240 , 08.1-241<br />

Cescon P 08.1-222<br />

Chamecki M 08.1-13<br />

Chancerel B 08.1-210<br />

Chandra S 08.1-60<br />

Changqing G 08.1-322<br />

Chappellaz J 08.1-338 , 08.1-350 ,<br />

08.1-359<br />

Chapron E 08.1-318<br />

Charlet L 08.1-318<br />

Chatelain C 08.1-152<br />

Chaves M M 08.1-104<br />

Cheburkin A K 08.1-365<br />

Chen G 08.1-224<br />

Chernyavsky B 08.1-285<br />

Cherubini P 08.1-54 , 08.1-87 ,<br />

08.1-333<br />

Cherubinic P 08.1-181<br />

Chiarello G L 08.1-415 , 08.1-416<br />

Chimani B 08.1-23<br />

Chipperfield M P 08.1-24<br />

Chorover J 08.1-197<br />

Chorus I 08.1-254<br />

Choularton T 08.1-14 , 08.1-71<br />

Chow F K 08.1-75<br />

Christodoulakis D 08.1-164<br />

Churkina G 08.1-300<br />

Chylek P 08.1-15<br />

Ciccarese L 08.1-404<br />

Cirpka O A 08.1-340<br />

Clappier A 08.1-78<br />

Claude H 08.1-39 , 08.1-60<br />

Clement A 08.1-69<br />

Clothier B E 08.1-210<br />

Coch T 08.1-176<br />

Coe H 08.1-14 , 08.1-79<br />

Coelho Inockdo S 08.1-100<br />

Coetzee G 08.1-39 , 08.1-60


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors 211<br />

Cofield R E 08.1-39<br />

Coldea G 08.1-108<br />

Collaud Coen M 08.1-16<br />

Collin P Y 08.1-347<br />

Colombaroli D 08.1-319<br />

Combourieu Nebout N 08.1-343<br />

Comiskey J A 08.1-152<br />

Conedera M 08.1-320<br />

Conen F 08.1-302<br />

Conesa H M 08.1-102 , 08.1-103 ,<br />

08.1-242<br />

Connolly P 08.1-14 , 08.1-52 ,<br />

08.1-71<br />

Consiglio T K 08.1-101<br />

Cook E R 08.1-326<br />

Cook M 08.1-327<br />

Cordero E 08.1-24<br />

Cornelissen G 08.1-297<br />

Cornelius N 08.1-266<br />

Corstanje R 08.1-198<br />

Cortay R 08.1-152<br />

Corvalan C 08.1-384<br />

Cotrufo F 08.1-305<br />

Cotrufo M F 08.1-87<br />

Cottrell L 08.1-79<br />

Cozic J 08.1-14 , 08.1-16 ,<br />

08.1-52 , 08.1-55 ,<br />

08.1-71<br />

Crawford I 08.1-14<br />

Crawford J H 08.1-224<br />

Cremene C 08.1-88<br />

Cripps M G 08.1-144<br />

Croci Maspoli M 08.1-17<br />

Crosier J 08.1-14<br />

Crutzen P 08.1-8<br />

Csencsics D 08.1-189<br />

Cuddy D T 08.1-39<br />

Cuevas E 08.1-60<br />

Cuffey K M 08.1-307<br />

Curchod F 08.1-213<br />

Curjuric I 08.1-395<br />

Currie L A 08.1-297<br />

Czerwinski J 08.1-420<br />

D‘alessandro C M 08.1-181<br />

D‘arrigo R 08.1-379<br />

Dabas A 08.1-23<br />

Daemmgen U 08.1-305<br />

Daffer W H 08.1-39<br />

Dahl Jensen D 08.1-343<br />

Dahm C N 08.1-235<br />

Dalessandro C M 08.1-372<br />

Dameris M 08.1-24<br />

Damski J 08.1-18<br />

Danna B 08.1-66<br />

Daskalova A 08.1-213<br />

Dauer T 08.1-8<br />

David J S 08.1-104<br />

David T S 08.1-104<br />

Davidson N C 08.1-243<br />

Davies H C 08.1-17 , 08.1-22 ,<br />

08.1-37 , 08.1-50<br />

Davies J 08.1-39 , 08.1-60 ,<br />

08.1-63<br />

Davis C P 08.1-12<br />

de Angelis M 08.1-325<br />

de Backer H 08.1-39 , 08.1-60<br />

de Batist M 08.1-276<br />

de Blust G 08.1-97 , 08.1-107<br />

de Frutos A M 08.1-70<br />

de La Rosa J M 08.1-297<br />

de Meester B 08.1-433<br />

de Vries W 08.1-305<br />

Debret M 08.1-318<br />

Decarlo P F 08.1-79<br />

Deckers J 08.1-446<br />

Deckert R 08.1-24<br />

Declerck S 08.1-240<br />

Decrem M 08.1-105<br />

Defilippi R 08.1-107<br />

Defourny P 08.1-180<br />

Dejung S 08.1-432<br />

Delfino A 08.1-414<br />

Della Marta P M 08.1-11 , 08.1-19 ,<br />

08.1-20 , 08.1-56<br />

Demello J A 08.1-244<br />

Demeny A 08.1-369<br />

Demerjian K L 08.1-4 , 08.1-79<br />

Demuth S 08.1-258<br />

Denoth M 08.1-106<br />

Dersch J 08.1-428<br />

Desai A R 08.1-300<br />

Dessler A E 08.1-21<br />

Deushi M 08.1-24<br />

Dewulf J 08.1-433<br />

Di Carmine C 08.1-70<br />

Di Marco C 08.1-305<br />

Dibb J 08.1-224<br />

Didone M 08.1-22<br />

Diemer M 08.1-94<br />

Dieng L 08.1-134<br />

Dier H 08.1-39 , 08.1-60<br />

Dietrich P 08.1-414<br />

Dietrich S 08.1-191<br />

Dilley M 08.1-82<br />

Dimitrakopoulos P G 08.1-126<br />

Dimopoulos P 08.1-417<br />

Ding L 08.1-297<br />

Dix B 08.1-8<br />

Döbeli M 08.1-435 , 08.1-444<br />

Dobson R 08.1-245<br />

Docherty K 08.1-79<br />

Doering M 08.1-246


212<br />

Doi H 08.1-68<br />

Doka G 08.1-434<br />

Domine F 08.1-224<br />

Dommergue A 08.1-222<br />

Don A 08.1-169<br />

Donegana M 08.1-354<br />

Doney S C 08.1-301<br />

Dong B 08.1-69<br />

Donoghue M 08.1-138<br />

Doppler T 08.1-247<br />

Dormann C F 08.1-107<br />

Dorninger M 08.1-23<br />

Dorokhov V 08.1-60<br />

Doucet J L 08.1-152<br />

Douet V 08.1-399<br />

Downs S H 08.1-383<br />

Dragosits U 08.1-305<br />

Drewnick F 08.1-79<br />

Drexler C 08.1-248<br />

Dreyfus G 08.1-338 , 08.1-359<br />

Drobinski P 08.1-23<br />

Drouin B J 08.1-39<br />

Dubey M 08.1-15<br />

Dubois D 08.1-143<br />

Ducassou E 08.1-321<br />

Duelli P 08.1-80 , 08.1-81 ,<br />

08.1-176<br />

Dufrene M 08.1-180<br />

Düggelin C 08.1-130<br />

Dullinger S 08.1-108<br />

Duncan B 08.1-60<br />

Dungan M A 08.1-330<br />

Dunlea E 08.1-79<br />

Dunn J C 08.1-297<br />

Duponnois R 08.1-134<br />

Duprat J 08.1-321<br />

Dürr B 08.1-23<br />

Dutay J C 08.1-301<br />

Dutschke M 08.1-404<br />

Dzepina K 08.1-79<br />

Eberl L 08.1-148<br />

Ebert M 08.1-52<br />

Ebi K L 08.1-384<br />

Ebinghaus R 08.1-8 , 08.1-222<br />

Ecker K 08.1-114<br />

Eckmeier E 08.1-109 , 08.1-110 ,<br />

08.1-333<br />

Edwards T C 08.1-194<br />

Eerdekens G 08.1-304<br />

Egli M 08.1-192 , 08.1-199<br />

Ehrmann O 08.1-109 , 08.1-110<br />

Eide H A 08.1-220<br />

Eisen O 08.1-377<br />

El Fahem T 08.1-289<br />

El Madidi S 08.1-150<br />

Elena Rossello R 08.1-97<br />

Elith J 08.1-124<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Ellwood B B 08.1-308<br />

