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Report from the Sub-comittee on the environment and health

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Importance of headl<strong>and</strong><br />

vegetati<strong>on</strong> to <str<strong>on</strong>g>the</str<strong>on</strong>g> fauna<br />

Effect of pattern of pesticide<br />

use <strong>on</strong> flora <strong>and</strong> fauna<br />

indirect, since herbicides <strong>and</strong> fungicides remove <str<strong>on</strong>g>the</str<strong>on</strong>g> food eaten by <str<strong>on</strong>g>the</str<strong>on</strong>g>se<br />

insect groups (Hald et al. 1994; Reddersen et al. 1998).<br />

The absence of herbicides, in particular, plays a major ecological role in<br />

headl<strong>and</strong>s because it results in a much richer flora, with <str<strong>on</strong>g>the</str<strong>on</strong>g> possibility of<br />

both flowering <strong>and</strong> seeding. The ground cover with different plant<br />

species is important as a food resource for herbivores, insects that visit<br />

flowers <strong>and</strong> seed-eaters, although <str<strong>on</strong>g>the</str<strong>on</strong>g> microclimate <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> possibility of<br />

c<strong>on</strong>cealment also play a role (Reddersen et al. 1998). Buffer z<strong>on</strong>es<br />

bordering <strong>on</strong> uncultivated small biotopes also mean that ground beetles<br />

<strong>and</strong> rove beetles can overwinter <str<strong>on</strong>g>the</str<strong>on</strong>g>re <strong>and</strong> return to <str<strong>on</strong>g>the</str<strong>on</strong>g> field in <str<strong>on</strong>g>the</str<strong>on</strong>g> spring.<br />

Certain comm<strong>on</strong> insect groups occur in <str<strong>on</strong>g>the</str<strong>on</strong>g> field <strong>on</strong>ly in <str<strong>on</strong>g>the</str<strong>on</strong>g> buffer z<strong>on</strong>e<br />

al<strong>on</strong>g uncultivated small biotopes, whe<str<strong>on</strong>g>the</str<strong>on</strong>g>r, as in <str<strong>on</strong>g>the</str<strong>on</strong>g> case of plant bugs<br />

<strong>and</strong> plant hoppers, <str<strong>on</strong>g>the</str<strong>on</strong>g>y live <str<strong>on</strong>g>the</str<strong>on</strong>g>re or, as in <str<strong>on</strong>g>the</str<strong>on</strong>g> case of harvest spiders,<br />

ants <strong>and</strong> woodlouse, <str<strong>on</strong>g>the</str<strong>on</strong>g>y are simply guests <str<strong>on</strong>g>from</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> boundary biotope.<br />

Only a few species of bird <strong>and</strong> small mammal live in <str<strong>on</strong>g>the</str<strong>on</strong>g> cultivated field,<br />

while <str<strong>on</strong>g>the</str<strong>on</strong>g> many species living in uncultivated small biotopes often go <strong>on</strong><br />

foraging excursi<strong>on</strong>s in <str<strong>on</strong>g>the</str<strong>on</strong>g> field edge: that applies, for example, to<br />

different species of mice <strong>and</strong> species of bird, such as yellowhammer,<br />

partridge <strong>and</strong> pheasant. Such species naturally potentially benefit <str<strong>on</strong>g>from</str<strong>on</strong>g><br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> ample food resources available to <str<strong>on</strong>g>the</str<strong>on</strong>g>m in unsprayed headl<strong>and</strong>s.<br />

Wild plants are an important <strong>and</strong> basic element in <str<strong>on</strong>g>the</str<strong>on</strong>g> agroecosystem’s<br />

species diversity, see earlier secti<strong>on</strong>s. Use of reduced herbicide dosages<br />

could be expected <strong>on</strong> average to leave more weed in Danish fields.<br />

Surviving plants could form a food resource for herbivorous insects,<br />

am<strong>on</strong>g o<str<strong>on</strong>g>the</str<strong>on</strong>g>rs, if <str<strong>on</strong>g>the</str<strong>on</strong>g> food quality of <str<strong>on</strong>g>the</str<strong>on</strong>g> host plants were adequate. This<br />

has been studied 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> knotgrass leaf beetle <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> herbicide<br />

Glean (Elmegaard, Kjær 1995; Kjær, Elmegaard 1996).<br />

There is generally reas<strong>on</strong> to assume that sublethally treated plants can<br />

form a food resource for herbivorous animals. The treated plants do not<br />

always have <str<strong>on</strong>g>the</str<strong>on</strong>g> same quality as untreated plants, but for herbivorous<br />

animals <strong>and</strong> seed-eaters, insects visiting flowers, etc. a little food is better<br />

than n<strong>on</strong>e.<br />

However, <str<strong>on</strong>g>the</str<strong>on</strong>g>re has not been any clear tendency towards an increase in<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> amount of weed due to <str<strong>on</strong>g>the</str<strong>on</strong>g> widespread use of reduced dosages – at<br />

any rate not when <str<strong>on</strong>g>the</str<strong>on</strong>g> registrati<strong>on</strong> takes place at harvest time (Kristensen<br />

1994). In o<str<strong>on</strong>g>the</str<strong>on</strong>g>r words, farmers have become better at spraying optimally<br />

<strong>and</strong> are achieving <str<strong>on</strong>g>the</str<strong>on</strong>g> same effect with reduced dosages. Studies have not<br />

been carried out of <str<strong>on</strong>g>the</str<strong>on</strong>g> development of weed throughout <str<strong>on</strong>g>the</str<strong>on</strong>g> seas<strong>on</strong> as a<br />

functi<strong>on</strong> of changes in <str<strong>on</strong>g>the</str<strong>on</strong>g> spraying pattern.<br />

Reduced dosages of insecticides are not widely used, but are<br />

recommended in certain cases by <str<strong>on</strong>g>the</str<strong>on</strong>g> Agricultural Advisory Service.<br />

For species with LD50 close to or above <str<strong>on</strong>g>the</str<strong>on</strong>g> corresp<strong>on</strong>ding field dose,<br />

repeated spraying will also increase <str<strong>on</strong>g>the</str<strong>on</strong>g> probability of <str<strong>on</strong>g>the</str<strong>on</strong>g> individual<br />

being hit <strong>and</strong> affected by an applicati<strong>on</strong>. The advantage or disadvantage<br />

of split dosing (i.e. <str<strong>on</strong>g>the</str<strong>on</strong>g> full dose is distributed over several applicati<strong>on</strong>s<br />

with reduced dose) for harmless organisms thus seems to depend <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

species’ sensitivity to <str<strong>on</strong>g>the</str<strong>on</strong>g> dosage used. It is <str<strong>on</strong>g>the</str<strong>on</strong>g>refore interesting to<br />

compare <str<strong>on</strong>g>the</str<strong>on</strong>g>se c<strong>on</strong>siderati<strong>on</strong>s with observati<strong>on</strong>s in <str<strong>on</strong>g>the</str<strong>on</strong>g> field. Split dosing<br />

69

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