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Global Change Abstracts The Swiss Contribution - SCNAT

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<strong>Global</strong> <strong>Change</strong> <strong>Abstracts</strong> – <strong>The</strong> <strong>Swiss</strong> <strong>Contribution</strong> | Oceans and Fresh Water Systems<br />

hydrological soil information is not available at a<br />

European scale, we reclassified the Soil Geographical<br />

Database of Europe (SGDBE) at 1:1 million in a<br />

hydrological manner by adopting the Hydrology Of<br />

Soil Types (HOST) system developed in the UK. <strong>The</strong><br />

HOST classification describes dominant pathways<br />

of water movement through soil and was related to<br />

the base flow index (BFI) of a catchment (the longterm<br />

proportion of base flow on total stream flow).<br />

In the original UK study, a linear regression of the<br />

coverage of HOST classes in a catchment explained<br />

79% of BFI variability. We found that a hydrological<br />

soil classification can be built based on the information<br />

present in the SGDBE. <strong>The</strong> reclassified SGDBE<br />

and the regression coefficients from the original UK<br />

study were used to predict BFIs for 103 catchments<br />

spread throughout Europe. <strong>The</strong> predicted BFI explained<br />

around 65% of the variability in measured<br />

BFI in catchments in Northern Europe, but the explained<br />

variance decreased from North to South.<br />

We therefore estimated new regression coefficients<br />

from the European discharge data and found that<br />

these were qualitatively similar to the original estimates<br />

from the UK. This suggests little variation<br />

across Europe in the hydrological effect of particular<br />

HOST classes, but decreasing influence of soil<br />

on BFI towards Southern Europe. Our preliminary<br />

study showed that pedological information is useful<br />

for characterising soil hydrology within Europe and<br />

the long-term discharge regime of catchments in<br />

Northern Europe. Based on these results, we draft a<br />

roadmap for a refined hydrological classification of<br />

European soils.<br />

Hydrology and Earth System Sciences, 2007, V11,<br />

N4, pp 1501-1513.<br />

08.1-278<br />

Selecting scenarios to assess exposure of surface<br />

waters to veterinary medicines in Europe<br />

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

Switzerland<br />

Water Resources , Agriculture, Soil Sciences<br />

Registering a veterinary medicinal product (VMP) in<br />

the European Union requires assessing its potential<br />

to contaminate surface waters (SW) on a European<br />

scale. VMP are spread to land in manure or excreted<br />

during grazing and may enter SW through runoff,<br />

erosion, or leaching. Since the factors driving these<br />

processes vary largely across Europe, it is necessary<br />

to identify characteristic conditions, so-called scenarios,<br />

un(er which VMP enter SW. <strong>The</strong>se scenarios<br />

may guide the parameterization of mechanistic fate<br />

models to predict environmental concentrations for<br />

environmental risk assessment. A number of such<br />

scenarios for pesticides and VMP have been developed<br />

rather pragmatically. Here, we describe how a<br />

143<br />

geo-referenced European database of driving factors<br />

was used to divide the European environment into<br />

groups with similar conditions for SW contamination<br />

by VMP. Out of these groups, relevant exposure<br />

scenarios in Europe were selected by a simple scoring<br />

system. Comparing these to the existing scenarios<br />

showed that a number of situations are not well<br />

covered. <strong>The</strong> newly identified scenarios are primarily<br />

located in hilly areas of Central Europe and the<br />

Mediterranean, and in Eastern European plains with<br />

a continental climate. We recommend that they are<br />

included in the technical guidelines for higher-tier<br />

assessment of VMP.<br />

Environmental Science Technology, 2007, V41,<br />

N13, JUL 1, pp 4669-4676.<br />

08.1-279<br />

Assessing iron-mediated oxidation of toluene<br />

and reduction of nitroaromatic contaminants<br />

in anoxic environments using compound- specific<br />

isotope analysis<br />

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

Switzerland<br />

Geochemistry & Geophysics , Microbiology , Marine<br />

& Freshwater Biology<br />

We evaluated compound-specific isotope analysis<br />

(CSIA) as a tool to assess the coupling of microbial<br />

toluene oxidation by Fe(III)- reducing<br />

bacteria and abiotic reduction of nitroaromatic<br />

contaminants by biogenic mineral-bound Fe(II)<br />

species. Examination of the two processes in<br />

isolated systems revealed a reproducible carbon<br />

isotope fractionation for toluene oxidation by<br />

Geobacter metallireducens with a solid Fe(111)<br />

phase as terminal electron acceptor. We found a<br />

carbon isotope enrichment factor, epsilon(C), of<br />

-1.0 +/- 0.1%o, which corresponds to an apparent<br />

kinetic isotope effect (AKIE(C)) of 1.0073 +/- 0.0009<br />

for the oxidative cleavage of a C-H bond. Nitrogen<br />

isotope fractionation of the reduction of nitroaromatic<br />

compounds (NAC) by mineral-bound Fe(11)<br />

species yielded a nitrogen isotope enrichment factor,<br />

EN, of -39.7 +/- 3.4%o for the reduction of an<br />

aromatic NO 2-group (AKIE(N) = 1.0413 +/- 0.0037)<br />

that was constant for variable experimental conditions.<br />

Finally, AKIE values for C and N observed<br />

in coupled experiments, where reactive Fe(11) was<br />

generated through microbial activity, were identical<br />

to those obtained in the isolated experiments.<br />

This study provides new evidence on isotope fractionation<br />

behavior during contaminant transformation<br />

and promotes the use of CSIA for-the elucidation<br />

of complex contaminant transformation<br />

pathways in the environment.<br />

Environmental Science Technology, 2007, V41,<br />

N22, NOV 15, pp 7773-7780.

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