Elmquist M 08.1-297<br />

Elshorbany Y 08.1-66<br />

Emde C 08.1-12<br />

Emmenegger L 08.1-113 , 08.1-302 ,<br />

08.1-420<br />

Emmett B A 08.1-305<br />

Ennos R A 08.1-133<br />

Enpu G 08.1-322<br />

Epstein H E 08.1-111<br />

Erhardt A 08.1-88<br />

Eriksen S E H 08.1-393<br />

Eriksson P 08.1-12<br />

Erisman J W 08.1-305<br />

Ershova N 08.1-228<br />

Esper J 08.1-323 , 08.1-326 ,<br />

08.1-362 , 08.1-372 ,<br />

08.1-379<br />

Esperschuetz J 08.1-112<br />

Esswein H 08.1-131<br />

Etien N 08.1-372<br />

Eugster W 08.1-113<br />

Evans K F 08.1-12<br />

Excoffier L 08.1-266<br />

Eyring V 08.1-24 , 08.1-42<br />

Fabbro T 08.1-138<br />

Fahrig L 08.1-160<br />

Fahrni J 08.1-266<br />

Faien X 08.1-318<br />

Fain X 08.1-222<br />

Falge E 08.1-300<br />

Falourd S 08.1-338<br />

Famulari D 08.1-305<br />

Favrat D 08.1-412 , 08.1-426<br />

Faz A 08.1-102 , 08.1-103<br />

Fearnside P 08.1-404<br />

Federer U 08.1-325<br />

Feist D G 08.1-25<br />

Feldmeyer C E 08.1-114<br />

Feller U 08.1-115 , 08.1-117<br />

Fenandez W 08.1-432<br />

Feng Q 08.1-381<br />

Fenner K 08.1-278<br />

Fenner S 08.1-139<br />

Fereday D R 08.1-56<br />

Fernandez N 08.1-121<br />

Ferrachat S 08.1-45<br />

Ferrari C P 08.1-222<br />

Ferri D 08.1-415 , 08.1-416<br />

Ferriere A 08.1-428<br />

Fette M 08.1-249<br />

Fiebig M 08.1-55<br />

Fiedler J 08.1-404<br />

Fierz M 08.1-26<br />

Filipiak M J 08.1-39<br />

Filippi D 08.1-8<br />

Filot M 08.1-372


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors 213<br />

Findlay C S 08.1-160<br />

Finger D 08.1-237 , 08.1-250 ,<br />

08.1-251 , 08.1-255<br />

Finlayson C M 08.1-243<br />

Finn J A 08.1-126<br />

Finsinger W 08.1-324 , 08.1-374<br />

Fischer E M 08.1-200<br />

Fischer H 08.1-8 , 08.1-304 ,<br />

08.1-325 , 08.1-338 ,<br />

08.1-359 , 08.1-364 ,<br />

08.1-367<br />

Fischer M 08.1-163 , 08.1-191<br />

Fischer U 08.1-431<br />

Fischlin A 08.1-404<br />

Fisher T G 08.1-344<br />

Flamant C 08.1-23<br />

Flechard C 08.1-302<br />

Flechard C R 08.1-305<br />

Fleitmann D 08.1-368<br />

Flemming J 08.1-40<br />

Fleuti E 08.1-61<br />

Fliebbach A 08.1-143<br />

Fliessbach A 08.1-112<br />

Flores C D X 08.1-297<br />

Flühler H 08.1-123 , 08.1-212<br />

Flynn M 08.1-14 , 08.1-71<br />

Föllmi K B 08.1-356 , 08.1-357<br />

Follows M 08.1-301<br />

Fomin V V 08.1-173<br />

Fontana D 08.1-280<br />

Fook L S 08.1-39<br />

Foppa N 08.1-57 , 08.1-223<br />

Forner C 08.1-404<br />

Forni L 08.1-415 , 08.1-416<br />

Forsberg B 08.1-403<br />

Fowler D 08.1-305<br />

Francois B 08.1-201<br />

Francois R 08.1-327<br />

Frank D 08.1-323 , 08.1-326 ,<br />

08.1-372 , 08.1-379<br />

Frank D A 08.1-158 , 08.1-303<br />

Franke H 08.1-8<br />

Franssen H J H 08.1-247<br />

Frei A 08.1-419<br />

Freibauer A 08.1-404<br />

Frelechoux F 08.1-116<br />

Frenzel M 08.1-107<br />

Frescino T S 08.1-194<br />

Freunberger S A 08.1-414<br />

Frey M M 08.1-224<br />

Frick G 08.1-72<br />

Frick J 08.1-390<br />

Friess H 08.1-77<br />

Friess U 08.1-8<br />

Frioud M 08.1-23 , 08.1-70<br />

Frischknecht R 08.1-434<br />

Frith S M 08.1-24<br />

Fritsche J 08.1-222<br />

Froeberg L 08.1-89<br />

Froidevaux L 08.1-34 , 08.1-39 ,<br />

08.1-60<br />

Frossard E 08.1-212 , 08.1-216<br />

Frumhoff P 08.1-404<br />

Fuentes I 08.1-432<br />

Füglistaler S 08.1-21<br />

Fuhrer J 08.1-54 , 08.1-86 ,<br />

08.1-182 , 08.1-183<br />

Fuhrer O 08.1-27<br />

Fujita S 08.1-359<br />

Fujiwara M 08.1-39 , 08.1-60<br />

Fuller R A 08.1-39<br />

Fundel F 08.1-325 , 08.1-364<br />

Funk M 08.1-226 , 08.1-233<br />

Furger M 08.1-23<br />

Fusina F 08.1-292<br />

Gabrielli P 08.1-325<br />

Gagen M 08.1-346<br />

Gäggeler H W 08.1-337<br />

Galbraith E D 08.1-327<br />

Galfetti T 08.1-328<br />

Galiana A 08.1-134<br />

Gallagher M W 08.1-14 , 08.1-71 ,<br />

08.1-305<br />

Galle A 08.1-117<br />

Gallet J C 08.1-338<br />

Galloway J N 08.1-296<br />

Gander A 08.1-125<br />

Gander M J 08.1-118<br />

Ganzeveld L 08.1-304<br />

Garcia Cuetos L 08.1-270<br />

Garcia G 08.1-102 , 08.1-103<br />

Garcia Pichel F 08.1-197<br />

Garcia R R 08.1-24<br />

Gaspari V 08.1-325<br />

Gattinger A 08.1-112<br />

Gaumont Guay D 08.1-135<br />

Gausa M 08.1-70<br />

Gautier L 08.1-152<br />

Gavin D G 08.1-92<br />

Gazarini L C 08.1-104<br />

Gedamke S 08.1-48<br />

Geer A J 08.1-25<br />

Gehrig R 08.1-16 , 08.1-46<br />

Geidl M 08.1-421<br />

Gellrich M 08.1-119 , 08.1-156<br />

Generoso S 08.1-28<br />

George C 08.1-66<br />

George D G 08.1-239<br />

Gerbase M W 08.1-383<br />

Gerber J D 08.1-385 , 08.1-386<br />

Gerlach R 08.1-109 , 08.1-110<br />

Gern L 08.1-399<br />

Gettelman A 08.1-24<br />

Gfeller U 08.1-420


214<br />

Ghazoul J 08.1-120 , 08.1-387 ,<br />

08.1-437<br />

Ghosn D 08.1-108<br />

Giaccai D 08.1-192<br />

Gil A 08.1-100<br />

Gilbert D 08.1-147<br />

Gilichinsky D A 08.1-329<br />

Gillet F 08.1-116<br />

Gimenez O 08.1-167<br />

Gimmi U 08.1-98<br />

Ginibre C 08.1-330<br />

Giorgetta M A 08.1-24<br />

Girardclos S 08.1-237<br />

Giraudeau J 08.1-321<br />

Gnansounou E 08.1-418<br />

Godin Beekmann S 08.1-39 , 08.1-60<br />

Goldscheider N 08.1-252<br />

Gong E 08.1-331<br />

Gong S L 08.1-29 , 08.1-38<br />

Gonseth Y 08.1-175<br />

Gonthier E 08.1-321<br />

Gonzales L M 08.1-378<br />

Gonzalez Perez J A 08.1-297<br />

Gonzalez Vila F J 08.1-297<br />

Gooday A J 08.1-266<br />

Goss K U 08.1-3 , 08.1-207<br />

Gottfried M 08.1-108<br />

Goudswaard P C 08.1-284<br />

Gove J H 08.1-300<br />

Govers G 08.1-446<br />

Grabherr G 08.1-108<br />

Grabner M 08.1-372<br />

Graf A 08.1-334<br />

Graf R F 08.1-121<br />

Graf U 08.1-114 , 08.1-143<br />

Graham C H 08.1-124<br />

Grajcar M 08.1-435 , 08.1-444<br />

Grangeon S 08.1-222<br />

Granin N G 08.1-276<br />

Grannas A M 08.1-224<br />

Grant A N 08.1-62<br />

Graser N 08.1-253<br />

Graves A R 08.1-151<br />

Green S R 08.1-210<br />

Gret Regamey A 08.1-440<br />

Grey D 08.1-388<br />

Griffin R E M 08.1-73<br />

Griffin R J 08.1-79<br />

Griffis T J 08.1-135<br />

Grimm V 08.1-121<br />

Grisa E 08.1-312<br />

Grobety B 08.1-46<br />

Gröhn I 08.1-23<br />

Gronholm T 08.1-229<br />

Groom G B 08.1-97<br />

Grosjean M 08.1-315 , 08.1-316<br />

Groza C 08.1-88<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Gruber E 08.1-391<br />

Gruber N 08.1-256 , 08.1-296 ,<br />

08.1-301<br />

Gruber S 08.1-231 , 08.1-234<br />

Gruber U 08.1-225<br />

Grübler M U 08.1-122<br />

Grundl T 08.1-341<br />

Grunwaldt J D 08.1-415 , 08.1-416<br />

Gschwend P M 08.1-297<br />

Guan C 08.1-331<br />

Gubser S 08.1-23<br />

Guerova G 08.1-30<br />

Gueydon A 08.1-100<br />

Gugerli F 08.1-130 , 08.1-189<br />

Guggenberger G 08.1-297<br />

Guglielmetti M 08.1-123<br />

Guillemin M T 08.1-372<br />

Guilyardi E 08.1-69<br />

Guisan A 08.1-124 , 08.1-156 ,<br />

08.1-157<br />

Gujer E 08.1-420<br />

Gulitski G 08.1-31 , 08.1-32 ,<br />

08.1-33<br />

Gumnior M 08.1-332<br />

Gunning C 08.1-92<br />

Gunst L 08.1-143<br />

Günthardt Goerg M S 08.1-145<br />

Gurk C 08.1-304<br />

Gurtz J 08.1-281<br />

Güsewell S 08.1-125 , 08.1-238<br />

Gustafsson O 08.1-297<br />

Gutermann T 08.1-23<br />

Güthe F 08.1-413<br />

Gutierrez E 08.1-372<br />

Gutirrez E 08.1-181<br />

Guyer M 08.1-396<br />

Guzman M I 08.1-224<br />

Gysel M 08.1-14<br />

Haag S 08.1-159<br />

Häberli C 08.1-23<br />

Hachikubo A 08.1-220<br />

Haeberli W 08.1-221 , 08.1-227<br />

Hagedorn F 08.1-333<br />

Hagemann S 08.1-298<br />

Hahn D 08.1-143<br />

Hajdas I 08.1-333 , 08.1-344<br />

Hak C 08.1-44<br />

Hakansson L 08.1-334<br />

Halada L 08.1-97<br />

Hale B W 08.1-171<br />

Hall A M 08.1-310<br />

Haller L 08.1-252<br />

Häller Scharnhorst E 08.1-23<br />

Halliday A N 08.1-236 , 08.1-272<br />

Halmann M 08.1-419<br />

Hammes K 08.1-297<br />

Hammill A 08.1-393


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors 215<br />

Hanisco T F 08.1-21<br />

Hannigan R 08.1-308<br />

Hansen G 08.1-60<br />

Hansen G H 08.1-70<br />

Hansson M 08.1-325<br />

Harder H 08.1-304<br />

Hartkopf Fröder C 08.1-297<br />

Harwood R S 08.1-39<br />

Hatakeyama S 08.1-79<br />

Hatcher P G 08.1-297<br />

Haug G H 08.1-327 , 08.1-352<br />

Haupt M 08.1-372<br />

Hauser A 08.1-57 , 08.1-223<br />

Hauser C 08.1-138<br />

Hawthorne W D 08.1-152<br />

Hayden K 08.1-49<br />

Haye S 08.1-436<br />

Haylock M R 08.1-19<br />

He J W 08.1-2<br />

Heard D E 08.1-224<br />

Heck T 08.1-434<br />

Hector A 08.1-126<br />

Hedderson T A 08.1-314<br />

Heeb N V 08.1-420<br />

Hegner E 08.1-369<br />

Heimann M 08.1-300<br />

Hein S 08.1-127<br />

Heintzenberg J 08.1-8<br />

Heiri O 08.1-311 , 08.1-324<br />

Helander M 08.1-128<br />

Heldstab J 08.1-40 , 08.1-395<br />

Helle G 08.1-372<br />

Helleis F 08.1-8<br />

Hellweg S 08.1-433<br />

Helmig D 08.1-224<br />

Hemmes K 08.1-421<br />

Henderson Sellers A 08.1-299<br />

Hendricks J 08.1-42 , 08.1-55<br />

Hendrickx F 08.1-107<br />

Henne S 08.1-362<br />

Henning S 08.1-16<br />

Henriques M O 08.1-104<br />

Herber A 08.1-70<br />

Hermann M 08.1-8<br />

Hermle S 08.1-145<br />

Herrmann B 08.1-305<br />

Herzog F 08.1-84 , 08.1-105 ,<br />

08.1-107 , 08.1-151<br />

Heymsfield A J 08.1-12<br />

Hieber M 08.1-274<br />

Hilasvuori E 08.1-372<br />

Hillamo R 08.1-70<br />

Hinden H 08.1-264<br />

Hinneri S 08.1-128<br />

Hinz H L 08.1-144<br />

Hirschi M 08.1-298<br />

Hirzel A H 08.1-129 , 08.1-166 ,<br />

08.1-180<br />

Hjort C 08.1-334<br />

Hoch S W 08.1-293<br />

Hochuli P A 08.1-328<br />

Hockaday W C 08.1-297<br />

Hocke K 08.1-34<br />

Hodell D A 08.1-196<br />

Hoebee S E 08.1-130<br />

Hoegger B 08.1-63<br />

Hoehne N 08.1-404<br />

Hofer G 08.1-97<br />

Hoffman H 08.1-61<br />

Hoffmann G 08.1-338<br />

Hoffmann H 08.1-100<br />

Hoffmann M R 08.1-224<br />

Hoffmann V 08.1-389<br />

Hofmeister J 08.1-206<br />

Hofstetter P 08.1-100<br />

Hofstetter T B 08.1-279 , 08.1-280<br />

Hogrefe O 08.1-4<br />

Hohenegger C 08.1-35 , 08.1-36<br />

Höhener P 08.1-205<br />

Hoinka K P 08.1-37<br />

Holderegger R 08.1-130 , 08.1-177 ,<br />

08.1-189<br />

Holliger C 08.1-263<br />

Hollinger D Y 08.1-300<br />

Hollingsworth P M 08.1-133<br />

Hollis J M 08.1-277<br />

Holten J I 08.1-108<br />

Holzgang O 08.1-83<br />

Hölzle M 08.1-231<br />

Holzner C P 08.1-253<br />

Honegger P 08.1-420<br />

Honrath R E 08.1-224<br />

Hoose C 08.1-45<br />

Hopke P K 08.1-4<br />

Hoppel W 08.1-72<br />

Höppner C 08.1-390<br />

Horacek M 08.1-335<br />

Hori M 08.1-220<br />

Horvath L 08.1-305<br />

Houel S 08.1-297<br />

Houlahan J E 08.1-160<br />

Howard D C 08.1-97<br />

Hruska J 08.1-206<br />

Hu A 08.1-69<br />

Huang L 08.1-297<br />

Huang P 08.1-29 , 08.1-38<br />

Huebert B J 08.1-297<br />

Huey L G 08.1-224<br />

Hug W 08.1-373<br />

Hugentobler M 08.1-231<br />

Hui D 08.1-300<br />

Huijbregts M A J 08.1-433<br />

Humair P F 08.1-399


216<br />

Hungerbühler K 08.1-232 , 08.1-431<br />

Hunkeler D 08.1-205<br />

Huntrieser H 08.1-55<br />

Hunziker M 08.1-410<br />

Hurkmans R 08.1-215<br />

Hurni H 08.1-228<br />

Huss Danell K 08.1-126<br />

Huss M 08.1-226<br />

Hutterli M 08.1-224<br />

Hutterli M A 08.1-325<br />

Huybrechts P 08.1-364 , 08.1-367<br />

Ibelings B W 08.1-254<br />

Indermühle N 08.1-264<br />

Irannejad P 08.1-299<br />

Iriarte M 08.1-432<br />

Isaksen I S A 08.1-44<br />

Issembe Y A 08.1-152<br />

Ivits E 08.1-187<br />

Ivy Ochs S 08.1-334<br />

Jaccard S L 08.1-327<br />

Jacobeit J 08.1-56<br />

Jacobi H W 08.1-224<br />

Jacquat O 08.1-202 , 08.1-357<br />

Jaffre T 08.1-133<br />

Jäger J 08.1-131 , 08.1-160 ,<br />

08.1-437<br />

Jäggi M 08.1-132 , 08.1-216<br />

Jahn C 08.1-61<br />

Jankovska V 08.1-336<br />

Jankowski T 08.1-239 , 08.1-283<br />

Jarnot R F 08.1-39<br />

Jarro R 08.1-432<br />

Jarvinen M 08.1-239<br />

Jarvis A J 08.1-300<br />

Jaun L 08.1-250 , 08.1-255<br />

Jayne J T 08.1-79<br />

Jeanneret P 08.1-84<br />

Jenk T M 08.1-337<br />

Jenni L 08.1-83 , 08.1-146<br />

Jennings E 08.1-239 , 08.1-283<br />

Jeppesen E 08.1-283<br />

Jiang Y B 08.1-39<br />

Jimenez C 08.1-12<br />

Jimenez Carceles F J 08.1-242<br />

Jimenez J L 08.1-79<br />

Jin X 08.1-301<br />

Jochem E 08.1-391<br />

Joeckel P 08.1-42<br />

Joergensen R G 08.1-218<br />

John V O 08.1-12<br />

Johns T 08.1-404<br />

Johnsen S 08.1-338 , 08.1-343<br />

Johnson B 08.1-39<br />

Johnson B J 08.1-60 , 08.1-63<br />

Johnson G C 08.1-256<br />

Johst K 08.1-91<br />

Jokela J 08.1-172<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Jonas T 08.1-142<br />

