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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 />