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The Impact of Pesticides - Academy Publish

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Paraoxon is then either metabolized by an A-esterase into p-NP and DEP, or it bindsto proteins such as AChE (less than 20%) (Hayes, 1982; Jokanovic, 2001). <strong>The</strong>metabolites p-NP and APs, i.e. DETP and DEP, are eliminated in urine and faeces.<strong>The</strong> model and its parameter values is also based on available data on the kinetics <strong>of</strong>parathion and its metabolites in volunteers (Hartwell et al., 1964; Hayes et al., 1964;Maibach et al., 1971; Feldmann and Maibach, 1974; Morgan et al., 1977). <strong>The</strong>model consists <strong>of</strong> specific inputs to describe amounts <strong>of</strong> parathion bioavailable atthe skin surface, GI tract or respiratory tract; a body compartment to represent tissueburdens <strong>of</strong> parathion and paraoxon that rapidly reach and maintain a fixed ratio withblood burden; a storage compartment to characterize storage tissue burdens <strong>of</strong>parathion and paraoxon that are slowly returned to blood; specific metabolitecompartments for p-NP or AP metabolites (the sum <strong>of</strong> DETP and DEP) in blood andin tissues in dynamic equilibrium with blood; retention compartments which delaysexcretion <strong>of</strong> p-NP or APs in urine; urinary and faecal compartments to representseparately cumulative excretion <strong>of</strong> total p-NP or APs in urine and faeces,respectively.Simulations were then performed to propose BRVs for p-NP and APs in urine usingan 8-h dermal scenario to a total dose corresponding to an available repeatedexposureNOEL dose <strong>of</strong> 4.8 mg/day (i.e., 58 µg/day/kg bw). <strong>The</strong> NOEL wasdetermined from the volunteer studies <strong>of</strong> Edson et al., (1964) and Rider et al. (1969)based on the inhibition <strong>of</strong> plasma-ChE or RBC-AChE. BRVs for p-NP and APs <strong>of</strong> 6and 2 nmol/kg bw, respectively, were derived in 12-h urine collections and 24 and15 nmol/kg bw, respectively, in 24-h urine samples. <strong>The</strong>se values are expressed ascumulative amounts in urine over given time periods following the onset <strong>of</strong> anexposure episode.<strong>The</strong> suggested BRV value for p-NP may be considered protective on the basis <strong>of</strong>results obtained by Hayes et al. (1964) in volunteers exposed to parathion andshowing no significant inhibition <strong>of</strong> RBC-AChE (0%) and plasma-ChE (6%)activities at p-NP value <strong>of</strong> 15.9 µmol in 24-h urine collections (i.e. 24 nmol/kg bwassuming a body weight <strong>of</strong> 70 kg). <strong>The</strong> current applicability <strong>of</strong> these proposedBRVs to practical biomonitoring situations is difficult due to limits <strong>of</strong> the usage <strong>of</strong>parathion in the USA since 1991 and increased parathion handling andpostapplication restrictions (EPA, 1999a).CarbarylCarbaryl (1-naphthyl methylcarbamate, CAS 63-25-2) is a contact insecticide <strong>of</strong> thecarbamate family, which inhibits ChE activity in humans. Most studies in exposedworkers measured ChE activity and the ACGIH recommends a RBC-AChE activity<strong>of</strong> 70% <strong>of</strong> the individual’s baseline as a BEI ® (ACGIH, 2011) while no biologicalreference value based on urinary biomarkers were proposed.<strong>The</strong> main urinary carbaryl metabolite in humans is 1-naphthol (over 85%) while 4-(hydroxy)-1-naphthyl N-,ethyl carbamate (free or glucurono-conjugate), 1-naphthylglucuronideand 1-naphthyl-sulfate are minor urinary metabolites (Knaak et al.,1965; Kozbelt, 1968; Chin et al., 1974; Feldmann and Maibach, 1974). 1-Naphtholis rapidly excreted in urine mostly within 24-h after absorption and mainly asglucurono- and sulfo-conjugates.<strong>Academy</strong><strong>Publish</strong>.org - <strong>The</strong> <strong>Impact</strong> <strong>of</strong> <strong>Pesticides</strong>114

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