Jones A E 08.1-224<br />

Jones G 08.1-221<br />

Jones N 08.1-30<br />

Jones P D 08.1-10 , 08.1-11 ,<br />

08.1-56<br />

Jones S 08.1-305<br />

Jongman R H G 08.1-97<br />

Jonsell U 08.1-325<br />

Joos F 08.1-301<br />

Jörgensen R G 08.1-190<br />

Joseph E 08.1-60<br />

Joshi J 08.1-126<br />

Jouda F 08.1-399<br />

Jouzel J 08.1-338 , 08.1-343 ,<br />

08.1-359 , 08.1-361<br />

Jumpponen A 08.1-126<br />

Jung J Y 08.1-68<br />

Jungbluth N 08.1-434<br />

Jungclaus J H 08.1-69<br />

Jungner H 08.1-372<br />

Junker B 08.1-392<br />

Junkermann W 08.1-44<br />

Jürgens N 08.1-74<br />

Jurgensen M F 08.1-158<br />

Juschus O 08.1-339<br />

Kägi R 08.1-46<br />

Kahn R 08.1-15<br />

Kaiser H P 08.1-247<br />

Kaiser K 08.1-297<br />

Kalela Brundin M 08.1-372<br />

Kalin Arroyo M T 08.1-138<br />

Kamdem M N D 08.1-152<br />

Kamenik C 08.1-257 , 08.1-366<br />

Kaminski J W 08.1-29<br />

Kämpfer N 08.1-25 , 08.1-34<br />

Kan C 08.1-290<br />

Kanka R 08.1-108<br />

Kapitanov V A 08.1-276<br />

Kaplan J O 08.1-111 , 08.1-378<br />

Karni J 08.1-428<br />

Käser G 08.1-221<br />

Kasper M 08.1-420<br />

Katsouyanni K 08.1-403<br />

Kattge J 08.1-300<br />

Kaufmann P 08.1-325 , 08.1-364 ,<br />

08.1-367<br />

Kavanaugh J L 08.1-307<br />

Kawamura K 08.1-359<br />

Keel S G 08.1-132<br />

Keidel D 08.1-383 , 08.1-395<br />

Kelder H 08.1-39 , 08.1-60<br />

Kellenberger D 08.1-434<br />

Keller A 08.1-213<br />

Keller F 08.1-227<br />

Keller G 08.1-356<br />

Keller J 08.1-40 , 08.1-44


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors 217<br />

Keller M 08.1-40<br />

Keller R 08.1-383<br />

Kery M 08.1-162<br />

Kesik M 08.1-305<br />

Kettle C J 08.1-133<br />

Khayesi M 08.1-405<br />

Kholmyansky M 08.1-31 , 08.1-32 ,<br />

08.1-33<br />

Kholodov A L 08.1-329<br />

Kiczka M 08.1-203<br />

Kienast F 08.1-149 , 08.1-175<br />

Kim K R 08.1-68<br />

Kindlmann P 08.1-85<br />

Kinnison D E 08.1-24<br />

Kinzelbach W 08.1-31 , 08.1-32 ,<br />

08.1-33 , 08.1-289<br />

Kipfer R 08.1-253 , 08.1-340 ,<br />

08.1-341<br />

Kipfstuhl S 08.1-364<br />

Kirschbaum M U F 08.1-404<br />

Kisa M 08.1-134<br />

Kishe Machumu M 08.1-284<br />

Klan P 08.1-224<br />

Klank C 08.1-437<br />

Klar N 08.1-160<br />

Klausenn J 08.1-68<br />

Kläy A 08.1-396<br />

Kleffmann J 08.1-66<br />

Kleijn D 08.1-80<br />

Klein R J T 08.1-393<br />

Kleinbauer I 08.1-108<br />

Klettner C 08.1-108<br />

Kljun N 08.1-135<br />

Kloster S 08.1-45<br />

Klotz S 08.1-107<br />

Klump S 08.1-340 , 08.1-341<br />

Kneisel C 08.1-227<br />

Knoepfel P 08.1-385 , 08.1-386<br />

Knosp B W 08.1-39<br />

Kock H H 08.1-8<br />

Koenig Langlo G 08.1-39<br />

Koeppel C 08.1-8<br />

Koetz R 08.1-414<br />

Kohler M 08.1-420<br />

Kohls K 08.1-261<br />

Köllner T 08.1-136 , 08.1-438<br />

Kondo Y 08.1-79<br />

König Langlo G 08.1-60<br />

Konz M 08.1-258<br />

Koptsik G 08.1-204<br />

Körner C 08.1-132 , 08.1-137 ,<br />

08.1-138 , 08.1-140 ,<br />

08.1-141 , 08.1-164<br />

Korup O 08.1-342<br />

Kosnik M 08.1-403<br />

Kouame F N 08.1-152<br />

Kouka L A 08.1-152<br />

Kovar P 08.1-97<br />

Kram P 08.1-206<br />

Krämer S M 08.1-203<br />

Kramer Schadt S 08.1-121 , 08.1-160<br />

Kramers J D 08.1-309 , 08.1-368 ,<br />

08.1-369<br />

Krapiec M 08.1-372<br />

Kräuchi N 08.1-54<br />

Krebs P 08.1-320<br />

Kretzschmar R 08.1-197 , 08.1-202 ,<br />

08.1-203<br />

Kreuzer M 08.1-184<br />

Kriaa S 08.1-289<br />

Kruesmann T 08.1-380<br />

Krumeich R 08.1-416<br />

Krüsi B O 08.1-149<br />

Krystyn L 08.1-308 , 08.1-335<br />

Kubik P W 08.1-310 , 08.1-313 ,<br />

08.1-334 , 08.1-345 ,<br />

08.1-380 , 08.1-435 ,<br />

08.1-446<br />

Kubistin D 08.1-304<br />

Küchler M 08.1-187<br />

Kuechler M 08.1-114<br />

Kuenzli N 08.1-383<br />

Kuhlman U 08.1-247<br />

Kulakowski D 08.1-159<br />

Kulawik S 08.1-60<br />

Kulmala M 08.1-18 , 08.1-229<br />

Kunes P 08.1-336<br />

Kunz H 08.1-41<br />

Künzli N 08.1-395<br />

Kupper J 08.1-146<br />

Kurz Besson C 08.1-104<br />

Kurz D 08.1-206<br />

Kuypers M M M 08.1-261<br />

Kypreos S 08.1-394<br />

Kyro E 08.1-39<br />

Kyroe E 08.1-60<br />

Kyrola E 08.1-34<br />

Kytzia S 08.1-440<br />

Labat A 08.1-404<br />

Labba N 08.1-100<br />

Lachavanne J B 08.1-260<br />

Läderach C 08.1-214<br />

Laemmle C 08.1-417<br />

Lai X 08.1-381<br />

Laivao M O 08.1-101<br />

Laloui L 08.1-201<br />

Lambert A 08.1-39<br />

Lambert F 08.1-325 , 08.1-367<br />

Lambrecht A 08.1-364<br />

Lancini A 08.1-237<br />

Landais A 08.1-343<br />

Landry C 08.1-2


218<br />

Laneve G 08.1-39<br />

Langnickel U 08.1-428<br />

Lanz V A 08.1-1<br />

Largeau C 08.1-297<br />

Lark R M 08.1-198<br />

Larson T V 08.1-76<br />

Lauer A 08.1-42 , 08.1-55<br />

Laurent D 08.1-414<br />

Laville P 08.1-305<br />

Law K 08.1-55<br />

Lawrence G A 08.1-259<br />

Lazarev V E 08.1-329<br />

Le Meur E 08.1-233<br />

Leadley P W 08.1-126<br />

Leaitch W R 08.1-49<br />

Leal M E 08.1-152<br />

Leblanc T 08.1-39<br />

Lecroq B 08.1-266<br />

Lee G 08.1-68<br />

Lee M H 08.1-68<br />

Leeder M R 08.1-309<br />

Leel Ossy Sz 08.1-369<br />

Lefebvre E 08.1-233<br />

Lefer B 08.1-224<br />

Legreid G 08.1-43<br />

Lehmann A 08.1-175<br />

Lehning M 08.1-229<br />

Lehr P 08.1-49<br />

Leifeld J 08.1-139<br />

Lejoly J 08.1-152<br />

Lelieveld J 08.1-8 , 08.1-304<br />

Leme N P 08.1-39<br />

Lemieux Dudon B 08.1-359<br />

Leong C P 08.1-60<br />

Lepage M 08.1-134<br />

Lepper K 08.1-344<br />

Leser H 08.1-439<br />

Lesins G 08.1-59<br />

Leuenberger H 08.1-184<br />

Leuenberger M 08.1-8 , 08.1-338 ,<br />

08.1-343 , 08.1-372<br />

Leuenberger P 08.1-383<br />

Leuzinger S 08.1-140 , 08.1-141<br />

Levelt P F 08.1-60<br />

Levy P 08.1-305<br />

Lewis S L 08.1-152<br />

Li W 08.1-220<br />

Li Y F 08.1-29<br />

Liebst B 08.1-170<br />

Lihavainen H 08.1-70<br />

Liira J 08.1-107<br />

Lin N H 08.1-68<br />

Linder H P 08.1-314<br />

Lindsay K 08.1-301<br />

Liniger H P 08.1-262<br />

Liniger M A 08.1-41<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Lips M 08.1-182<br />

