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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.

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