- Page 2 and 3: Pesticide residues in food — 2007
- Page 4: TABLE OF CONTENTS Page List of part
- Page 7 and 8: Dr Vicki L. Dellarco, Office of Pes
- Page 10 and 11: Abbreviations used 3-MC ACTH ADI ai
- Page 12 and 13: MRL MS MS/MS MTD NMR NOAEC NOAEL NO
- Page 14: Introduction The toxicological mono
- Page 19 and 20: 4 Aminopyralid has not been evaluat
- Page 21 and 22: 6 Table 3. Tissue distribution of r
- Page 23 and 24: 8 The test material was 94.5% chemi
- Page 25 and 26: 10 One male rat died on test day 3,
- Page 27 and 28: 12 had slight irritation of the iri
- Page 29 and 30: 14 not dose-dependant. Sodium was a
- Page 31 and 32: 16 In a 13-week feeding study, grou
- Page 33 and 34: 18 Rat In a 24-month study of toxic
- Page 35 and 36: 20 2.4 Genotoxicity Aminopyralid (b
- Page 37 and 38: 22 change was considered to be a ph
- Page 39 and 40: 24 in one rabbit in the group at th
- Page 41 and 42: 26 respectively (Table 16). Gross p
- Page 43 and 44: 28 then radiolabelled aminopyralid
- Page 45 and 46: 30 moribund condition on day 17 of
- Page 47 and 48: 32 Critical end-points for setting
- Page 49 and 50: 34 Dryzga, M.D. & Stebbins, K.E. (2
- Page 51 and 52: 36 Wilson, C.W. (2001) Aminopyralid
- Page 53 and 54: 38 Appendix 1 Application of the IP
- Page 55 and 56: 40 urine, 24-28% in faeces, and 2-3
- Page 57 and 58: 42 24 h. Clearance of radioactivity
- Page 59 and 60: 44 and DACT (G 28273) using a gas c
- Page 61 and 62: 46 Figure 1. Proposed metabolic pat
- Page 63 and 64: 48 Figure 3. Primary metabolic path
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50 Table 3. Dermal irritation and s
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52 Table 4. Results of studies of c
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54 cholesterol of females at the hi
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56 No treatment-related effect on s
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58 From the rats in the supplementa
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60 There were no effects on clinica
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62 Body-weight gain was retarded by
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64 2.4 Genotoxicity Atrazine was te
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66 End-point Test system Concentrat
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68 Litter parameters, including lit
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70 Table 13. Relevant findings of a
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72 Dealkylation reactions at the 4
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74 In a test for DNA repair in vitr
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76 The NOAEL was 50 ppm, equal to 4
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78 (iii) Diaminochlorotriazine, DAC
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80 on control diet for a 39-week re
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82 Table 18. Relevant findings in a
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84 basophilia, minimal subacute int
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86 Hydroxyatrazine was not carcinog
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88 DEA and DIA significantly increa
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90 analysed for LH. Rats were necro
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92 gavage for 4 weeks; a group of 4
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94 a dose of 6.25 mg/kg bw (i.e. 12
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96 In a study on the effects of atr
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98 those in the control group that
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100 (h) Studies on estrogenic and a
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102 Although it has been reported t
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104 Immunological effects in B6C3F
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106 independent reviews (Neuberger,
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108 selected by random digit-dialle
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110 supported by a number of short-
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112 DEA, DIA and DACT did not show
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114 Special 6-month study a Special
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116 Group ARfD for atrazine, deethy
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118 Appendix 1 Application of the I
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120 greater, and in a 26-week study
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122 1. Comparison of the reproducti
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124 III. Can human relevance of the
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126 Cummings, A.M., Rhodes, B.E. &
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128 implications for endocrine disr
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130 IARC (1999) Atrazine. In: Some
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132 Meek, M.E., Bucher, J.R., Cohen
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134 Pino, A., Maura, A. & Grillo, P
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136 No. 2214-01 dated 4 March 2002
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138 Wise, P.M., Kashon, M.L., Krajn
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140 for c onsideration by the prese
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142 Figure 1. Proposed metabolic pa
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144 Benzazimide (azinphos-methyl me
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146 Table 3. Cholinesterase activit
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148 Table 5. Cholinesterase activit
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150 Table 7. Results of studies of
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152 Table 9. Pup parameters in rats
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154 Table 12. Inhibition of plasma,
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156 Deaths occurred in all groups,
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158 Treatment-related functional ob
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160 in males at 120 ppm and in fema
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162 on the day after cessation of t
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164 The main toxicological findings
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166 Levels relevant for risk assess
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168 Summary Value Study Safety fact
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170 Herbold, B.A. (1995) E1582 - Mi
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172 United States Environment Prote
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174 At its meeting in 2000, the Joi
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176 With cyclopropyl-labelled cyhal
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178 The patterns of metabolites der
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180 2. Toxicological studies 2.1 Ac
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182 months of treatment. At the sam
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184 of the dosing period and a redu