Lischke H 08.1-111 , 08.1-156 ,<br />

08.1-157<br />

Lister D 08.1-11<br />

Littot G 08.1-325<br />

Liu L 08.1-44<br />

Liu L J S 08.1-76 , 08.1-383 ,<br />

08.1-395<br />

Livesey N J 08.1-39 , 08.1-60<br />

Livingstone D M 08.1-239 , 08.1-267 ,<br />

08.1-316<br />

Ljung K 08.1-345<br />

Loader N J 08.1-346 , 08.1-372<br />

Lods Crozet B 08.1-274<br />

Logvinovich D 08.1-348<br />

Lohmann U 08.1-12 , 08.1-15 ,<br />

08.1-42 , 08.1-45 ,<br />

08.1-49 , 08.1-59 ,<br />

08.1-292<br />

Longet D 08.1-266<br />

Lopez Capel E 08.1-297<br />

Lopez D 08.1-11<br />

Loreau M 08.1-126<br />

Lorenzo R 08.1-46<br />

Lorke A 08.1-267<br />

Lotter A F 08.1-324 , 08.1-371<br />

Louanchi F 08.1-301<br />

Loubet B 08.1-305<br />

Louchouarn P 08.1-297<br />

Louis Schmid B 08.1-347 , 08.1-348 ,<br />

08.1-349 , 08.1-360<br />

Loulergue L 08.1-338 , 08.1-350 ,<br />

08.1-359<br />

Lowell T V 08.1-344<br />

Lowry P P Ii 08.1-101<br />

Luckman B 08.1-379<br />

Lueer B 08.1-297<br />

Luetscher M 08.1-351<br />

Luka H 08.1-155<br />

Lundstroem C 08.1-440<br />

Lundstroem T 08.1-142<br />

Lupi A 08.1-70<br />

Lüscher A 08.1-174<br />

Luterbacher J 08.1-19 , 08.1-20 ,<br />

08.1-317 , 08.1-323 ,<br />

08.1-353<br />

Lüthi B 08.1-31 , 08.1-32 ,<br />

08.1-33<br />

Lüthi D 08.1-22 , 08.1-200 ,<br />

08.1-338<br />

Macmillan L 08.1-262<br />

Mäder P 08.1-112 , 08.1-143<br />

Madole R 08.1-313<br />

Maelfait J P 08.1-107<br />

Magand O 08.1-318<br />

Magne P A 08.1-414


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Maibach M 08.1-396<br />

Maier Reimer E 08.1-301<br />

Malhi Y 08.1-152<br />

Mancini E 08.1-24<br />

Mang Y 08.1-331<br />

Mann M E 08.1-47<br />

Manning D A C 08.1-297<br />

Manzi V 08.1-78<br />

Manzini E 08.1-24<br />

Marchetto A 08.1-319<br />

Marcolli C 08.1-48<br />

Marechal F 08.1-412<br />

Marechal F M A 08.1-422 , 08.1-426<br />

Margaritoulis D 08.1-291<br />

Marland G 08.1-404<br />

Marsh D R 08.1-24<br />

Marshall J 08.1-49<br />

Martinez Harder M 08.1-304<br />

Martinsson B G 08.1-8<br />

Martius O 08.1-50<br />

Martucci G 08.1-51<br />

Marty P 08.1-241<br />

Martynenko A V 08.1-2<br />

Masamvu K 08.1-82<br />

Mascle J 08.1-321<br />

Maselli D 08.1-228<br />

Masiello C A 08.1-297<br />

Masson Delmotte V 08.1-338 , 08.1-343 ,<br />

08.1-359 , 08.1-372<br />

Matear R J 08.1-301<br />

Matera V 08.1-356 , 08.1-357<br />

Matsueda H 08.1-68<br />

Matsumoto K 08.1-301<br />

Matter A 08.1-368<br />

Matthaei S 08.1-275<br />

Matthes S 08.1-24<br />

Matthey R 08.1-51<br />

Matzinger A 08.1-259<br />

Mätzler C 08.1-123<br />

Mayer A 08.1-420<br />

Mayer J 08.1-190 , 08.1-218<br />

Mazza C 08.1-118<br />

Mc Connell J 08.1-224<br />

Mcardell B W 08.1-271<br />

Mccarroll D 08.1-346<br />

Mccaughey J H 08.1-135<br />

Mccracken K G 08.1-294<br />

Mcdermid I S 08.1-39<br />

Mcdonald R 08.1-313<br />

Mcginnis D F 08.1-276<br />

Mckenney J L 08.1-144<br />

Meckler N A 08.1-352<br />

Meier N 08.1-353<br />

Meisser M 08.1-116<br />

Meister R 08.1-223<br />

Melieres M A 08.1-318<br />

219<br />

Melles M 08.1-339<br />

Menetrey N 08.1-260<br />

Meneveau C 08.1-13<br />

Menon M 08.1-145<br />

Merlin O 08.1-215<br />

Merrill J 08.1-39 , 08.1-60<br />

Mertes S 08.1-52 , 08.1-71<br />

Merzouki A 08.1-108<br />

Metzger M J 08.1-97<br />

Meurer M 08.1-320<br />

Meyer H 08.1-329<br />

Michaelowa A 08.1-397 , 08.1-398 ,<br />

08.1-401 , 08.1-402 ,<br />

08.1-404<br />

Michaelowa K 08.1-397 , 08.1-398<br />

Michna P 08.1-113<br />

Middlebrook A M 08.1-79<br />

Miemczyk S 08.1-8<br />

Migeon S 08.1-321<br />

Mills T M 08.1-210<br />

Milne R 08.1-305<br />

Milow B 08.1-428<br />

Minikus Stary N 08.1-333<br />

Minster B 08.1-338<br />

Mirabella A 08.1-192 , 08.1-199<br />

Mishchenko M 08.1-15<br />

Mitchell E A D 08.1-147<br />

Mitev V 08.1-51<br />

Mitra S 08.1-297<br />

Miyoshi T 08.1-79<br />

Mizandrontsev I B 08.1-276<br />

Mkumbo O C 08.1-284<br />

Mobbs D C 08.1-305<br />

Moberg A 08.1-11 , 08.1-56<br />

Moffat A M 08.1-300<br />

Mohr M 08.1-1<br />

Moiseev P 08.1-108<br />

Moisen G G 08.1-194<br />

Molau U 08.1-108<br />

Molina A 08.1-446<br />

Mondeshka M 08.1-213<br />

Monegato G 08.1-354<br />

Monfray P 08.1-301<br />

Monnet C 08.1-355<br />

Montanarella L 08.1-404<br />

Montani A 08.1-281<br />

Moore D 08.1-60<br />

Moran B 08.1-133<br />

Moran Cadenas F 08.1-399<br />

Morand M 08.1-122<br />

Morasch B 08.1-205<br />

Moreira M B 08.1-100<br />

Moret H P 08.1-8<br />

Moret J 08.1-399<br />

Morganti A 08.1-325 , 08.1-364 ,<br />

08.1-367


220 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Morgenstern K 08.1-135<br />

