D10: Impact of Contaminants - Hydromod
D10: Impact of Contaminants - Hydromod
D10: Impact of Contaminants - Hydromod
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Integrated Water Resource Management for Important Deep European Lakes and their Catchment Areas<br />
EUROLAKES<br />
<strong>D10</strong>: <strong>Impact</strong> <strong>of</strong> <strong>Contaminants</strong><br />
FP5_Contract No.: EVK1-CT1999-00004<br />
Version: 4.0<br />
Date: 25/07/01<br />
File: <strong>D10</strong>-vers.4.0.doc<br />
Page 78 <strong>of</strong> 136<br />
tions (2 cm depth) in the measured harbour at Lake Geneva are for TBT in the range <strong>of</strong><br />
660 to more than 5000 µg/kg dry weight and for TPT between 118 and approximately<br />
1800 µg/kg. In comparison to other Lakes in the same study, the marina <strong>of</strong> Lake Geneva<br />
showed the highest contamination. The TPT concentrations were always lower<br />
than TBT concentrations. In 1993 TPT was not measured and the highest level reached<br />
by TPT was 0.9 µg/g dw in Lake Geneva marina in September 1990. The butyltin concentrations<br />
in zebra mussel tissue <strong>of</strong> Lake Geneva marina over the 4-year period<br />
showed no decrease <strong>of</strong> the contamination. The annual concentrations actually increased.<br />
Furthermore, the TBT concentrations were quite stable throughout the year<br />
and no clear summer-winter pr<strong>of</strong>ile was detectable. Irgarol 1051 is the trade name <strong>of</strong> a<br />
triazine herbicide (2-methylthio-4tert-butylamino-6-cyclopropylamino-s-triazine). After<br />
the ban <strong>of</strong> organotin compounds in antifouling paints in Switzerland in 1990 they were<br />
replaced by Irgarol 1051 and copper based products [TÓTH et al 1996]. In the study <strong>of</strong><br />
[TÓTH et al 1996] two marinas and one reference site were chosen in Lake Geneva.<br />
The samples were collected between August 1994 and April 1995. The present Irgarol<br />
1051 concentrations in water <strong>of</strong> Lake Geneva marinas do not reach the acute toxic levels<br />
for algae but an ecotoxic long-term effect on phytoplankton, algae and macrophytes<br />
cannot be excluded.<br />
Location Butyltin concentratíon (µg/L)<br />
June 1988 September 1988<br />
DBT TBT DBT TBT<br />
Geneva (CH) 0.014<br />
0.299<br />
0.005<br />
0.049<br />
(nd - 0.083) (nd - 1.079) (nd - 0.022) (nd - 0.087)<br />
Lausanne (CH) 0.072<br />
0.271<br />
0.037<br />
0.123<br />
(nd - 0.0103) (0.077 - 0.377) (nd - 0.065) (0.079 - 0.170)<br />
Montreux (CH) 0.061<br />
0.353<br />
0.005<br />
0.041<br />
(nd - 0.243) (nd - 0.695) (nd - 0.011) (nd - 0.106)<br />
Thonon (F) nd 0.015<br />
0.003<br />
0.026<br />
(nd - 0.063) (nd - 0.008) (nd - 0.045)<br />
Yvoire (F) nd 0.047<br />
0.007<br />
0.045<br />
Reference (CH) nd<br />
(nd - 0.064)<br />
0.013<br />
(nd - 0.053)<br />
(nd - 0.010)<br />
0.002<br />
(nd - 0.008)<br />
(nd - 0.015)<br />
0.004<br />
(nd - 0.015)<br />
Each value i a mean <strong>of</strong> 6 samples (3 stations each with one surface and one bottom sample)<br />
except for the reference point (2 stations). The range is indicated below in parantheses.<br />
TPT has not been detected. (nd = not detected, CH = Switzerland, F = France)<br />
Table 10-2:Concentrations <strong>of</strong> butyltins in water <strong>of</strong> Lake Geneva marinas and one natural<br />
site (reference) [BECKER et al 1992]