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186 (up to 26%) and triglycerides (
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188 weight or fetal crown/rump leng
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190 treatment with lambda-cyhalothr
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192 No other data on human observat
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194 In a 2-year dietary study with
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196 15 mg/kg bw per day 30 mg/kg bw
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198 Summary for cyhalothrin and lam
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200 Milburn, G.M. (2004) Lambda-cyh
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202 beet and several vegetable and
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204 Table 1. Key parameters of bloo
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206 differences in the percentage a
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208 2. Toxicological studies 2.1 Ac
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210 Signs of irritation were observ
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212 and 0, 4.6, 45.2 and 639 mg/kg
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214 ratios in males at all doses an
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216 The stability of difenoconazole
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218 Table 4. Treatment-related hist
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220 3000 ppm and 6000 ppm, but thes
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222 conducted on all mice during th
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224 Absolute liver weights and live
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226 Hepatocellular Early 0 2 0 2 0
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228 Blood chemistry measurements sh
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230 (a) Discussion of a possible mo
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232 toxic for this compound, partic
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234 after an exposure period of at
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236 male pups at 250 ppm were signi
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238 There were also no treatment-re
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240 Table 14. Incidence of skeletal
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242 Analyses of the sites of fetal
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244 weekly throughout the study. At
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246 Table 15. Scores for hindlimb g
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248 Table 17. Results of studies of
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250 Table 18. Studies of toxicity a
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252 1,2,4-Triazole does not modulat
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254 Table 20. Results of studies of
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256 recovery period. The microsomal
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258 Microscopic examinations reveal
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260 powder. The remaining one third
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262 16 deaths among females at 3000
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264 of allergic reaction to a formu
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266 Lowest relevant developmental N
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268 Gerspach, R. (2000) CGA 169374
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270 Melly, J. & Lohse, K. (1982) Mi
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272 Thomas, H. (1992) The effect of
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274 Explanation Dimethomorph is a c
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276 Profiles for urinary and faecal
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278 Table 7. Excretion pattern in r
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280 Table 9. Tissue distribution of
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282 In an additional study on possi
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284 2.2 Short-term studies of toxic
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286 To investigate the contribution
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288 groups at the highest dose, fem
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290 The ileums from all mice in the
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292 the control group were terminat
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294 the groups at weeks 11 (only ha
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296 in females). This study was con
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298 without metabolic activation (8
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300 Clinical observations, feed con
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302 weights measured and they were
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304 of them with signs of improper
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306 (j) Cardiovascular, respiratory
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308 that the increased incidence in
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310 Toxicological evaluation The Me
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312 Ainsworth, G.A. & Wright, A. (1
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314 Müller, W. (1989a) SAG 151 Ora
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FLUSILAZOLE First draft prepared by
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319 very low. Total residues exclud
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321 irritation, flusilazole (purity
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323 Dogs Groups of four male and fo
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325 Table 2. Incidence of liver tum
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327 deaths that occurred before ter
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329 Table 5. Results of studies of
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331 included: higher mortality (2 o
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333 98-99% in the control group and
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335 delivered by caesarean section
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337 Table 7. Incidence of hydroceph
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339 CYP3A and CYP4A isozymes). This
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341 Overall, the data suggested tha
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343 d Greater than the maximum tole
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345 Brock, W.J., Vick, D.A. & Chrom
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347 Schardein, J. (1998). A dermal
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350 Explanation Procymidone is the
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352 Comparative kinetics between sp
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354 Radioactivity in urine (%) —
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356 the applied dose in receptor fl