Morris G 08.1-39 , 08.1-60<br />

Morse D L 08.1-307<br />

Mort H 08.1-357<br />

Mort H P 08.1-356<br />

Moser C 08.1-438<br />

Mosimann T 08.1-420<br />

Motik E 08.1-100<br />

Motoyoshi H 08.1-220<br />

Mouchet A 08.1-301<br />

Moutinho P 08.1-404<br />

Mozurkewich M 08.1-72<br />

Mucher C A 08.1-97<br />

Mukai H 08.1-68<br />

Mukhala E 08.1-82<br />

Mulder C P H 08.1-126<br />

Mulder T 08.1-321<br />

Müller A 08.1-407 , 08.1-444<br />

Müller B 08.1-250<br />

Müller Böker U 08.1-392<br />

Müller C 08.1-80<br />

Müller C B 08.1-81<br />

Müller D C A 08.1-422<br />

Müller Fürstenberger G 08.1-400<br />

Müller M 08.1-131 , 08.1-139<br />

Müller M D 08.1-53<br />

Müller R 08.1-211 , 08.1-423<br />

Müller S 08.1-25<br />

Müller S W 08.1-89<br />

Müller T 08.1-190 , 08.1-218<br />

Mulvaney R 08.1-325<br />

Munari Probst M C 08.1-424<br />

Münkemüller T 08.1-91<br />

Murat A 08.1-321<br />

Murdiyarso D 08.1-404<br />

Murdoch W W 08.1-129<br />

Muscheler R 08.1-345<br />

Musial W 08.1-100<br />

Myers J H 08.1-106<br />

Myhre C L 08.1-70<br />

Naef Dänzer B 08.1-122<br />

Naert C 08.1-146<br />

Naess L O 08.1-393<br />

Nagashima T 08.1-24<br />

Nagel P 08.1-282<br />

Nägeli H 08.1-146<br />

Nagy L 08.1-108<br />

Najjar R G 08.1-301<br />

Nakajima Y 08.1-220<br />

Narcisi B 08.1-359<br />

Nater M 08.1-199<br />

Navarro L 08.1-432<br />

Navratil T 08.1-206<br />

Ndour M 08.1-66<br />

Neary L 08.1-38<br />

Neff C 08.1-320<br />

Neftel A 08.1-96 , 08.1-302 ,<br />

08.1-305<br />

Nekrasova V 08.1-263<br />

Nelson F E 08.1-234<br />

Nelson R K 08.1-244<br />

Nemecek T 08.1-434<br />

Nemitz E 08.1-305<br />

Neretin L N 08.1-261<br />

Nesic Z 08.1-135<br />

Nesshoever C 08.1-126<br />

Neu U 08.1-47<br />

Newchurch M 08.1-39 , 08.1-60<br />

Newman P A 08.1-24<br />

Nguyen H N 08.1-8<br />

Nguyen T H 08.1-297<br />

Nguyen Viet H 08.1-147<br />

Niederer C 08.1-207<br />

Niederer P 08.1-228<br />

Nieke J 08.1-220<br />

Nielsen E H 08.1-371<br />

Nielsen J E 08.1-24<br />

Niggli U 08.1-143<br />

Nikolskiy P A 08.1-329<br />

Nisbet R M 08.1-129<br />

Niu T 08.1-29<br />

Noges P 08.1-283<br />

Noges T 08.1-239 , 08.1-283<br />

Nogues Bravo D 08.1-138<br />

Nolte E 08.1-329<br />

Noormets Asko 08.1-300<br />

Norina E S 08.1-217<br />

Northam T 08.1-63<br />

Norton K P 08.1-380<br />

Notter B 08.1-262<br />

Nouet J 08.1-338<br />

Novak K 08.1-54<br />

Nowack B 08.1-219 , 08.1-441<br />

Nozhevnikova A N 08.1-263<br />

Nunes J 08.1-104<br />

Nusbaumer L 08.1-152<br />

Nyeki S 08.1-16<br />

Nyenhuis M 08.1-230<br />

Nyfeler P 08.1-8<br />

O‘brien K L 08.1-393<br />

Oberdoerster C 08.1-123<br />

Oberson A 08.1-212<br />

Obrist D 08.1-222<br />

Obzhirov A I 08.1-276<br />

Oehme M 08.1-143<br />

Oerter H 08.1-338 , 08.1-364 ,<br />

08.1-377<br />

Oertli B 08.1-240 , 08.1-260 ,<br />

08.1-264<br />

Oesch D 08.1-223<br />

Ohmura A 08.1-15 , 08.1-293<br />

Okumura Y 08.1-69


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Olesen J E 08.1-305<br />

Oliva C 08.1-416<br />

Olsommer D 08.1-414<br />

Oltmans S J 08.1-39 , 08.1-60 ,<br />

08.1-63<br />

Onasch T 08.1-79<br />

Opal C 08.1-425<br />

Opelt K 08.1-148<br />

Oram D 08.1-8<br />

Ordonez C 08.1-44<br />

Orr J C 08.1-301<br />

Orsini D 08.1-4<br />

Ortega Calvo J J 08.1-208<br />

Ortiz P 08.1-70<br />

Osullivan D 08.1-8<br />

Otto R 08.1-149<br />

Ou Yang C F 08.1-68<br />

Oukarroum A 08.1-150<br />

Padoa Schioppa E 08.1-97<br />

Paelinx D 08.1-97<br />

Paganelli G 08.1-414<br />

Paillex A 08.1-265<br />

Palazzi F 08.1-412 , 08.1-426<br />

Palma J 08.1-151<br />

Palmborg C 08.1-126<br />

Palo A 08.1-97<br />

Panciera R 08.1-215<br />

Pantet A 08.1-209<br />

Papale D 08.1-300<br />

Parisod C 08.1-358<br />

Parlange M B 08.1-13<br />

Parlow E 08.1-53 , 08.1-295<br />

Parmentier I 08.1-152 , 08.1-153<br />

Parren M P E 08.1-152<br />

Parrenin F 08.1-338 , 08.1-350 ,<br />

08.1-359 , 08.1-364 ,<br />

08.1-367<br />

Parreno J C 08.1-408<br />

Parriaux A 08.1-209<br />

Parrish A 08.1-34<br />

Parrondos M C 08.1-39 , 08.1-60<br />

Pauli H 08.1-108<br />

Pautasso M 08.1-153<br />

Pawelczyk S 08.1-372<br />

Pawlowski J 08.1-266 , 08.1-270<br />

Pawson S 08.1-24<br />

Payet J 08.1-436<br />

Payette S 08.1-379<br />

Pazdur A 08.1-372<br />

Peacock E E 08.1-244<br />

Pearman P B 08.1-154<br />

Pedersen T F 08.1-327<br />

Peeters F 08.1-267<br />

Peh K S H 08.1-152<br />

Peintinger M 08.1-94 , 08.1-268<br />

Pellenard P 08.1-347<br />

221<br />

Peloquin J A 08.1-269<br />

Pena N 08.1-404<br />

Peng P 08.1-297<br />

Penkett S 08.1-8<br />

Penuelas J 08.1-305<br />

Pereira J S 08.1-104<br />

Perez Soba M 08.1-97<br />

Perun V S 08.1-39<br />

Petelski T 08.1-70<br />

Peter A 08.1-249<br />

Peter T 08.1-5 , 08.1-48<br />

Petermann J L 08.1-420<br />

Peterson A T 08.1-124<br />

Peterson L C 08.1-352<br />

Petit J R 08.1-359<br />

Petrasch J 08.1-427<br />

Pettke T 08.1-363<br />

Petzold A 08.1-55<br />

Pfiffner L 08.1-155<br />

Pfister C 08.1-353<br />

Philipona R 08.1-293<br />

Philipp A 08.1-56<br />

Phillips O L 08.1-152<br />

Phillips S 08.1-124<br />

Phillips W 08.1-310<br />

Pierre M 08.1-372<br />

Pieters R 08.1-259<br />

Pilegaard K 08.1-305<br />

Pingoud K 08.1-404<br />

Pini R 08.1-354 , 08.1-374<br />

Pitari G 08.1-24<br />

Pitz P R 08.1-428<br />

Plane J 08.1-224<br />

Planells O 08.1-372<br />

Platt U 08.1-8<br />

Plattner G K 08.1-301<br />

Plessen B 08.1-352<br />

Ploetze M 08.1-363<br />

Pluess A 08.1-437<br />

Plummer D A 08.1-24<br />

Pochanart P 08.1-68<br />

Pochon X 08.1-270<br />

Poesen J 08.1-446<br />

Poethke H J 08.1-127<br />

Pohl M 08.1-125<br />

Polyakov A V 08.1-34<br />

Poon S 08.1-68<br />

Popel O 08.1-428<br />

Popp C 08.1-57<br />

Porcelli D 08.1-236 , 08.1-272<br />

Portman C 08.1-309<br />

Posny F 08.1-39 , 08.1-60 ,<br />

08.1-63<br />

Possenti P 08.1-233<br />

Possingham H P 08.1-186<br />

Pote J 08.1-252


222 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Potvin C 08.1-168<br />

Prati D 08.1-268<br />

Preusser F 08.1-332 , 08.1-339<br />

Prevot A S H 08.1-1 , 08.1-6 ,<br />

08.1-40 , 08.1-44<br />

Price W J 08.1-144<br />

Prin Y 08.1-134<br />

Probst Hensch N M 08.1-383<br />

Pronk W 08.1-64<br />

Pszenny A A P 08.1-62<br />

Pukiene R 08.1-372<br />

Pupek M 08.1-8<br />

Purohita P 08.1-401<br />

Purtschert R 08.1-341<br />

Radionov V 08.1-70<br />

Radoux J 08.1-180<br />

Radtke U 08.1-339<br />

Raharimampionona J 08.1-101<br />

Raible C C 08.1-317<br />

Raimondi S 08.1-199<br />

Rais O 08.1-399<br />

Rais P 08.1-347 , 08.1-348 ,<br />

08.1-349 , 08.1-360<br />

Raisbeck G 08.1-338 , 08.1-350 ,<br />

08.1-359<br />

Raisbeck G M 08.1-361<br />

Rakonczay Z 08.1-404<br />

Rametsteiner E 08.1-404<br />

Raminosoa T 08.1-101<br />

Ramonet M 08.1-8<br />

Ramos I L 08.1-97<br />

Randa B 08.1-8<br />

Ranzi R 08.1-58<br />

Rappenglück B 08.1-61<br />

Rasmus K 08.1-229<br />

Rasmus S 08.1-229<br />

Ratheiser G 08.1-23<br />

Rautiainen J 08.1-79<br />

Ravazzi C 08.1-354 , 08.1-374<br />

Raynaud D 08.1-338 , 08.1-359<br />

Read D J 08.1-126<br />

Read W G 08.1-39<br />

Real E 08.1-55<br />

Rechsteiner C 08.1-417<br />

Reddy C M 08.1-244<br />

Redecker D 08.1-178<br />

Redondas A 08.1-60<br />

Rehkamper M 08.1-272<br />

Reichelt M 08.1-8<br />

Reichert P 08.1-287 , 08.1-288<br />

Reichstein M 08.1-300<br />

Reimann S 08.1-43 , 08.1-44 ,<br />

08.1-74<br />

Reis S 08.1-305<br />

Reiter K 08.1-108<br />

Rellstab C 08.1-237<br />

Renold M 08.1-69<br />

Restuti D 08.1-402<br />

Reynolds Henne C E 08.1-362 , 08.1-372<br />

Rhee T S 08.1-8<br />

Rhoads K 08.1-4<br />

Ribstein P 08.1-221<br />

Richardson A D 08.1-300<br />

Richardson D M 08.1-185<br />

Richner H 08.1-23 , 08.1-51<br />

Richner W 08.1-105<br />

Richoz S 08.1-335<br />

Richter K 08.1-447<br />

Rickebusch S 08.1-156 , 08.1-157<br />

Rickenmann D 08.1-271<br />

Rieke Zapp D 08.1-214<br />

Rieu R 08.1-363<br />

Rigling A 08.1-188<br />

Rigo G 08.1-295<br />

Rinne K T 08.1-372<br />

Ripperger S 08.1-272<br />

Risch A C 08.1-158 , 08.1-303<br />

Riseth J A 08.1-100<br />

Rivera A 08.1-221 , 08.1-221<br />

Rixen C 08.1-159<br />

Robertson I 08.1-346<br />

Robinson B H 08.1-210<br />

Robinson C T 08.1-273 , 08.1-274 ,<br />

08.1-275<br />

Robledo C 08.1-393<br />

Rochat T 08.1-383<br />

Roche P 08.1-97<br />

Rock J 08.1-404<br />

Röckner E 08.1-45<br />

Rodewald R 08.1-385 , 08.1-386<br />

Rodionov A 08.1-297<br />

Roecker C 08.1-424<br />

Roedenbeck I A 08.1-160<br />

Roeder N 08.1-100<br />

Roer I 08.1-230<br />

Rohwer J 08.1-8<br />

Roiger A 08.1-55<br />

Rosch M 08.1-110<br />

Roscher C 08.1-161<br />

Rosenfeld K 08.1-8<br />

Rosenmeier M F 08.1-196<br />

Rossi G 08.1-108<br />

Rotach A 08.1-246<br />

Rotach M W 08.1-75<br />

Rotach P 08.1-130<br />

Roth M 08.1-366<br />

Rothenbühler C 08.1-227<br />

Röthlisberger R 08.1-325<br />

Roux P J 08.1-422<br />

Rouzaud J N 08.1-297<br />

Rowe H 08.1-308<br />

Rowe P J 08.1-309


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Roy D 08.1-172<br />

Royle J A 08.1-162<br />

Rozanov E 08.1-24<br />

Rudel T K 08.1-165<br />

Rudmann Maurer K 08.1-163<br />

Ruffieux D 08.1-23 , 08.1-34<br />

Ruggiero A 08.1-241<br />

Rummler H 08.1-118<br />

Rumpel C 08.1-297<br />

Ruth U 08.1-325 , 08.1-359 ,<br />

08.1-364 , 08.1-367<br />

Rutishauser T 08.1-353<br />

Rybak O 08.1-364<br />

Rydberg B 08.1-12<br />

Sabbatelli T A 08.1-47<br />

Sadoff C W 08.1-388<br />

Sahsuvar L 08.1-29<br />

Saikkonen K 08.1-128<br />

Saladie O 08.1-11<br />

Salam A 08.1-59<br />

Salcedo D 08.1-79<br />

Salzmann N 08.1-231<br />

Samankassou E 08.1-322 , 08.1-331<br />

Samoli E 08.1-403<br />

Sander R 08.1-224 , 08.1-304<br />

Sandradewi J 08.1-1<br />

Sanon A 08.1-134<br />

Sanz M J 08.1-404<br />

Sapkota A 08.1-365<br />

Saracino A 08.1-181 , 08.1-372<br />

Sarmiento J L 08.1-301<br />

Sarris D 08.1-164<br />

Sartori M 08.1-260<br />

Satake A 08.1-165<br />

Sattler T 08.1-166<br />

Saurer M 08.1-54 , 08.1-87 ,<br />

08.1-337 , 08.1-362 ,<br />

08.1-372<br />

Savarino J 08.1-224<br />

Sawa Y 08.1-68<br />

Schäfer K 08.1-61<br />

Schäffer B 08.1-211<br />

Schäffer E 08.1-250<br />

Schäffer P 08.1-349<br />

Schansker G 08.1-150<br />

Schär C 08.1-27 , 08.1-35 ,<br />

08.1-36 , 08.1-67 ,<br />

08.1-200 , 08.1-281 ,<br />

08.1-298<br />

Schärer M 08.1-212<br />

Scharffe D 08.1-8<br />

Scharnhorst W 08.1-442<br />

Schatz G E 08.1-101<br />

Schaub M 08.1-54 , 08.1-167<br />

Scheidegger C 08.1-90 , 08.1-187 ,<br />

08.1-189<br />

223<br />

Scherer Lorenzen M 08.1-126 , 08.1-168 ,<br />

08.1-169<br />

Scheringer M 08.1-232<br />

Scherrer L 08.1-46<br />

Scherrer S C 08.1-41<br />

Schier W 08.1-110<br />

Schileyko A A 08.1-88<br />

Schiller C 08.1-304<br />

Schilt A 08.1-338 , 08.1-350<br />

Schindler C 08.1-383 , 08.1-395 ,<br />

08.1-403<br />

Schippers A 08.1-261<br />

Schirrmeister L 08.1-329<br />

Schjoerring J K 08.1-305<br />

Schlaepfer D R 08.1-246<br />

Schlager H 08.1-8 , 08.1-55<br />

Schlamadinger B 08.1-404<br />

Schleser G H 08.1-372<br />

Schlitzer R 08.1-301<br />

Schloter M 08.1-112<br />

Schlüchter C 08.1-334<br />

Schlumpf N 08.1-333<br />

Schlunegger F 08.1-214 , 08.1-342<br />

Schmid B 08.1-80 , 08.1-81 ,<br />

08.1-126 , 08.1-161<br />

Schmid M 08.1-250 , 08.1-251 ,<br />

08.1-276<br />

Schmid P 08.1-420<br />

Schmid S 08.1-183<br />

Schmidlin F 08.1-39<br />

Schmidlin F J 08.1-60 , 08.1-63<br />

Schmidt Lüttman M 08.1-131<br />

Schmidt M W I 08.1-109 , 08.1-110 ,<br />

08.1-297 , 08.1-333<br />

Schmidt R 08.1-257 , 08.1-366<br />

Schmidt T 08.1-107<br />

Schmutz C 08.1-53<br />

Schneider C 08.1-221<br />

Schneider H 08.1-143<br />

Schneider J 08.1-52 , 08.1-79<br />

Schneider M K 08.1-277 , 08.1-278<br />

Schneider U A 08.1-404<br />

Schneller J 08.1-170<br />

Schneuwly D M 08.1-95<br />

Schnitzler A 08.1-171<br />

Schoch W 08.1-333<br />

Schoeberl M R 08.1-60<br />

Scholz R W 08.1-136 , 08.1-438<br />

Schönmann S 08.1-148<br />

Schotterer U 08.1-351<br />

Schraner M 08.1-24<br />

Schreiber D 08.1-1<br />

Schroeder B 08.1-127<br />

Schroth M H 08.1-217 , 08.1-245<br />

Schubert C J 08.1-261


224 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Schulin R 08.1-145 , 08.1-198 ,<br />

