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IARC MONOGRAPHS ON THE EVALUATION OF CARCINOGENIC ...

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these naphthols as metabolites. The frequency of detection was 86% for 1-naphthol and<br />

81% for 2-naphthol. The mean concentrations were 15 and 5.4 μg/g creatinine, respectively.<br />

Concentrations of 1-naphthol ranged up to 1400 μg/g creatinine.<br />

Yang et al. (1999) examined the relationship between certain enzyme polymorphisms<br />

and naphthalene metabolism in 119 men who were not occupationally<br />

exposed to polycyclic aromatic hydrocarbons. A polymorphism in exon 7 of the CYP1A1<br />

gene was not related to urinary naphthol excretion. Smokers with the c1/c2 or c2/c2<br />

genotype in CYP2E1 excreted higher concentrations of 2-naphthol in the urine than<br />

smokers with the c1/c1 genotype. Smokers deficient in glutathione S-transferase M1<br />

(GSTM1) showed higher urinary concentrations (without correction for creatinine) of<br />

both 1-naphthol and 2-naphthol.<br />

Nan et al. (2001) examined the effects of occupation, lifestyle and genetic polymorphisms<br />

of CYP1A1, CYP2E1 and the glutathione S-transferases GSTM1 and GSTT1<br />

on the concentrations of 2-naphthol in the urine of 90 coke-oven workers in comparison<br />

with 128 university students. The urinary excretion of 2-naphthol was higher in the cokeoven<br />

workers (7.69 μmol/mol creatinine) than in the students (2.09 μmol/mol creatinine).<br />

In the control group, the excretion was higher in smokers (3.94 μmol/mol creatinine)<br />

than in nonsmokers (1.55 μmol/mol creatinine). Urinary 2-naphthol concentrations<br />

were higher in coke-oven workers with the c1/c2 or c2/c2 genotypes than in those with<br />

the more common c1/c1 genotype of CYP2E1. Urinary 2-naphthol concentrations were<br />

also higher in the urine of GSTM1-null workers than in GSTM1-positive workers.<br />

4.1.2 Experimental systems<br />

(a) Absorption, distribution and excretion<br />

NAPHTHALENE 393<br />

Early studies indicated that in rats naphthalene is well absorbed from the gastrointestinal<br />

tract (Chang, 1943). When naphthalene was fed to white male rats (weight,<br />

about 300 g) [strain unspecified] at a concentration of 1% (w/w) in the diet, none was<br />

detected in the faeces. Similarly, when it was administered as a single dose by stomach<br />

tube (0.1 g), it was not measurable in the faeces.<br />

Eisele (1985) examined the distribution of [ 14 C]naphthalene in laying pullets, swine<br />

and dairy cattle following oral administration. In pullets given a dose of 0.44 mg, the<br />

major site of deposition was the kidney followed by fat, lung and liver. Following acute<br />

administration of 2.46 mg in swine, the major site of deposition was fat, where the level<br />

was up to 10 times higher than that in liver. After chronic administration (0.112 mg per<br />

day for 31 days), the lung, liver and heart were major sites of accumulation. In cows,<br />

chronic exposure (5.115 mg per day for 31 days) led to deposition primarily in the liver.<br />

When [ 14 C]naphthalene was applied dermally (3.3 μg/cm 2 ; total dose, 43 μg) to male<br />

Sprague-Dawley rats, the plasma half-life for absorption was 2.1 h and that for elimination<br />

was 12.8 h. The highest concentration of radioactivity 48 h after dosing was found<br />

in the skin followed by ileum, duodenum and kidney. Seventy per cent of the<br />

radioactivity was found in the urine in the first 48 h, with 3.7% appearing in the faeces

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