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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The sub-committee’s<br />
recommendati<strong>on</strong>s<br />
c<strong>on</strong>cerning <str<strong>on</strong>g>the</str<strong>on</strong>g> impacts of<br />
pesticides in <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
envir<strong>on</strong>ment<br />
86<br />
aquatic ecosystems. In <str<strong>on</strong>g>the</str<strong>on</strong>g> case of <str<strong>on</strong>g>the</str<strong>on</strong>g> aquatic envir<strong>on</strong>ment, any effect<br />
<str<strong>on</strong>g>from</str<strong>on</strong>g> pesticides is undesirable, including changes of flora <strong>and</strong> fauna in<br />
coastal waters, lakes, p<strong>on</strong>ds <strong>and</strong> watercourses. Am<strong>on</strong>g <str<strong>on</strong>g>the</str<strong>on</strong>g> aquatic<br />
ecosystems, it is particularly p<strong>on</strong>ds, watercourses <strong>and</strong> lakes near fields<br />
that could potentially be affected.<br />
The freshwater envir<strong>on</strong>ment is in all probability affected by <str<strong>on</strong>g>the</str<strong>on</strong>g> present<br />
use of pesticides, but it is not possible <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> basis of <str<strong>on</strong>g>the</str<strong>on</strong>g> existing data to<br />
quantify <str<strong>on</strong>g>the</str<strong>on</strong>g> magnitude of <str<strong>on</strong>g>the</str<strong>on</strong>g> impact nati<strong>on</strong>ally. On <str<strong>on</strong>g>the</str<strong>on</strong>g> basis of<br />
informati<strong>on</strong> <str<strong>on</strong>g>from</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> county authorities, it is provisi<strong>on</strong>ally estimated that<br />
around 2% of <str<strong>on</strong>g>the</str<strong>on</strong>g> unfulfilled targets of about 11,000 km watercourses can<br />
be due to toxic substances, including pesticides. In particular, <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
c<strong>on</strong>centrati<strong>on</strong> levels measured indicate that it is insecticides – <strong>and</strong><br />
especially pyrethroids – that can have an adverse effect. Owing to <str<strong>on</strong>g>the</str<strong>on</strong>g>ir<br />
persistence, pyrethroids can also occur in <str<strong>on</strong>g>the</str<strong>on</strong>g> freshwater ecosystems for a<br />
l<strong>on</strong>g period of time. There are also documented cases of effects of<br />
herbicides <strong>on</strong> algae <strong>and</strong> o<str<strong>on</strong>g>the</str<strong>on</strong>g>r primary producers. Several measurements<br />
indicate c<strong>on</strong>centrati<strong>on</strong>s of pyrethroids <strong>and</strong> certain thiophosphate<br />
insecticides that are close to <str<strong>on</strong>g>the</str<strong>on</strong>g> level that has effects according to <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
existing literature. For some pesticides, this level is lower than <str<strong>on</strong>g>the</str<strong>on</strong>g> limit<br />
value of 0.1 microgramme per litre for drinking water.<br />
In both cultivated areas <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> adjacent biotopes, <str<strong>on</strong>g>the</str<strong>on</strong>g> use of pesticides<br />
involves a risk of reduced populati<strong>on</strong>s of flora <strong>and</strong> fauna, changed<br />
biodiversity, changes in <str<strong>on</strong>g>the</str<strong>on</strong>g> cultivati<strong>on</strong> medium <strong>and</strong> natural pest<br />
regulati<strong>on</strong>, <strong>and</strong> of food-chain effects <strong>and</strong> o<str<strong>on</strong>g>the</str<strong>on</strong>g>r indirect effects. Seen<br />
overall, it is not <str<strong>on</strong>g>the</str<strong>on</strong>g> individual field <strong>and</strong> its possible loss of wild flora that<br />
are <str<strong>on</strong>g>the</str<strong>on</strong>g> problem, but ra<str<strong>on</strong>g>the</str<strong>on</strong>g>r <str<strong>on</strong>g>the</str<strong>on</strong>g> total, countrywide effects <strong>on</strong> characteristic<br />
farml<strong>and</strong> flora <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> associated fauna.<br />
In forestry, very little use is made of pesticides, whereas, in Christmas<br />
tree <strong>and</strong> ornamental greenery cultures, <str<strong>on</strong>g>the</str<strong>on</strong>g> same quantities are used as in<br />
farming. The treatment frequency index in nurseries <strong>and</strong> market gardens<br />
is high. There is a lack of specific studies of <str<strong>on</strong>g>the</str<strong>on</strong>g> effect of herbicides <strong>on</strong><br />
forest-floor plant species, but <str<strong>on</strong>g>the</str<strong>on</strong>g>re is no doubt that even <str<strong>on</strong>g>the</str<strong>on</strong>g> limited use<br />
made of pesticides in forestry has adverse effects. Many woodl<strong>and</strong> plant<br />
species have a very slow recol<strong>on</strong>isati<strong>on</strong> rate of less than 1 metre per year,<br />
which makes <str<strong>on</strong>g>the</str<strong>on</strong>g>m particularly sensitive to herbicides, even though <str<strong>on</strong>g>the</str<strong>on</strong>g>se<br />
are <strong>on</strong>ly applied in c<strong>on</strong>necti<strong>on</strong> with clear cutting <strong>and</strong> afforestati<strong>on</strong>.<br />
For <str<strong>on</strong>g>the</str<strong>on</strong>g> scenarios in which pesticides are used, <str<strong>on</strong>g>the</str<strong>on</strong>g>re are no systematic<br />
studies of how pesticides in large, c<strong>on</strong>nected areas affect wild flora <strong>and</strong><br />
<str<strong>on</strong>g>the</str<strong>on</strong>g> associated fauna in hedgerows, waysides <strong>and</strong> o<str<strong>on</strong>g>the</str<strong>on</strong>g>r small biotopes<br />
<strong>and</strong> in neighbouring nature areas. The effects <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> flora caused by<br />
precipitati<strong>on</strong> of l<strong>on</strong>g-distance transported herbicides in Denmark is not<br />
known. Foreign studies show that effects probably exist, but fur<str<strong>on</strong>g>the</str<strong>on</strong>g>r<br />
investigati<strong>on</strong>s of both <str<strong>on</strong>g>the</str<strong>on</strong>g> atmospheric transport <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> effects are<br />
needed for any closer determinati<strong>on</strong>. There is also a need to assess <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
effect of pesticides <strong>on</strong> aquatic organisms in relati<strong>on</strong> to <str<strong>on</strong>g>the</str<strong>on</strong>g> actual finds in<br />
watercourses <strong>and</strong> surface water. The sub-committee recommends that <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
necessary knowledge be built up <strong>and</strong> that time series be established to<br />
document any effects <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> terrestrial <strong>and</strong> aquatic ecosystems seen in<br />
relati<strong>on</strong> to <str<strong>on</strong>g>the</str<strong>on</strong>g> proven occurrence of pesticides in <str<strong>on</strong>g>the</str<strong>on</strong>g> envir<strong>on</strong>ment.