08.1-208 , 08.1-211 ,<br />

08.1-213 , 08.1-219<br />

Schulte D 08.1-377<br />

Schultz M 08.1-44<br />

Schulz T 08.1-64<br />

Schulze E D 08.1-161 , 08.1-169<br />

Schumacher J 08.1-161 , 08.1-169<br />

Schumann U 08.1-8<br />

Schüpbach B 08.1-84<br />

Schürmann G 08.1-61<br />

Schurter M 08.1-255<br />

Schwab F J 08.1-4<br />

Schwab M 08.1-214<br />

Schwander J 08.1-338 , 08.1-359<br />

Schwank M 08.1-123<br />

Schwartz J 08.1-383 , 08.1-403<br />

Schwartz M J 08.1-39<br />

Schwarz M 08.1-187<br />

Schwarz von Raumer H G 08.1-131<br />

Schwarzenbach R P 08.1-3 , 08.1-207 ,<br />

08.1-279 , 08.1-280<br />

Schwarzlaender M 08.1-144<br />

Schweiger O 08.1-107<br />

Schwierz C 08.1-17 , 08.1-50<br />

Schwikowski M 08.1-337 , 08.1-351<br />

Scinocca J F 08.1-24<br />

Seehausen O 08.1-172 , 08.1-284<br />

Seidel T M 08.1-62<br />

Seinfeld J H 08.1-2<br />

Seiz G 08.1-23<br />

Selmo E 08.1-338<br />

Semeniuk K 08.1-24<br />

Semple K T 08.1-208<br />

Seneviratne S I 08.1-200 , 08.1-298<br />

Senterre B 08.1-152<br />

Settele J 08.1-127<br />

Severi M 08.1-325 , 08.1-359 ,<br />

08.1-364 , 08.1-367<br />

Severinghaus J P 08.1-307<br />

Shakun J D 08.1-368<br />

Sharma S 08.1-70<br />

Sheil D 08.1-152<br />

Shepherd T G 08.1-24<br />

Shepson P B 08.1-224<br />

Shibata K 08.1-24<br />

Shimono A 08.1-79<br />

Shisanya C A 08.1-405<br />

Shiyatov S G 08.1-173<br />

Shotyk W 08.1-365<br />

Shrestha A 08.1-258<br />

Shuidenko A 08.1-404<br />

Siamantziouras A S D 08.1-126<br />

Sieber T N 08.1-128<br />

Siegfried T 08.1-289<br />

Siegwolf R 08.1-104<br />

Siegwolf R T W 08.1-87 , 08.1-132 ,<br />

08.1-216 , 08.1-362<br />

Sierro A 08.1-167<br />

Siggaard Andersen M L 08.1-325<br />

Sigman D M 08.1-327 , 08.1-352<br />

Signarbieux C 08.1-115<br />

Sigro J 08.1-11<br />

Siklosy Z 08.1-369<br />

Simpson W R 08.1-224<br />

Sinaj S 08.1-212<br />

Six D 08.1-233<br />

Sjogren S 08.1-14<br />

Skanes H 08.1-97<br />

Skelly J M 08.1-54<br />

Skiba U 08.1-305<br />

Skjemstad J O 08.1-109 , 08.1-297<br />

Skorkovsky J 08.1-403<br />

Skrivankova P 08.1-39 , 08.1-60<br />

Skutsch M 08.1-404<br />

Slater R D 08.1-301<br />

Slaveykova V I 08.1-436<br />

Slemr F 08.1-8<br />

Smart P L 08.1-351<br />

Smernik R J 08.1-297<br />

Smit H G J 08.1-63<br />

Smith Dwight M 08.1-297<br />

Smith J U 08.1-305<br />

Smith P 08.1-305 , 08.1-404<br />

Smith W O Jr 08.1-269<br />

Snyder W V 08.1-39<br />

Soberon J 08.1-138<br />

Sodeau J R 08.1-224<br />

Soliva R 08.1-406 , 08.1-443<br />

Soltic P 08.1-417<br />

Somogyi Z 08.1-404<br />

Song J 08.1-297<br />

Sonke B 08.1-152<br />

Sonninen E 08.1-372<br />

Sosef M S M 08.1-152<br />

Souchez R 08.1-338<br />

Soussana J F 08.1-174 , 08.1-305<br />

Southon J R 08.1-327<br />

Spahni R 08.1-338 , 08.1-350 ,<br />

08.1-359<br />

Sparks D L 08.1-197<br />

Spatzierer M 08.1-23<br />

Speelmans M 08.1-107<br />

Speers L 08.1-138<br />

Spehn E M 08.1-126 , 08.1-138<br />

Spezzaferri S 08.1-370<br />

Spichiger R 08.1-134<br />

Spichtinger P 08.1-292<br />

Spiess E 08.1-105<br />

Spirig C 08.1-96<br />

Spoetl C 08.1-335<br />

Sprung D 08.1-8


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Sreerekha T R 08.1-12<br />

Stahel W A 08.1-432<br />

Stähelin J 08.1-43 , 08.1-73<br />

Stamm C 08.1-212 , 08.1-277 ,<br />

08.1-278<br />

Stamnes K 08.1-220<br />

Stanisci A 08.1-108<br />

Starinsky A 08.1-375<br />

Stauber M 08.1-211<br />

Stauch V J 08.1-300<br />

Stauffer B 08.1-338<br />

Stauffer F 08.1-247<br />

Stebel K 08.1-70<br />

Steck C E 08.1-175 , 08.1-176<br />

Steck T 08.1-34<br />

Stefanopoulou A 08.1-429 , 08.1-430<br />

Steffensen J P 08.1-325 , 08.1-338 ,<br />

08.1-359 , 08.1-367<br />

Stehlik I 08.1-177<br />

Steil B 08.1-24<br />

Stein M 08.1-375<br />

Steinacker R 08.1-23<br />

Steinbacher M 08.1-43 , 08.1-74<br />

Steiner D 08.1-250<br />

Steiner M 08.1-64<br />

Steinfeld A 08.1-77 , 08.1-419 ,<br />

08.1-423 , 08.1-427 ,<br />

08.1-428<br />

Steinhage D 08.1-377<br />

Steinle P 08.1-65<br />

Steinmann P 08.1-356 , 08.1-357<br />

Stek P C 08.1-39<br />

Stemmler K 08.1-43 , 08.1-66<br />

Stenni B 08.1-338<br />

Stephan G 08.1-400<br />

Steppe K 08.1-195<br />

Sterck F J 08.1-195<br />

Sterner T 08.1-407<br />

Stickler A 08.1-304<br />

Stier P 08.1-45<br />

Stievenard M 08.1-372<br />

Stirling C H 08.1-236<br />

Stock P 08.1-8<br />

Stocker J 08.1-232<br />

Stocker M 08.1-444 , 08.1-445<br />

Stocker T F 08.1-69 , 08.1-317 ,<br />

08.1-338 , 08.1-361<br />

Stöckli R 08.1-67<br />

Stöckli V 08.1-142<br />

Stöcklin J 08.1-163<br />

Stofer S 08.1-90 , 08.1-187<br />

Stoffel M 08.1-95<br />

Stohl A 08.1-55<br />

Stolarski R S 08.1-24<br />

Stoll A 08.1-264<br />

Stone R S 08.1-70<br />

225<br />

Storvold R 08.1-220<br />

Stouffer R J 08.1-69<br />

Straeter W 08.1-63<br />

Strahan S 08.1-60<br />

Straile D 08.1-239 , 08.1-267 ,<br />

08.1-283<br />

Strasky S 08.1-334<br />

Strasser A 08.1-373<br />

Strasser R 08.1-99<br />

Strasser R J 08.1-150<br />

Straub K L 08.1-280<br />

Strehler C 08.1-125<br />

Stroem J 08.1-70<br />

Stropp J 08.1-152<br />

Strumia S 08.1-87<br />

Stüben D 08.1-356 , 08.1-357<br />

Stubenrauch C J 08.1-12<br />

Stubi R 08.1-39 , 08.1-63<br />

Stuebi R 08.1-60<br />

Sturm M 08.1-237 , 08.1-315 ,<br />

08.1-316<br />

Sugiura K 08.1-220<br />

Sugiyama S 08.1-226<br />

Suh S 08.1-438<br />

Sullivan W 08.1-72<br />

Sun B 08.1-331<br />

Sun B L 08.1-331<br />

Sun G 08.1-444<br />

Sun H 08.1-138<br />

Sun J Y 08.1-79<br />

Sun Y L 08.1-79<br />

Sunderland T C H 08.1-152<br />

Sundstrom O 08.1-429 , 08.1-430<br />

Suter M 08.1-86 , 08.1-435 ,<br />

08.1-444 , 08.1-445<br />

Sutter C 08.1-408<br />

Sutton M A 08.1-305<br />

Sutton R 08.1-69<br />

Svensson A 08.1-359<br />

Swaine M D 08.1-152<br />

Swart P K 08.1-285<br />

Switsur V R 08.1-372<br />

Sykorova Z 08.1-178<br />

Sylla S 08.1-134<br />

Synal H A 08.1-337 , 08.1-435 ,<br />

08.1-444 , 08.1-445<br />

Szczepanek M 08.1-372<br />

Szeroczynska K 08.1-257<br />

Szidat S 08.1-337<br />

Szidatt S 08.1-1<br />

Szychowska Krapiec E 08.1-372<br />

Taalas P 08.1-18<br />

Tacher L 08.1-201<br />

Takahashi F 08.1-220<br />

Takami A 08.1-79<br />

Takegawa N 08.1-79


226<br />

Takimoto G 08.1-172<br />

Tang Y S 08.1-305<br />

Tanikawa T 08.1-220<br />

Tanimoto H 08.1-68<br />

Tanner T M 08.1-393<br />

Tarasick D 08.1-39<br />

Tarasick D W 08.1-60 , 08.1-63<br />

Targino A 08.1-14<br />

Tchouto M G P 08.1-152<br />

Tellez F 08.1-428<br />

Ter Steege H 08.1-152<br />

Terentev M M 08.1-173<br />

Terry A C 08.1-126<br />

Teubner K 08.1-239<br />

Teuling A J 08.1-215<br />

Thaler R 08.1-8<br />

Thalmann P 08.1-409<br />

<strong>The</strong>is D E 08.1-216<br />

<strong>The</strong>lin P 08.1-209<br />

<strong>The</strong>obald M R 08.1-305<br />

<strong>The</strong>urillat J P 08.1-108<br />

Thierstein H R 08.1-352<br />

Thioulouse J 08.1-134<br />

Thlix L 08.1-18<br />

Thompson A 08.1-39<br />

Thompson A M 08.1-60 , 08.1-63<br />

Thornton P E 08.1-179<br />

Thouret V 08.1-39 , 08.1-60<br />

Thurstans R P 08.1-39<br />

Tian W 08.1-24<br />

Tielbörger K 08.1-248<br />

Tietema A 08.1-305<br />

Timmermann A 08.1-69<br />

Timofeyev Y M 08.1-34<br />

Tinguely M 08.1-40<br />

Tinner W 08.1-311 , 08.1-312 ,<br />

08.1-319 , 08.1-324 ,<br />

08.1-371 , 08.1-374 ,<br />

08.1-376<br />

Tison J L 08.1-338<br />

Titeux N 08.1-180<br />

Tobler N B 08.1-279 , 08.1-280<br />

Tockner K 08.1-246<br />

Todaro L 08.1-181 , 08.1-372<br />

Toledano C 08.1-70<br />

Tomaselli M 08.1-108<br />

Tomasi C 08.1-70<br />

Tong C 08.1-2<br />

Torriani D S 08.1-182 , 08.1-183<br />

Torrico A 08.1-432<br />

Touloumi G 08.1-403<br />

Traversi R 08.1-367<br />

Travis J M J 08.1-91<br />

Treffeisen R 08.1-70<br />

Treydte K 08.1-372<br />

Treydte K S 08.1-362<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Tribsch A 08.1-138<br />

Triguero V 08.1-201<br />

Trines E 08.1-404<br />

Troch P A 08.1-215<br />

Troumbis A Y 08.1-126<br />

Tschannett S 08.1-23<br />

Tschopp J M 08.1-383<br />

Tsinober A 08.1-31 , 08.1-32 ,<br />

08.1-33<br />

Tsuboi K 08.1-68<br />

Tsukada A 08.1-414<br />

Tumskoy V E 08.1-329<br />

Twarloh B 08.1-325<br />

Twigg M 08.1-305<br />

Tykarski P 08.1-138<br />

Tyran E 08.1-100<br />

Udisti R 08.1-325 , 08.1-359 ,<br />

08.1-364 , 08.1-367<br />

Uehlinger U 08.1-246<br />

Uhlenbrook S 08.1-258<br />

Uijlenhoet R 08.1-215<br />

Ulbrich I 08.1-79<br />

Ulrich A 08.1-420<br />

Unterlugauer P 08.1-108<br />

Urmann K 08.1-217<br />

Urquieta E 08.1-432<br />

Valente F 08.1-104<br />

Valentino F 08.1-8<br />

Valsecchi V 08.1-324 , 08.1-374<br />

van den Bergh H 08.1-78<br />

van der Grift E A 08.1-160<br />

van der Knaap W O 08.1-336 , 08.1-346<br />

van der Vorst G 08.1-433<br />

van der Werf W 08.1-151<br />

van Dorland H A 08.1-184<br />

van Gemerden Barend S 08.1-152<br />

van Herle J 08.1-412<br />

van Hout R 08.1-13<br />

van Kleunen M 08.1-185 , 08.1-191<br />

van Langenhove H 08.1-433<br />

van Peteghem C 08.1-146<br />

van Valkenburg J L C H 08.1-152<br />

van Velthoven P 08.1-8<br />

van Wingerden W K R E 08.1-107<br />

Vanacker V 08.1-446<br />

Vanderborght J 08.1-123<br />

Varenne P 08.1-414<br />

Vassere S 08.1-320<br />

Vaz M 08.1-104<br />

Veblen T T 08.1-92<br />

Vedrine S 08.1-373<br />

Velimirov A 08.1-143<br />

Venkatachari P 08.1-4<br />

Vennemann T W 08.1-369<br />

Verbunt M 08.1-281<br />

Verel R 08.1-199


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Verheggen B 08.1-14 , 08.1-16 ,<br />

