Global Change Abstracts The Swiss Contribution - SCNAT
Global Change Abstracts The Swiss Contribution - SCNAT
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 />