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Application for the Reassessment of a Hazardous Substance under ...

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levels, analytical dichlorvos concentrations were 0.08, 0.80, 8.0, 80 and 400ppm after 12 h[ours], declining to 0.022, 0.224, 2.24, 22 and 112 ppm after156 h[ours], respectively. Average concentrations <strong>of</strong> dichlorvos were 0.047,0.467, 4.67, 46.7 and 234 ppm. The average DCA content present was0.014, 0.114, 0.887, 6.86 and 28.6 ppm in <strong>the</strong>se groups, respectively.“Mortalities, clinical signs and bodyweight effects: There was no treatmentrelatedeffect on mortalities, clinical signs or bodyweight gain.“Haematology, clinical chemistry and urinalysis: There was no treatmentrelatedeffect on any heamatology, clinical chemistry or urinary parameter.ChE activity: Plasma and RBC ChE activities were measured 13 timesduring <strong>the</strong> study, with no significant effects observed in <strong>the</strong> three lowestdose groups. In <strong>the</strong> 100 ppm group, plasma and RBC ChE activities werereduced to 60-90% and to 50-90% <strong>of</strong> controls in males and females,respectively. In <strong>the</strong> 500 ppm group, activities were reduced to 20-70% and20-60%, respectively. Activities tended to increase as <strong>the</strong> study progressed.At termination, brain ChE activity was significantly decreased only in <strong>the</strong>500 ppm group, by 45-47% in rats sacrificed after 6 months, declining to 5-15% in those sacrificed after 24 months.“Pathology: There was no treatment-related effect on organ weights <strong>of</strong> ratssacrificed at scheduled intervals or at termination, and <strong>the</strong>re were notreatment-related macroscopic lesions. Histology revealed hepatocellularfatty vacuolisation in all 500 ppm rats, and in approximately 80% <strong>of</strong> femalesand 62% <strong>of</strong> males at 100 ppm. This was only evident in animals sacrificedafter 18 or 24 months. All neoplastic lesions were benign, with mostoccurring in <strong>the</strong> mammary and pituitary glands <strong>of</strong> both sexes without dosedependency.There were no tumours that occurred only at <strong>the</strong> high-dose.Overall, no treatment-related effects were observed on <strong>the</strong> incidence ortiming <strong>of</strong> tumours.“Conclusion: The NOEL following 2-years <strong>of</strong> dietary exposure todichlorvos was 10 ppm (mean analytical concentration <strong>of</strong> 4.67 ppm;equivalent to 0.23 mg/kg bw/d[ay]) based on <strong>the</strong> inhibition <strong>of</strong> plasma andRBC ChE activity at and above 100 ppm (mean analytical concentration46.7 ppm; equivalent to 2.3 mg/kg bw/d[ay]). Hepatocellular abnormalitieswere evident at 100 and 500 ppm, but <strong>the</strong>se were insufficient to indicateimpairment <strong>of</strong> normal liver function.‖ (Original not sighted; APVMA,2008a)The ATSDR (1997) reported:“In a 90-day study in female Sherman rats, groups <strong>of</strong> 10 animals wereexposed to doses ranging from 0 to 69.9 mg/kg [b.w.]/day in <strong>the</strong>ir feed(Durham et al. 1957). Two animals from each group were bled on days3, 11, 60, and 90, and serum cholinesterase and erythrocyteacetylcholinesterase were determined. Clinical signs <strong>of</strong> neurologicaltoxicity were not noted in any dosage group. Cholinesterase data waspresented graphically so <strong>the</strong> percentage inhibition <strong>of</strong> <strong>the</strong>Dichlorvos reassessment – application Page 236 <strong>of</strong> 436

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