08.1-52 , 08.1-71 ,<br />

08.1-72<br />

Vernooij M G C 08.1-26<br />

Verstege A 08.1-323<br />

Vesala T 08.1-305<br />

Vescovi E 08.1-374<br />

Viatte P 08.1-39 , 08.1-60<br />

Vidale P L 08.1-67 , 08.1-200<br />

Vigotti M A 08.1-403<br />

Vigran J O 08.1-328<br />

Vincent C 08.1-233<br />

Viovy N 08.1-305<br />

Virkkula A 08.1-70<br />

Vitale V 08.1-70<br />

Vittoz P 08.1-108<br />

Viviroli D 08.1-262<br />

Voemel H 08.1-60<br />

Vögelin A 08.1-202<br />

Vogler C 08.1-10 , 08.1-73<br />

Vogt S 08.1-23<br />

Volk M 08.1-86<br />

Vollmer M K 08.1-74<br />

Vollmer T 08.1-212<br />

Vomel H 08.1-39<br />

von Blanckenburg F 08.1-380 , 08.1-446<br />

von Clarmann T 08.1-34<br />

von der Gathen P 08.1-39 , 08.1-60<br />

von Fumetti S 08.1-282<br />

von Glasow R 08.1-224<br />

von Hildebrand A 08.1-384<br />

von Hoyningen Huene W 08.1-70<br />

von Weissenfluh H 08.1-20<br />

Vonk J 08.1-403<br />

Vose R 08.1-379<br />

Vuichard N 08.1-305<br />

Vuilleumier S 08.1-186<br />

Wacker L 08.1-126 , 08.1-337 ,<br />

08.1-435 , 08.1-444<br />

Waelbroeck C 08.1-359<br />

Wagenbach D 08.1-325<br />

Wagner A 08.1-260<br />

Wagner H H 08.1-189<br />

Wagner P A 08.1-39<br />

Waibel A 08.1-8<br />

Waldmann N 08.1-375<br />

Walker J P 08.1-215<br />

Walker S 08.1-82<br />

Wallner A 08.1-410<br />

Walser A 08.1-281<br />

Walser D 08.1-414<br />

Walter S 08.1-52<br />

Walther A 08.1-11<br />

Walz A 08.1-440<br />

Wandel A 08.1-8<br />

Wang J L 08.1-68<br />

227<br />

Wang T 08.1-68<br />

Wanink J H 08.1-284<br />

Wanner H 08.1-19 , 08.1-20 ,<br />

08.1-56 , 08.1-317 ,<br />

08.1-353<br />

Ward M 08.1-404<br />

Waschitschek K 08.1-8<br />

Waser L 08.1-114<br />

Waser L T 08.1-187<br />

Waterhouse J S 08.1-372<br />

Waters J W 08.1-39<br />

Waugh D W 08.1-24<br />

Weber C 08.1-249<br />

Weber D 08.1-154<br />

Weber O 08.1-438<br />

Weber P 08.1-188<br />

Wegelin M 08.1-432<br />

Wegmann F 08.1-232<br />

Wegner A 08.1-325<br />

Wehrli B 08.1-249 , 08.1-263<br />

Wehrli C 08.1-70<br />

Wehrli M 08.1-376<br />

Weigel A P 08.1-75<br />

Weigl M 08.1-372<br />

Weilenmann M 08.1-74 , 08.1-126<br />

Weimer A 08.1-4<br />

Weimer S 08.1-1 , 08.1-79<br />

Weinbruch S 08.1-52<br />

Weingartner E 08.1-14 , 08.1-16 ,<br />

08.1-52 , 08.1-55 ,<br />

08.1-71<br />

Weingartner R 08.1-262<br />

Weinzierl B 08.1-55<br />

Weirig M F 08.1-301<br />

Weisser W W 08.1-161<br />

Weissert H 08.1-328 , 08.1-347 ,<br />

08.1-348 , 08.1-349 ,<br />

08.1-360<br />

Weller E 08.1-169<br />

Weller R 08.1-224<br />

Weng L 08.1-219<br />

Wenger D 08.1-420<br />

Wenzelides V 08.1-274<br />

Werner F 08.1-447<br />

Werner M 08.1-338<br />

Werner R 08.1-23<br />

Werth S 08.1-189<br />

Wesche C 08.1-377<br />

Westberg H H 08.1-76<br />

Wettstein H R 08.1-184<br />

Weyand A 08.1-163<br />

Weyhenmeyer G A 08.1-239 , 08.1-283<br />

Whitehead J 08.1-305<br />

Whittaker R J 08.1-152<br />

Wichern F 08.1-190 , 08.1-218<br />

Wichser A 08.1-420


228 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Authors<br />

Wick L 08.1-354 , 08.1-374<br />

Wick L Y 08.1-208<br />

Wiedensohler A 08.1-8<br />

Wiederhold J G 08.1-203<br />

Wiemken A 08.1-178<br />

Wilcox C 08.1-186<br />

Wildi W 08.1-252<br />

Wilhelms F 08.1-364<br />

Willems J H 08.1-238<br />

Willi Y 08.1-191<br />

Williams J 08.1-304<br />

Williams J W 08.1-378<br />

Williams P 08.1-79<br />

Williamson J 08.1-76<br />

Wilson R 08.1-379<br />

Winkler E 08.1-268<br />

Wirth L 08.1-177<br />

Witte F 08.1-284<br />

Witte J C 08.1-60 , 08.1-63<br />

Wittmann H 08.1-380<br />

Wolewinski T 08.1-422<br />

Wolff E 08.1-325 , 08.1-359 ,<br />

08.1-364 , 08.1-367<br />

Wolff E W 08.1-224 , 08.1-338<br />

Wöll H 08.1-152<br />

Wong A 08.1-68<br />

Woodruff R 08.1-384<br />

Worsnop D R 08.1-79<br />

Wortmann U G 08.1-285<br />

Wrbka T 08.1-97<br />

Wu C F 08.1-68 , 08.1-76<br />

Wu S Y 08.1-76<br />

Wüest A 08.1-250 , 08.1-251 ,<br />

08.1-255 , 08.1-259 ,<br />

08.1-276<br />

Wunderle S 08.1-57 , 08.1-223<br />

Xie S 08.1-381<br />

Xie S P 08.1-69<br />

Xoplaki E 08.1-20<br />

Xueref Remy I 08.1-8<br />

Yamagata Y 08.1-404<br />

Yamanaka Y 08.1-301<br />

Yamanouchi T 08.1-70<br />

Yang H 08.1-286 , 08.1-287<br />

Yang J 08.1-287 , 08.1-288<br />

Yanko Hombach V 08.1-370<br />

Yassaa N 08.1-304<br />

Yasunari T J 08.1-220<br />

Yela M 08.1-39 , 08.1-60<br />

Yerokhin S 08.1-228<br />

Yin H 08.1-381<br />

Yin J 08.1-69<br />

Yiou F 08.1-361<br />

Yonemura S 08.1-68<br />

Yongli Z Baoliang S 08.1-322<br />

Yool A 08.1-301<br />

Yorish S 08.1-31 , 08.1-32 ,<br />

08.1-33<br />

Yoshiki M 08.1-24<br />

Young D 08.1-43<br />

Youngblut D 08.1-379<br />

Yu Qin 08.1-111<br />

Z‘graggen A 08.1-77<br />

Zablocki G 08.1-39 , 08.1-60<br />

Zachariah Wolff J L 08.1-421<br />

Zahn A 08.1-8<br />

Zammouri M 08.1-289<br />

Zanelli R 08.1-192<br />

Zängl G 08.1-23<br />

Zappa M 08.1-58 , 08.1-290<br />

Zarate E 08.1-78<br />

Zarza E 08.1-428<br />

Zbinden J A 08.1-291<br />

Zbinden N 08.1-138<br />

Zbinden R 08.1-40<br />

Zech U 08.1-8<br />

Zeeman M 08.1-113<br />

Zeh M 08.1-250 , 08.1-255<br />

Zehnder A 08.1-286<br />

Zehnder A J B 08.1-263<br />

Zellweger J P 08.1-383<br />

Zellwegern C 08.1-68<br />

Zennegg M 08.1-420<br />

Zeyer J 08.1-217 , 08.1-245<br />

Zeyer K 08.1-113 , 08.1-302 ,<br />

08.1-420<br />

Zhang J 08.1-45<br />

Zhang Q 08.1-4 , 08.1-79<br />

Zhang T 08.1-234<br />

Zhang W 08.1-297<br />

Zhang Y M 08.1-79<br />

Zhao L Y L 08.1-219<br />

Zhao T L 08.1-29 , 08.1-38<br />

Zhu T 08.1-224<br />

Zielinski T 08.1-70<br />

Ziemke J R 08.1-60<br />

Ziereis H 08.1-8<br />

Zierhofer W 08.1-411<br />

Zierl B 08.1-306<br />

Zimmermann F 08.1-193<br />

Zimmermann N E 08.1-119 , 08.1-124 ,<br />

08.1-156 , 08.1-157 ,<br />

08.1-173 , 08.1-179 ,<br />

08.1-194<br />

Zingg A 08.1-113<br />

Zobel M 08.1-107<br />

Zobrist B 08.1-48<br />

Zopfi J 08.1-252<br />

Zweifel R 08.1-195


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Disciplines 229<br />

Index of Disciplines<br />

Agriculture, Soil Sciences 08.1-80 – 08.1-85 , 08.1-94 , 08.1-96 , 08.1-100 ,<br />

08.1-102 , 08.1-103 , 08.1-105 , 08.1-109 , 08.1-112 ,<br />

08.1-116 , 08.1-119 , 08.1-122 , 08.1-125 , 08.1-134 ,<br />

08.1-136 , 08.1-139 , 08.1-143 , 08.1-145 , 08.1-147 ,<br />

08.1-149 , 08.1-150 , 08.1-151 , 08.1-155 , 08.1-156 ,<br />

08.1-158 , 08.1-163 , 08.1-174 – 08.1-177 , 08.1-182 ,<br />

08.1-183 , 08.1-184 , 08.1-190 , 08.1-192 , 08.1-196 –<br />

08.1-200 , 08.1-202 , 08.1-203 , 08.1-204 , 08.1-206 ,<br />

08.1-207 , 08.1-208 , 08.1-210 – 08.1-213 , 08.1-215 –<br />

08.1-219 , 08.1-238 , 08.1-241 , 08.1-242 , 08.1-277 ,<br />

08.1-278 , 08.1-297 , 08.1-298 , 08.1-300 , 08.1-302 ,<br />

08.1-303 , 08.1-305 , 08.1-320 , 08.1-333 , 08.1-371 ,<br />

08.1-404 , 08.1-406 , 08.1-436 , 08.1-440 , 08.1-443 ,<br />

08.1-446<br />

Biodiversity 08.1-80 , 08.1-81 , 08.1-84 , 08.1-85 , 08.1-86 ,<br />

08.1-88 , 08.1-90 , 08.1-91 , 08.1-93 , 08.1-94 ,<br />

08.1-97 , 08.1-100 , 08.1-101 , 08.1-106 , 08.1-107 ,<br />

08.1-112 , 08.1-116 , 08.1-120 , 08.1-125 – 08.1-131 ,<br />

08.1-133 , 08.1-136 , 08.1-137 , 08.1-138 , 08.1-140 ,<br />

08.1-141 , 08.1-144 , 08.1-147 , 08.1-148 , 08.1-151 –<br />

08.1-154 , 08.1-159 , 08.1-160 , 08.1-161 , 08.1-163 ,<br />

08.1-166 – 08.1-172 , 08.1-175 – 08.1-178 , 08.1-180 ,<br />

08.1-181 , 08.1-183 , 08.1-185 , 08.1-186 , 08.1-187 ,<br />

08.1-189 , 08.1-191 , 08.1-193 , 08.1-238 , 08.1-240 ,<br />

08.1-241 , 08.1-260 , 08.1-264 , 08.1-265 , 08.1-266 ,<br />

08.1-267 , 08.1-270 , 08.1-282 , 08.1-284 , 08.1-291 ,<br />

08.1-355<br />

Cryology / Glaciology 08.1-159 , 08.1-220 – 08.1-234 , 08.1-290 , 08.1-292 ,<br />

08.1-307 , 08.1-310 , 08.1-325 , 08.1-329 , 08.1-334 ,<br />

08.1-337 , 08.1-338 , 08.1-343 , 08.1-344 , 08.1-350 ,<br />

08.1-351 , 08.1-354 , 08.1-358 , 08.1-359 , 08.1-361 ,<br />

08.1-363 , 08.1-364 , 08.1-367 , 08.1-374 , 08.1-377 ,<br />

08.1-380<br />

Ecology 08.1-80 – 08.1-86 , 08.1-88 – 08.1-94 , 08.1-96 –<br />

08.1-102 , 08.1-106 – 08.1-109 , 08.1-111 – 08.1-116 ,<br />

08.1-118 , 08.1-120 , 08.1-121 , 08.1-122 , 08.1-124 –<br />

08.1-131 , 08.1-133 , 08.1-135 – 08.1-141 , 08.1-144 ,<br />

08.1-145 , 08.1-147 – 08.1-158 , 08.1-159 – 08.1-163 ,<br />

08.1-165 – 08.1-183 , 08.1-185 – 08.1-189 , 08.1-191 –<br />

08.1-194 , 08.1-204 , 08.1-216 , 08.1-238 – 08.1-244 ,<br />

08.1-246 , 08.1-249 , 08.1-250 , 08.1-255 , 08.1-257 ,<br />

08.1-264 – 08.1-267 , 08.1-270 , 08.1-273 , 08.1-282 ,<br />

08.1-284 , 08.1-291 , 08.1-296 , 08.1-303 , 08.1-306 ,<br />

08.1-319 , 08.1-320 , 08.1-331 , 08.1-371 , 08.1-385 ,<br />

08.1-386 , 08.1-406 , 08.1-410 , 08.1-433 , 08.1-436 ,<br />

08.1-438 , 08.1-439<br />

Economics 08.1-151 , 08.1-165 , 08.1-286 , 08.1-382 , 08.1-388 ,<br />

08.1-389 , 08.1-391 , 08.1-393 , 08.1-394 , 08.1-396 ,<br />

08.1-397 , 08.1-398 , 08.1-400 , 08.1-401 , 08.1-402 ,<br />

08.1-405 , 08.1-407 , 08.1-408 , 08.1-411 , 08.1-422 ,<br />

08.1-431 , 08.1-434 , 08.1-438 , 08.1-440 , 08.1-442 ,<br />

08.1-443


230<br />

<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Disciplines<br />

Energy + Fuels 08.1-391 , 08.1-400 , 08.1-401 , 08.1-402 , 08.1-412 ,<br />

08.1-413 , 08.1-414 , 08.1-417 , 08.1-418 , 08.1-419 ,<br />

08.1-421 , 08.1-422 , 08.1-424 , 08.1-425 , 08.1-426 ,<br />

08.1-428 , 08.1-429 , 08.1-430 , 08.1-433 , 08.1-447<br />

Engineering 08.1-3 , 08.1-77 , 08.1-401 , 08.1-412 – 08.1-432 ,<br />

08.1-435 , 08.1-441 , 08.1-442 , 08.1-444 , 08.1-445 ,<br />

08.1-447<br />

Forestry 08.1-13 , 08.1-54 , 08.1-55 , 08.1-80 , 08.1-87 ,<br />

08.1-90 , 08.1-92 , 08.1-95 , 08.1-98 , 08.1-99 ,<br />

08.1-101 , 08.1-104 , 08.1-109 , 08.1-110 , 08.1-113 ,<br />

08.1-114 , 08.1-117 , 08.1-119 , 08.1-123 , 08.1-124 ,<br />

08.1-128 , 08.1-130 , 08.1-132– 08.1-135 , 08.1-140 ,<br />

08.1-141 , 08.1-142 , 08.1-145 , 08.1-152 , 08.1-157 ,<br />

08.1-159 , 08.1-164 , 08.1-165 , 08.1-168 , 08.1-169 ,<br />

08.1-171 , 08.1-173 , 08.1-179 , 08.1-181 , 08.1-188 ,<br />

08.1-189 , 08.1-194 , 08.1-195 , 08.1-204 , 08.1-206 ,<br />

08.1-219 , 08.1-300 , 08.1-306 , 08.1-312 , 08.1-319 ,<br />

08.1-323 , 08.1-333 , 08.1-336 , 08.1-346 , 08.1-362 ,<br />

08.1-379 , 08.1-387 , 08.1-437<br />

Geochemistry & Geophysics 08.1-31 , 08.1-32 , 08.1-33 , 08.1-102 , 08.1-103 ,<br />

08.1-139 , 08.1-190 , 08.1-192 , 08.1-197 , 08.1-199 ,<br />

08.1-202 – 08.1-207 , 08.1-213 , 08.1-216 – 08.1-219 ,<br />

08.1-232 , 08.1-235 , 08.1-236 , 08.1-245 , 08.1-253 ,<br />

08.1-259 , 08.1-261 , 08.1-263 , 08.1-272 , 08.1-276 ,<br />

08.1-279 , 08.1-280 , 08.1-283 , 08.1-285 , 08.1-296 ,<br />

08.1-297 , 08.1-301 , 08.1-308 , 08.1-309 , 08.1-315 ,<br />

08.1-325 , 08.1-330 , 08.1-333 , 08.1-335 , 08.1-337 ,<br />

08.1-339 , 08.1-340 , 08.1-341 , 08.1-343 , 08.1-345 ,<br />

08.1-347 , 08.1-348 , 08.1-349 , 08.1-352 , 08.1-356 ,<br />

08.1-368 , 08.1-369 , 08.1-423 , 08.1-435 , 08.1-444 ,<br />

08.1-445<br />

Geology 08.1-196 , 08.1-199 , 08.1-201 , 08.1-205 , 08.1-209 ,<br />

08.1-214 , 08.1-227 , 08.1-230 , 08.1-285 , 08.1-297 ,<br />

08.1-308 , 08.1-309 , 08.1-311 , 08.1-313 , 08.1-315 ,<br />

08.1-316 , 08.1-318 , 08.1-321 , 08.1-328 , 08.1-330 ,<br />

08.1-332 , 08.1-334 , 08.1-335 , 08.1-339 , 08.1-342 ,<br />

08.1-344 – 08.1-348 , 08.1-352 , 08.1-355 , 08.1-356 ,<br />

08.1-357 , 08.1-360 , 08.1-365 , 08.1-368 , 08.1-369 ,<br />

08.1-373 , 08.1-374 , 08.1-375 , 08.1-380 , 08.1-381 ,<br />

08.1-446<br />

Geomorphology 08.1-95 , 08.1-196 , 08.1-201 , 08.1-209 , 08.1-214 ,<br />

08.1-227 , 08.1-230 , 08.1-237 , 08.1-246 , 08.1-271 ,<br />

08.1-310 , 08.1-313 , 08.1-318 , 08.1-342 , 08.1-354 ,<br />

08.1-377 , 08.1-446<br />

History 08.1-9 , 08.1-98 , 08.1-110 , 08.1-320 , 08.1-374 ,<br />

08.1-376 , 08.1-389<br />

Human & Public Health 08.1-254 , 08.1-383 , 08.1-384 , 08.1-395 , 08.1-403 ,<br />

