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Report from the Sub-comittee on the environment and health

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The Dane's dietary pattern<br />

<strong>and</strong> daily intake of<br />

pesticides<br />

Calculati<strong>on</strong> of <str<strong>on</strong>g>the</str<strong>on</strong>g> daily<br />

intake in different<br />

scenarios for reduced use<br />

of pesticides<br />

210<br />

gave <str<strong>on</strong>g>the</str<strong>on</strong>g> Veterinary & Food Administrati<strong>on</strong> cause for c<strong>on</strong>cern with<br />

respect to public <strong>health</strong> (Büchert, Engell 1998).<br />

There is a lack of data <strong>on</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> distributi<strong>on</strong> of Danish c<strong>on</strong>sumpti<strong>on</strong><br />

between Danish <strong>and</strong> imported food products. The main reas<strong>on</strong> for that is,<br />

that with <str<strong>on</strong>g>the</str<strong>on</strong>g> "internal market", official statistics are no l<strong>on</strong>ger kept of<br />

imports <strong>and</strong> exports between <str<strong>on</strong>g>the</str<strong>on</strong>g> Member States. On <str<strong>on</strong>g>the</str<strong>on</strong>g> basis of earlier<br />

trade figures <strong>and</strong> agricultural statistics, it has been estimated that <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

distributi<strong>on</strong> between imports <strong>and</strong> domestic producti<strong>on</strong> is 1:1 for such<br />

fruit as apples, pears, plums, berries, etc., while exotic fruit, such as<br />

citrus fruit <strong>and</strong> kiwi, are all imported food products. For vegetables, <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

distributi<strong>on</strong> is about 1:4, although not for cucumber, tomatoes <strong>and</strong><br />

similar, where imports, distributed over <str<strong>on</strong>g>the</str<strong>on</strong>g> whole year, account for about<br />

70% of <str<strong>on</strong>g>the</str<strong>on</strong>g> total c<strong>on</strong>sumpti<strong>on</strong>. In <str<strong>on</strong>g>the</str<strong>on</strong>g> case of cereals, maize <strong>and</strong> rice are<br />

exclusively imported food products, while <str<strong>on</strong>g>the</str<strong>on</strong>g> c<strong>on</strong>sumpti<strong>on</strong> of barley is<br />

based entirely <strong>on</strong> Danish products. In <str<strong>on</strong>g>the</str<strong>on</strong>g> case of rye, wheat <strong>and</strong> oats, 5%,<br />

20% <strong>and</strong> 65%, respectively, of c<strong>on</strong>sumpti<strong>on</strong> is covered by imports.<br />

The variati<strong>on</strong> in <str<strong>on</strong>g>the</str<strong>on</strong>g> Danish c<strong>on</strong>sumers' dietary pattern can be judged <strong>on</strong><br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> basis of <str<strong>on</strong>g>the</str<strong>on</strong>g> Nati<strong>on</strong>al Food Agency's dietary study in 1995. The<br />

results of this study, which covered more than 1,800 pers<strong>on</strong>s, are<br />

summarised in table 6.2 in secti<strong>on</strong> 6.2. This table gives <str<strong>on</strong>g>the</str<strong>on</strong>g> average<br />

intake <strong>and</strong> selected fractiles for <str<strong>on</strong>g>the</str<strong>on</strong>g> adult populati<strong>on</strong>. The intake of<br />

pesticide residues was calculated as described in secti<strong>on</strong> 6.2 for all <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

pesticides detected in <str<strong>on</strong>g>the</str<strong>on</strong>g> studies of fruit <strong>and</strong> vegetables in 1996 <strong>and</strong><br />

1997. The intakes <str<strong>on</strong>g>from</str<strong>on</strong>g> Danish <strong>and</strong> imported food products were<br />

calculated separately, without detailed specificati<strong>on</strong> of <str<strong>on</strong>g>the</str<strong>on</strong>g> origin of <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

products (for details, see Büchert 1998). The results show a total average<br />

intake of pesticides of 190 microgrammes per day. The intake of 6<br />

pesticides/groups of pesticides, carbendazim, dithiocarbamates,<br />

iprodi<strong>on</strong>e, o-phenyl-phenol, procymid<strong>on</strong> <strong>and</strong> thiabendazol, corresp<strong>on</strong>ds<br />

to half <str<strong>on</strong>g>the</str<strong>on</strong>g> total intake, 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 half is distributed over about 60<br />

individual compounds.<br />

The total average load <str<strong>on</strong>g>from</str<strong>on</strong>g> food products is estimated to be approx. 200<br />

microgrammes of pesticide per day, more than half of which comes <str<strong>on</strong>g>from</str<strong>on</strong>g><br />

some few types of food products – namely, citrus fruit, potatoes <strong>and</strong><br />

apples. Around 60% comes <str<strong>on</strong>g>from</str<strong>on</strong>g> imported products <strong>and</strong> 40% <str<strong>on</strong>g>from</str<strong>on</strong>g><br />

Danish products. There are big variati<strong>on</strong>s in <str<strong>on</strong>g>the</str<strong>on</strong>g> calculated numerical<br />

values, <strong>and</strong>, in practice, <str<strong>on</strong>g>the</str<strong>on</strong>g> total intake is estimated to lie between very<br />

low <strong>and</strong> about 600 microgrammes per day. However, since most of <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

residual c<strong>on</strong>tent in citrus fruit is in <str<strong>on</strong>g>the</str<strong>on</strong>g> peel, which is not eaten, <str<strong>on</strong>g>the</str<strong>on</strong>g> actual<br />

daily intake of pesticides is less than 200 microgrammes per day. In this<br />

estimate, <str<strong>on</strong>g>the</str<strong>on</strong>g> intake via Danish products accounts for more than 50% of<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> total intake.<br />

The calculati<strong>on</strong>s of <str<strong>on</strong>g>the</str<strong>on</strong>g> daily intake cover both Danish <strong>and</strong> imported food<br />

products. Assuming that <str<strong>on</strong>g>the</str<strong>on</strong>g> diet's relative compositi<strong>on</strong> of Danish <strong>and</strong><br />

imported food products does not change, <str<strong>on</strong>g>the</str<strong>on</strong>g> daily intake can be<br />

estimated for <str<strong>on</strong>g>the</str<strong>on</strong>g> scenarios set up. These involve a reducti<strong>on</strong> of <str<strong>on</strong>g>the</str<strong>on</strong>g> use of<br />

pesticides in Denmark of 31% in <str<strong>on</strong>g>the</str<strong>on</strong>g> ++scenario, 80% in <str<strong>on</strong>g>the</str<strong>on</strong>g> +scenario,<br />

95% in <str<strong>on</strong>g>the</str<strong>on</strong>g> 0+scenario <strong>and</strong> 100% in <str<strong>on</strong>g>the</str<strong>on</strong>g> 0-scenario. The results are shown<br />

in figure 10.12.

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