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Pesticide residues in food — 2007: Toxicological ... - ipcs inchem

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404<br />

Explanation<br />

Profenofos is the International Organization for Standardization (ISO) approved name for<br />

(RS)-O-4-bromo-2-chlorophenyl O-ethyl S-propyl phosphorothioate (International Union of Pure<br />

and Applied Chemistry, IUPAC). The Chemical Abstracts Service (CAS) chemical name for profenofos<br />

is O-(4-bromo-2-chlorophenyl) O-ethyl S-propyl phosphorothioate (CAS No. 41198-08-7).<br />

It is a broad-spectrum organophosphorus <strong>in</strong>secticide that is used to control <strong>in</strong>sect pests <strong>in</strong> cotton,<br />

maize, sugar beet, soya bean, potato, vegetables and other crops. Its mode of action is by <strong>in</strong>hibition of<br />

acetylchol<strong>in</strong>esterase activity. Profenofos is a racemic mixture of the two optical isomers at the chiral<br />

phosphorus atom. The S (−) isomer is a markedly more potent <strong>in</strong>hibitor of acetylchol<strong>in</strong>esterase <strong>in</strong><br />

vitro than the R (+) isomer.<br />

Profenofos was previously evaluated by JMPR <strong>in</strong> 1990 (Annex 5, reference 171) and an acceptable<br />

daily <strong>in</strong>take (ADI) of 0–0.01 mg/kg bw per day was established. The ADI was based on the<br />

no-observed-adverse-effect level (NOAEL) of 20 ppm, equal to 1.0 mg/kg bw per day, the highest<br />

dose tested, <strong>in</strong> a three-generation study of reproduction <strong>in</strong> rats.<br />

Profenofos was re-evaluated by the present meet<strong>in</strong>g with<strong>in</strong> the periodic review programme of<br />

the Codex Committee on <strong>Pesticide</strong> Residues (CCPR). All pivotal studies with profenofos were certified<br />

as comply<strong>in</strong>g with good laboratory practice (GLP).<br />

Evaluation for acceptable daily <strong>in</strong>take<br />

1. Biochemical aspects<br />

1.1 Absorption, distribution and excretion<br />

RAI rats (four males and three females) received a s<strong>in</strong>gle oral dose (gavage) of r<strong>in</strong>g-labelled<br />

[ 14 C]profenofos (specific activity, 9.79 μCi/mg (362.23 kBq/mg) at approximately 4.8 mg/kg bw<br />

<strong>in</strong> ethanol : polyethylene glycol 200 : water (25 : 25 : 50). Ur<strong>in</strong>e and faeces were collected for 6<br />

days after dos<strong>in</strong>g and selected tissues were removed at necropsy. Essentially all the adm<strong>in</strong>istered<br />

radioactivity was elim<strong>in</strong>ated <strong>in</strong> the ur<strong>in</strong>e (males, 81.8%; and females, 96.4%) and faeces (males,<br />

15.7%; and females, 2.5%) with<strong>in</strong> 6 days. Most of the ur<strong>in</strong>ary and faecal excretion occurred with<strong>in</strong><br />

the first 24 h after dos<strong>in</strong>g. The elim<strong>in</strong>ation half-life for excretion was less than 8 h for both sexes.<br />

Only m<strong>in</strong>or amounts of 14 CO 2<br />

were elim<strong>in</strong>ated <strong>in</strong> expired air (males, 0.08%; and females, 0.07% ).<br />

When the rats were killed 6 days after dos<strong>in</strong>g, detectable amounts of radioactivity were present<br />

only <strong>in</strong> the liver (males, 0.013 μg equivalent/g; and females, 0.023 μg equivalent/g) and kidneys<br />

(males, 0.007 μg equivalent/g; and females, 0.008 μg equivalent/g). The concentration of radioactivity<br />

<strong>in</strong> blood, fat, muscle, testis, ovary and bra<strong>in</strong> was below the limit of quantification (for blood) or<br />

d etection (I fflaender & Mücke, 1974).<br />

Figure 1. Chemical structure of profenofos<br />

PROFENOFOS 403–443 JMPR <strong>2007</strong>

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