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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]

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