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Report from the Sub-comittee on the environment and health

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Ranking with respect to<br />

impacts <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> terrestrial<br />

envir<strong>on</strong>ment<br />

The sub-committee’s<br />

recommendati<strong>on</strong>s<br />

c<strong>on</strong>cerning impacts <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

terrestrial envir<strong>on</strong>ment<br />

Ranking with respect to <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

aquatic envir<strong>on</strong>ment<br />

The sub-committee’s<br />

recommendati<strong>on</strong> with<br />

respect to <str<strong>on</strong>g>the</str<strong>on</strong>g> aquatic<br />

envir<strong>on</strong>ment<br />

Ranking with respect to<br />

public <strong>health</strong><br />

The sub-committee’s<br />

recommendati<strong>on</strong>s with<br />

respect to public <strong>health</strong><br />

C<strong>on</strong>clusi<strong>on</strong> c<strong>on</strong>cerning<br />

changes in energy<br />

c<strong>on</strong>sumpti<strong>on</strong><br />

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> terrestrial envir<strong>on</strong>ment it is not possible to indicate a<br />

method for ranking <str<strong>on</strong>g>the</str<strong>on</strong>g> direct effects because it is <str<strong>on</strong>g>the</str<strong>on</strong>g> indirect effects <strong>and</strong><br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> combinati<strong>on</strong> of many pesticides that play <str<strong>on</strong>g>the</str<strong>on</strong>g> biggest role. However,<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> treatment frequency index can be used as a measure of <str<strong>on</strong>g>the</str<strong>on</strong>g> load<br />

because it is based <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> biologically active field dosage <strong>and</strong> is thus a<br />

simple indicator of both <str<strong>on</strong>g>the</str<strong>on</strong>g> direct effect <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> target organisms <strong>and</strong><br />

<str<strong>on</strong>g>the</str<strong>on</strong>g>ir related species <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> indirect load <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> ecosystem as a<br />

c<strong>on</strong>sequence of changes in <str<strong>on</strong>g>the</str<strong>on</strong>g> quantity <strong>and</strong> type of food resources in <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

food chains. It would also be possible to calculate an index for <str<strong>on</strong>g>the</str<strong>on</strong>g> dose<br />

that, as far as is known at present, would be harmless to <str<strong>on</strong>g>the</str<strong>on</strong>g> vast majority<br />

of <str<strong>on</strong>g>the</str<strong>on</strong>g> flora <strong>and</strong> fauna in uncultivated areas that receive pesticides via<br />

spray drift or atmospheric transport (critical loads).<br />

As a starting point, <str<strong>on</strong>g>the</str<strong>on</strong>g> sub-committee recommends that <str<strong>on</strong>g>the</str<strong>on</strong>g> treatment<br />

frequency index be used as index for <str<strong>on</strong>g>the</str<strong>on</strong>g> entire load <strong>on</strong> flora <strong>and</strong> fauna in<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> field <strong>and</strong> its immediate surroundings.<br />

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, in <str<strong>on</strong>g>the</str<strong>on</strong>g> present authorisati<strong>on</strong><br />

scheme an expert assessment is carried out that can lead to authorisati<strong>on</strong><br />

of new pesticides or products <strong>on</strong> certain c<strong>on</strong>diti<strong>on</strong>s c<strong>on</strong>cerning distance<br />

to watercourses <strong>and</strong> lakes. Such distance requirements indicate that <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

substance (<str<strong>on</strong>g>the</str<strong>on</strong>g> product) is problematical with respect to aquatic<br />

organisms <strong>and</strong> could be used directly for ranking or classifying<br />

pesticides.<br />

The sub-committee recommends that <str<strong>on</strong>g>the</str<strong>on</strong>g> administratively set distance<br />

requirements be used for ranking or classifying pesticides.<br />

For <str<strong>on</strong>g>the</str<strong>on</strong>g> human-toxicological area <strong>on</strong>e could use <str<strong>on</strong>g>the</str<strong>on</strong>g> relati<strong>on</strong>ship between<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> Acceptable Daily Intake, ADI, <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> estimated exposure to <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

substance as <str<strong>on</strong>g>the</str<strong>on</strong>g> basis for ranking pesticides. Generally speaking, with<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> current use of pesticides, <str<strong>on</strong>g>the</str<strong>on</strong>g> exposure at single substance level<br />

through food products is around 1% or less of ADI. A ranking scheme<br />

would enable identificati<strong>on</strong> of substances that, with <str<strong>on</strong>g>the</str<strong>on</strong>g>ir present use,<br />

have <str<strong>on</strong>g>the</str<strong>on</strong>g> lowest safety margin for humans. However, since <str<strong>on</strong>g>the</str<strong>on</strong>g> effects of<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> individual substances are not comparable, a ranking scheme would<br />

not suffice al<strong>on</strong>e but would have to be supplemented by an expert<br />

assessment.<br />

The sub-committee recommends that a ranking scheme be based <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

relati<strong>on</strong>ship between <str<strong>on</strong>g>the</str<strong>on</strong>g> Acceptable Daily Intake of <str<strong>on</strong>g>the</str<strong>on</strong>g> individual active<br />

ingredient <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> actual intake.<br />

11.8 The sub-committee’s c<strong>on</strong>clusi<strong>on</strong>s c<strong>on</strong>cerning energy<br />

c<strong>on</strong>sumpti<strong>on</strong>, emissi<strong>on</strong>s of greenhouse gases <strong>and</strong> nutrient<br />

leaching<br />

In <str<strong>on</strong>g>the</str<strong>on</strong>g> event of restructuring for pesticide-free agriculture, <str<strong>on</strong>g>the</str<strong>on</strong>g> direct<br />

energy cost for mechanical weed c<strong>on</strong>trol would rise, but would be offset<br />

to some extent by a saved, indirect energy cost for producti<strong>on</strong> of<br />

pesticides. The sub-committee c<strong>on</strong>cludes that <str<strong>on</strong>g>the</str<strong>on</strong>g> total energy cost for<br />

225

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