Report from the Sub-comittee on the environment and health

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• In <strong>the</strong> health assessment of pesticides, particularly with respect to risk groups, greater account should be taken of <strong>the</strong> fact that many different chemical substances are taken in at <strong>the</strong> same time. 133
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The Bichel Committee 1999 R
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1 INTRODUCTION 7 2 THE SUB-COMMITTE
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9 ENVIRONMENTAL AND HEALTH ASSESSME
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1 Introduction On 15 May 1997 <stro
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The President Members 10 Henrik San
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Consultants’ reports 12 The sub-c
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14 4 Occurrence of pesticides in <s
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The Nationwide Monitoring Programme
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Counties analyse samples fr
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20 system. However, the</st
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941 110 22 MB 270 31 13 MB 1281 10
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Substance Permitte
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26 The distribution of finds of pes
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28 concentrations of up to 11 micro
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Table 4.10 Occurrence of pesticides
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32 It will be seen from</st
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34 • The frequency of detection i
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36 Soil water samples containing pe
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38 Bromoxynil 3 n.d. 0.04 54 DNOC 4
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40 concentrations found so far are
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42 mononitrophenols and oth
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44 The main measure used to try to
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Models for volatilisation 46 • It
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Calculation of the
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Processes that remove pesticides <s
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52 atrazine and the</strong
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Potential sources of pesticides in
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56 Example 1: IPU dosage 1000 g act
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58 completely against future pollut
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Exposure of field fauna through tre
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Leaf beetles Direct effects of spra
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Indirect effects on mammals and bir
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Birds are particularly interesting
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Importance of headland vegetation t
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Effects of pesticides in forestry A
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Repeated spraying changes t
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Effect on seed production The wild
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Impact on the flor
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• The sub-committee recommends mo
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Effects on primary producers The ef
Page 84 and 85: Effects on amphibians Unlawful use
Page 86 and 87: concentrations than the</st
Page 88: The sub-committee recommends more c
Page 91 and 92: General ergonomic problems Particul
Page 93 and 94: Tractor accidents Accidents resulti
Page 95 and 96: The sprayer operator’s exposure t
Page 97 and 98: Pesticides and cancer 96 th
Page 99 and 100: Studies of frequency of cancer Repr
Page 101 and 102: Neurotoxicity Immunotoxicity and se
Page 103 and 104: Population studies 102 • Long-ter
Page 105 and 106: Other risk groups
Page 107 and 108: 106 tomat salat kinakål kartofler
Page 109 and 110: Calculation of pesticide intake <st
Page 111 and 112: The Danes’ dietary pattern Reduct
Page 113 and 114: Estimated intake from</stro
Page 115 and 116: Table 6.4 Estimated pesticide intak
Page 117 and 118: Variation in daily intake of pestic
Page 119 and 120: Endosulfan = Endosulfan Methidathio
Page 121 and 122: Limit values Authorisation of pesti
Page 123 and 124: Analytical studies: case control st
Page 125 and 126: Cancer Mechanism behind the
Page 127 and 128: Neurotoxicity Neurotoxicity in chil
Page 129 and 130: 128 6.2.7 Conclusions There is insu
Page 131 and 132: 130 • It cannot be proven on <str
Page 133: 132 Danish products. There are big
Page 137 and 138: Definition of proportionality Heavy
Page 139 and 140: Tropospheric ozone Veterinary drugs
Page 141 and 142: 140 effect that can be expected per
Page 143 and 144: Synthetic pesticid
Page 145 and 146: 144 formulations. Therefore, <stron
Page 147 and 148: International cooperation 146 be il
Page 149 and 150: Fuzzy Expert model Expert assessmen
Page 151 and 152: Setting up a gross list with a view
Page 153 and 154: Better monitoring of the</s
Page 155 and 156: 154 help in the as
Page 157 and 158: Impact index for the</stron
Page 159 and 160: Knowledge-building in the</
Page 161 and 162: 160 In relation to the</str
Page 163 and 164: Uncertainties and variations 162 A
Page 165 and 166: 164 which is fixed at 0.1 microgram
Page 167 and 168: 166 If the risk as
Page 169 and 170: Prevention of disease in cereal cro
Page 171 and 172: Prevention of pest attack in agricu
Page 173 and 174: 172 plants whose ability to establi
Page 175 and 176: Biobeds Municipal environmental sup
Page 177 and 178: Malt barley and gushing Direct effe
Page 179 and 180: Effect of soil treatment on wild pl
Page 181 and 182: Emissions of greenhouse gases 180 p
Page 183 and 184: Conclusions concerning environmenta
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Conclusions concerning leaching of
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0+-scenario: almost total phase-out
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Scenarios for forests Weath
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Soil Residues in the</stron
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Impact on the fiel
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Earthworms 194 has been carried out
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Assumptions and uncertainties Resul
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Comparison of weed control with and
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Results of calculations with <stron
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202 Scenarier Ingen behandling Plus
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Impacts on the flo
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Results of the mod
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Mechanical weed control 208 Behandl
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The Dane's dietary pattern and dail
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212 11 The sub-committee’s summar
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Conclusion concerning lack of time
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Conclusion concerning impacts on fl
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Conclusions concerning model analys
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Conclusions concerning exposure to
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Conclusion concerning mycotoxins Th
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Ranking with respect to groundwater
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Conclusion concerning emissions of
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Conclusions concerning natural subs
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230 12 References Abell, A., Bonde,
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232 Colborn, T., vom Saal., F.S., S
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234 Eyer, P. (1995). Neuropsychopat
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236 Graae, B.J. (1999). Florest flo
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238 Protection Conference: Pesticid
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240 Lindhardt, B., Sørensen, P.B.,
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242 consumption of fossil energy wi
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244 intoxication. The Pesticide Hea
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246 Underudvalget for Miljø og Sun
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248 Annex 1 Data required for autho
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250 11) Metabolism in animals The s
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252 Annex 2 The general rules for r
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Category 1 Category 2 Category 3 25
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256 reasonable and usable system fo
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Report from the Sub-comittee on the environment and health

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