08.1-420


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Disciplines<br />

Hydrology 08.1-58 , 08.1-67 , 08.1-212 , 08.1-215 , 08.1-235 ,<br />

08.1-236 , 08.1-237 , 08.1-238 , 08.1-246 – 08.1-251 ,<br />

08.1-255 , 08.1-258 , 08.1-271 , 08.1-274 , 08.1-275 ,<br />

08.1-277 , 08.1-281 , 08.1-282 , 08.1-287 , 08.1-288 ,<br />

08.1-289 , 08.1-290 , 08.1-298 , 08.1-299 , 08.1-332 ,<br />

08.1-341 , 08.1-392<br />

Instruments & Instrumentation 08.1-8 , 08.1-46 , 08.1-48 , 08.1-51 , 08.1-77 ,<br />

08.1-162 , 08.1-209 , 08.1-225 , 08.1-230 , 08.1-231 ,<br />

08.1-243 , 08.1-288 , 08.1-337 , 08.1-372 , 08.1-409 ,<br />

08.1-435 , 08.1-444 , 08.1-445<br />

International Relations 08.1-65 , 08.1-68 , 08.1-404 , 08.1-407<br />

Limnology 08.1-237 , 08.1-239 , 08.1-250 , 08.1-252 , 08.1-253 ,<br />

08.1-255 , 08.1-257 , 08.1-259 , 08.1-263 , 08.1-268 ,<br />

08.1-274 , 08.1-275 , 08.1-276 , 08.1-283 , 08.1-311 ,<br />

08.1-315 , 08.1-316 , 08.1-366<br />

Marine & Freshwater Biology 08.1-239 – 08.1-245 , 08.1-249 – 08.1-252 , 08.1-254 ,<br />

08.1-255 , 08.1-257 , 08.1-259 , 08.1-260 , 08.1-261 ,<br />

08.1-263 – 08.1-270 , 08.1-272 , 08.1-273 , 08.1-274 ,<br />

08.1-279 , 08.1-280 , 08.1-282 , 08.1-283 , 08.1-284 ,<br />

08.1-291 , 08.1-322 , 08.1-331 , 08.1-355 , 08.1-366 ,<br />

08.1-370<br />

Medicine 08.1-383 , 08.1-395 , 08.1-399 , 08.1-403<br />

Meteorology & Atmospheric Sciences 08.1-1 – 08.1-79 , 08.1-82 , 08.1-86 , 08.1-87 , 08.1-91 ,<br />

08.1-96 , 08.1-111 , 08.1-115 , 08.1-132 , 08.1-152 ,<br />

08.1-157 , 08.1-164 , 08.1-173 , 08.1-174 , 08.1-183 ,<br />

08.1-195 , 08.1-200 , 08.1-221 , 08.1-222 , 08.1-224 ,<br />

08.1-226 , 08.1-228 , 08.1-233 , 08.1-234 , 08.1-239 ,<br />

08.1-257 , 08.1-262 , 08.1-267 , 08.1-281 , 08.1-290 ,<br />

08.1-292 – 08.1-299 , 08.1-302 , 08.1-304 , 08.1-305 ,<br />

08.1-313 , 08.1-314 , 08.1-317 , 08.1-319 , 08.1-323 –<br />

08.1-328 , 08.1-338 , 08.1-343 , 08.1-349 , 08.1-350 ,<br />

08.1-353 , 08.1-359 , 08.1-361 , 08.1-363 , 08.1-366 ,<br />

08.1-373 , 08.1-375 , 08.1-376 , 08.1-378 , 08.1-379 ,<br />

08.1-382 , 08.1-383 , 08.1-393 , 08.1-394 , 08.1-396 –<br />

08.1-400 , 08.1-404 , 08.1-405 , 08.1-408 , 08.1-409 ,<br />

08.1-414 , 08.1-415 , 08.1-416 , 08.1-420<br />

Microbiology 08.1-112 , 08.1-118 , 08.1-128 , 08.1-130 , 08.1-134 ,<br />

08.1-147 , 08.1-148 , 08.1-189 , 08.1-205 , 08.1-252 ,<br />

08.1-261 , 08.1-263 , 08.1-279 , 08.1-280 , 08.1-285 ,<br />

08.1-314 , 08.1-358 , 08.1-432<br />

231


232 <strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Disciplines<br />

Modelling 08.1-2 , 08.1-7 , 08.1-12 , 08.1-15 , 08.1-18 , 08.1-21 ,<br />

08.1-22 , 08.1-24 , 08.1-27– 08.1-30 , 08.1-36 ,<br />

08.1-38 , 08.1-39 , 08.1-40 , 08.1-42 , 08.1-44 ,<br />

08.1-45 , 08.1-53 , 08.1-55 , 08.1-58 , 08.1-60 ,<br />

08.1-63 , 08.1-64 , 08.1-67 , 08.1-69 , 08.1-70 ,<br />

08.1-72 , 08.1-74 , 08.1-76 , 08.1-78 , 08.1-85 ,<br />

08.1-91 , 08.1-105 , 08.1-108 , 08.1-111 , 08.1-114 ,<br />

08.1-119 , 08.1-121 , 08.1-122 , 08.1-123 , 08.1-124 ,<br />

08.1-127 , 08.1-129 , 08.1-145 , 08.1-157 , 08.1-162 ,<br />

08.1-165 , 08.1-166 , 08.1-167 , 08.1-179 , 08.1-180 ,<br />

08.1-182 , 08.1-183 , 08.1-186 , 08.1-187 , 08.1-194 ,<br />

08.1-195 , 08.1-198 , 08.1-200 , 08.1-201 , 08.1-206 ,<br />

08.1-219 , 08.1-220 , 08.1-225 , 08.1-226 , 08.1-227 ,<br />

08.1-229 , 08.1-231 , 08.1-232 , 08.1-247 , 08.1-251 ,<br />

08.1-258 , 08.1-259 , 08.1-262 , 08.1-268 , 08.1-276 ,<br />

08.1-277 , 08.1-281 , 08.1-285 , 08.1-287 , 08.1-288 ,<br />

08.1-289 , 08.1-290 , 08.1-292 , 08.1-293 , 08.1-295 ,<br />

08.1-298 , 08.1-299 , 08.1-300 , 08.1-301 , 08.1-304 ,<br />

08.1-305 , 08.1-306 , 08.1-317 , 08.1-349 , 08.1-363 ,<br />

08.1-378 , 08.1-382 , 08.1-394 , 08.1-409 , 08.1-421 ,<br />

08.1-426 , 08.1-427 , 08.1-432 , 08.1-438 , 08.1-439 ,<br />

08.1-440<br />

Multidisciplinary Sciences 08.1-9 , 08.1-396 , 08.1-443<br />

Oceanography 08.1-17 , 08.1-31 , 08.1-32 , 08.1-33 , 08.1-47 ,<br />

08.1-69 , 08.1-236 , 08.1-256 , 08.1-267 , 08.1-269 ,<br />

08.1-272 , 08.1-296 , 08.1-301 , 08.1-327 , 08.1-335 ,<br />

08.1-345 , 08.1-347 , 08.1-352 , 08.1-356 , 08.1-357 ,<br />

08.1-360<br />

Paleontology 08.1-196 , 08.1-307 – 08.1-381 , 08.1-435 , 08.1-444 ,<br />

08.1-445<br />

Plant Sciences 08.1-13 , 08.1-54 , 08.1-55 , 08.1-80 , 08.1-86 –<br />

08.1-90 , 08.1-92 , 08.1-94 , 08.1-95 , 08.1-96 ,<br />

08.1-98 , 08.1-99 , 08.1-101 – 08.1-104 , 08.1-106 –<br />

08.1-110 , 08.1-112 – 08.1-117 , 08.1-119 , 08.1-123 –<br />

08.1-126 , 08.1-128 , 08.1-130 , 08.1-132 , 08.1-133 ,<br />

08.1-134 , 08.1-135 , 08.1-137 , 08.1-140 – 08.1-145 ,<br />

08.1-148 , 08.1-150 , 08.1-152 , 08.1-153 , 08.1-154 ,<br />

08.1-157 , 08.1-158 , 08.1-159 , 08.1-161 , 08.1-163 ,<br />

08.1-164 , 08.1-168 , 08.1-169 , 08.1-170 , 08.1-171 ,<br />

08.1-173 , 08.1-174 , 08.1-177 , 08.1-178 , 08.1-179 ,<br />

08.1-181 , 08.1-182 , 08.1-185 , 08.1-187 – 08.1-191 ,<br />

08.1-194 , 08.1-195 , 08.1-203 , 08.1-206 , 08.1-210 ,<br />

08.1-216 , 08.1-218 , 08.1-238 , 08.1-268 , 08.1-300 ,<br />

08.1-303 , 08.1-306 , 08.1-311 , 08.1-312 , 08.1-314 ,<br />

08.1-319 , 08.1-323 , 08.1-324 , 08.1-333 , 08.1-336 ,<br />

08.1-346 , 08.1-353 , 08.1-358 , 08.1-362 , 08.1-371 ,<br />

08.1-372 , 08.1-376 , 08.1-378 , 08.1-379 , 08.1-387 ,<br />

08.1-427 , 08.1-437<br />

Political Sciences 08.1-286 , 08.1-391 , 08.1-392 , 08.1-393 , 08.1-397 ,<br />

08.1-398 , 08.1-404 , 08.1-407 , 08.1-409 , 08.1-443


<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Index of Disciplines<br />

Remote Sensing 08.1-57 , 08.1-123 , 08.1-187 , 08.1-194 , 08.1-220 ,<br />

08.1-223 , 08.1-243 , 08.1-295<br />

Social Sciences 08.1-82 , 08.1-160 , 08.1-165 , 08.1-384 – 08.1-388 ,<br />

08.1-390 , 08.1-405 , 08.1-406 , 08.1-410 , 08.1-411 ,<br />

08.1-437<br />

Toxicology 08.1-102 , 08.1-103 , 08.1-105 , 08.1-146 , 08.1-147 ,<br />

08.1-197 , 08.1-202 , 08.1-204 , 08.1-208 , 08.1-210 ,<br />

08.1-212 , 08.1-213 , 08.1-217 , 08.1-244 , 08.1-254 ,<br />

08.1-436<br />

Urban Studies 08.1-1 , 08.1-4 , 08.1-6 , 08.1-40 , 08.1-66 , 08.1-73 ,<br />

08.1-76 , 08.1-78 , 08.1-79 , 08.1-131 , 08.1-153 ,<br />

08.1-177 , 08.1-295<br />

Water Resources 08.1-105 , 08.1-212 , 08.1-217 , 08.1-237 , 08.1-245 ,<br />

08.1-247 , 08.1-248 , 08.1-250 , 08.1-251 , 08.1-255 ,<br />

08.1-260 , 08.1-262 , 08.1-275 , 08.1-278 , 08.1-286 ,<br />

08.1-289 , 08.1-388 , 08.1-392 , 08.1-432<br />

Zoology 08.1-80 , 08.1-81 , 08.1-83 , 08.1-85 , 08.1-88 ,<br />

08.1-100 , 08.1-107 , 08.1-122 , 08.1-127 , 08.1-146 ,<br />

08.1-154 , 08.1-160 , 08.1-162 , 08.1-166 , 08.1-167 ,<br />

08.1-175 , 08.1-176 , 08.1-180 , 08.1-184 , 08.1-193 ,<br />

08.1-239 , 08.1-241 , 08.1-260 , 08.1-264 , 08.1-265 ,<br />

08.1-273 , 08.1-274 , 08.1-282 , 08.1-284 , 08.1-291 ,<br />

08.1-399<br />

233


SciSearch ® - Science Citation Index ®<br />

Description of the SciSearch ® Database<br />

SciSearch is a multi-disciplinary index to the international literature of science and technology. It corresponds<br />

to the Science Citation Index (available in print and on CD-ROM) and contains additional<br />

material from the Current Contents series of publications (available in print and on weekly diskettes or<br />

CD-ROM).<br />

SciSearch’s weekly updating gives extremely fast access to the international literature of scientific and<br />

technical research. It is structured to provide versatile retrieval possibilities: in addition to the conventional<br />

search approaches, SciSearch offers citation indexing to enable identification of current articles<br />

by their earlier cited papers. <strong>The</strong> database was recently enhanced with author abstracts, author keywords<br />

and KeyWords Plus.<br />

<strong>The</strong> database indexes all significant items (articles, reports of meetings, letters, editorials, correction<br />

notices, etc.) from approximately 6’400 scientific and technical journals published world-wide.<br />

Producer<br />

For further details of SciSearch, the Science Citation Index or Current Contents, please contact:<br />

Institute for Scientific Information (ISI)®<br />

Brunel Science Park, Brunel University<br />

Uxbridge, UB8 3PQ, U.K.<br />

Tel. +44 1895 270016<br />

Fax +44 1895 256710

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