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358 qualitative autoradiography of
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360 Binding to plasma proteins The
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362 Table 9. Results of studies of
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364 for males and females at 2500 o
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366 daily for signs of toxicity; bo
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368 Groups of four male and four fe
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370 Table 17. Hepatic findings in a
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372 Table 19. Results of studies of
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374 Table 20. Findings in offspring
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376 (b) Developmental toxicity Rats
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378 The study did not identify a NO
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380 Table 25. Blood plasma kinetic
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382 Table 27. Dosing schedule and t
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384 Table 28. Ejaculate mass and te
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386 3. Studies on metabolites (a) 3
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388 Table 31. Metabolite concentrat
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390 females. The histopathological
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392 was a significant increase in t
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394 Levels relevant to risk assessm
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396 Summary Value Study Safety fact
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398 Kogiso, S. (1991) Reverse mutat
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400 Savides, M.C. (2002) The in viv
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PROFENOFOS First draft prepared by
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405 Similar results were obtained i
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407 1.3 Effects on enzymes and othe
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409 bw by gavage. An additional fiv
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411 within 12 days. No other detail
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413 treatment. Corneal opacity was
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415 All rats of the group at the hi
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417 The treatment produced no signi
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419 In another study, groups of fou
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421 p resence of nodules or masses
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423 intervals at 0.3 ppm, but never
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425 The study was not conducted in
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427 activity was inhibited by 21% a
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429 day during gestation and 0, 0.7
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431 muscularly 60 min before the se
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433 Comments Biochemical aspects [P
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435 Studies of developmental toxici
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437 Estimate of acceptable daily in
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439 Cannelongo, B.F. (1982b) CGA 15
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441 Loosli, R. (1989) Cholinesteras
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443 Williams, S.C., Marco, G.J., Si
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446 Evaluation for acceptable daily
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448 Table 2. Calculated pharmacokin
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450 time, while the concentration i
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452 Sum 91.5 — — — — —
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454 Mice In a study of absorption,
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456 findings were observed on necro
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458 was observed (relative to contr
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460 The deaths were considered to b
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462 The LOAEL was 8000 ppm (529.1 a
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464 e xamination was performed befo
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466 43%, 71% and 59% (control, lowe
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468 At interim kill, no significant
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470 2.5 Reproductive toxicity (a) M
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472 necropsy. The uterus and ovarie
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474 (b) Short-term studies of neuro
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476 were noted at day 4. Liver weig
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478 In a 90-day dietary study of to
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480 Levels relevant to risk assessm
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482 Beyrouty, P. (2001b) A time of
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484 Hemmings, P.A. (1991a) Residue
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486 Simpson, E. (2003) Historical c
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488 All the pivotal studies met the
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490 or distribution of [ 14 C]zoxam
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492 indicated that zoxamide is very
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494 Metabolite RH141,452 (3,5-dichl
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496 2.2 Short-term studies of toxic
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498 The only findings of note were
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500 canine juvenile polyarteritis s
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502 Table 10. Organ weight and hist
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504 Week 52 3 167 2 795 2 538 2 052
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506 weights were increased in a dos
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508 The zoxamide metabolites, RH 14
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510 Table 15 Pup body weights durin
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512 consumption were monitored thro
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514 anti-tubulin compounds at 37 °
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516 were higher than those of the c
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518 Acute neurotoxicity b 2000 mg/k
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520 Ferguson, J.S., Morrison, R.D.
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522 Snyder, P.W., Kazacos, E.A., Sc
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524 14. Pesticide residues in food.
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526 50. Pesticide residues in food
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528 84. Pesticide residues in food