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Appendix D - Dossier (PDF) - Tera
Appendix D - Dossier (PDF) - Tera
Appendix D - Dossier (PDF) - Tera
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date: 20–JUL–2005<br />
5. Toxicity Substance ID: 71–43–2<br />
______________________________________________________________________________<br />
fold increase after exposure to 100 ppm (P
date: 20–JUL–2005 5. Toxicity Substance ID: 71–43–2 ______________________________________________________________________________ fold increase after exposure to 100 ppm (P
date: 20–JUL–2005 5. Toxicity Substance ID: 71–43–2 ______________________________________________________________________________ For biological monitoring, a urine sample was collected 4 hr into the work shift and analysed for unchanged benzene (headspace GC, limit of detection 0.05 ug/l) and t,t–muconic acid (t,t–MA; HPLC with UV detection, limit of detection 10 ug/l). Airborne exposure of the traffic wardens to benzene was determined using passive samplers, worn for 6 hr during a work shift. Exposure of laboratory staff was estimated from passive area monitoring (2 or 3 devices placed in the laboratory throughout an 8 hr work shift). Samples were analysed using GC–MS. DETERMINATION OF MICRONUCLEI (MN) Peripheral lymphocytes were isolated from heparinised blood by gradient centrifugation and grown in culture for 72 hr (1% phytohaemagglutin) prior to addition of cytochalasin B. Preparations were stained with May Grunwald–Giemsa, and 2000 binucleate lymphocytes per subject scored blind. Cell cycle parameters (number of nuclei) were evaluated on 1000 cells and the nuclear division index (NDI; mean number of nuclei/cell) calculated. STATISTICAL METHODS Results were analysed using Wilkoxon rank–sum and Kruskall–Wallis tests. Multiple regression (Ramsey omitted variable test; Cook–Weisberg heteroscedasticity test) of transformed data (Box–Cox method) was used to test possible associations between the presence of micronuclei in blood with benzene exposure and environmental factors. Result: EXPOSURE ANALYSES The following mean exposures (range in parentheses) were obtained for the overall study population: <strong>Appendix</strong> D: Benzene SIDS <strong>Dossier</strong> Airborne benzene: 4.37 ppb (0–14.30)* Urinary benzene: 0.66 ug/l (0–4.77) Urinary t,t–MA: 106 ug/l (7–721) * personal and environmental samples combined Following Box–Cox transformation, no significant correlation was found between benzene in air and benzene in urine (R^2 = 0.09). Comment: The authors note that this was not unexpected since benzene uptake is only a fraction of the total external dose. Urinary benzene and t,t–MA for the total population showed a moderate correlation (R^2 = 0.37). Urinary benzene levels for laboratory workers (0.79 ug/l) was significantly greater (P = 0.018) than for traffic wardens (0.22 ug/l). A similar significant (P = 0.001) difference was also present for t,t–MA (126 versus 46 ug/l, respectively). There was no apparent difference in airborne exposure between the laboratory workers (4.1 ppb; environmental monitoring) and the traffic wardens (5.1 ppb; personal exposure). – 499/957 –
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