Report from the Sub-comittee on the environment and health
Report from the Sub-comittee on the environment and health
Report from the Sub-comittee on the environment and health
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34<br />
• The frequency of detecti<strong>on</strong> is highest in agricultural catchment areas<br />
with clayey soils.<br />
• There are not many different pesticides in forest watercourses, but<br />
pesticides that are or have been used in forests occur frequently<br />
(atrazine, hexazin<strong>on</strong>e <strong>and</strong> dimethoate).<br />
• There are many different pesticides in urban watercourses.<br />
• The distance requirements made in c<strong>on</strong>necti<strong>on</strong> with authorisati<strong>on</strong> of<br />
pesticides are expected to reduce <str<strong>on</strong>g>the</str<strong>on</strong>g> frequency of detecti<strong>on</strong> in <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
future.<br />
4.3 Pesticides in lakes <strong>and</strong> p<strong>on</strong>ds<br />
Pesticides enter lakes, coastal waters <strong>and</strong> p<strong>on</strong>ds via watercourses, surface<br />
run-off <str<strong>on</strong>g>from</str<strong>on</strong>g> adjacent l<strong>and</strong>, groundwater <strong>and</strong> atmospheric depositi<strong>on</strong>,<br />
including spray drift. The effects of pesticides in stagnant water are<br />
described in secti<strong>on</strong> 5.3. There are as yet no systematic data <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
occurrence of pesticides in Danish lakes <strong>and</strong> coastal waters. Data <str<strong>on</strong>g>from</str<strong>on</strong>g><br />
<str<strong>on</strong>g>the</str<strong>on</strong>g>se compartments are <str<strong>on</strong>g>the</str<strong>on</strong>g>refore not included in <str<strong>on</strong>g>the</str<strong>on</strong>g> report. In<br />
c<strong>on</strong>necti<strong>on</strong> with Aquatic Envir<strong>on</strong>ment Plan II, a measuring programme is<br />
being initiated, but results for lakes cannot be expected in <str<strong>on</strong>g>the</str<strong>on</strong>g> coming<br />
year.<br />
The studies <str<strong>on</strong>g>from</str<strong>on</strong>g> stagnant water cover results <str<strong>on</strong>g>from</str<strong>on</strong>g> two projects. One<br />
includes samples <str<strong>on</strong>g>from</str<strong>on</strong>g> four p<strong>on</strong>ds in <str<strong>on</strong>g>the</str<strong>on</strong>g> Køge district (Spliid, Mogensen<br />
1995), while <str<strong>on</strong>g>the</str<strong>on</strong>g> o<str<strong>on</strong>g>the</str<strong>on</strong>g>r includes a number of p<strong>on</strong>ds in South Funen <strong>and</strong><br />
Avernakø (Briggs in press). In both districts, <str<strong>on</strong>g>the</str<strong>on</strong>g> p<strong>on</strong>ds are in fields with<br />
clayey soil. Many field p<strong>on</strong>ds have nei<str<strong>on</strong>g>the</str<strong>on</strong>g>r inflow nor outflow. It must<br />
<str<strong>on</strong>g>the</str<strong>on</strong>g>refore be expected that pesticides remain in <str<strong>on</strong>g>the</str<strong>on</strong>g>m l<strong>on</strong>ger than in<br />
watercourses <strong>and</strong> that <str<strong>on</strong>g>the</str<strong>on</strong>g> risk to <str<strong>on</strong>g>the</str<strong>on</strong>g> aquatic organisms in <str<strong>on</strong>g>the</str<strong>on</strong>g>m is greater.<br />
The results of <str<strong>on</strong>g>the</str<strong>on</strong>g>se studies are given in table 4.12.<br />
The c<strong>on</strong>centrati<strong>on</strong> interval in <str<strong>on</strong>g>the</str<strong>on</strong>g> table indicates <str<strong>on</strong>g>the</str<strong>on</strong>g> lowest <strong>and</strong> highest<br />
c<strong>on</strong>centrati<strong>on</strong> in <str<strong>on</strong>g>the</str<strong>on</strong>g> samples in which <str<strong>on</strong>g>the</str<strong>on</strong>g> pesticide in questi<strong>on</strong> was<br />
detected. Column 3 shows <str<strong>on</strong>g>the</str<strong>on</strong>g> number of samples analysed for <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
pesticide in questi<strong>on</strong> <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> number of samples in which <str<strong>on</strong>g>the</str<strong>on</strong>g> substance<br />
was detected. All <str<strong>on</strong>g>the</str<strong>on</strong>g> substances for which <str<strong>on</strong>g>the</str<strong>on</strong>g> samples were analysed<br />
were detected, with <str<strong>on</strong>g>the</str<strong>on</strong>g> excepti<strong>on</strong> of bromoxynil <strong>and</strong> simazine. The<br />
highest c<strong>on</strong>centrati<strong>on</strong> for an individual substance was 11 microgrammes<br />
per litre.<br />
Table 4.12<br />
Pesticides detected in p<strong>on</strong>ds in Danish farml<strong>and</strong> in studies carried out by<br />
DMU in 1989-1991 <strong>and</strong> by Amphic<strong>on</strong>sult in 1994-1995 (Mogensen,<br />
Spliid 1997)