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Pesticide residues in food — 2006: Toxicological ... - ipcs inchem

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321<br />

found <strong>in</strong> the faeces over the 6 days after dos<strong>in</strong>g. Thus more than 99% of the excreted radiolabel was<br />

<strong>in</strong> the ur<strong>in</strong>e (Gerbig et al., 1985).<br />

Humans<br />

A GLP-compliant study of pharmacok<strong>in</strong>etics was performed <strong>in</strong> three segments.<br />

The first segment was a pilot study <strong>in</strong> which one male volunteer was given the sodium salt<br />

of racemic haloxyfop acid as a s<strong>in</strong>gle oral dose at 0.2 mg/kg bw. Samples of blood and ur<strong>in</strong>e were<br />

collected at frequent <strong>in</strong>tervals up to 528 h after dos<strong>in</strong>g. Faeceal samples were also collected, but were<br />

not analysed.<br />

The second segment was performed <strong>in</strong> three male volunteers who were given the sodium salt of<br />

racemic haloxyfop as a s<strong>in</strong>gle oral dose at 0.2 mg/kg bw. Samples of blood and ur<strong>in</strong>e were collected<br />

at frequent <strong>in</strong>tervals up to 20 days after dos<strong>in</strong>g.<br />

The third segment was performed <strong>in</strong> four male volunteers who were given racemic haloxyfop<br />

methyl ester as a s<strong>in</strong>gle dermal dose at 0.8 mg/kg bw. Samples of blood and ur<strong>in</strong>e were collected at<br />

frequent <strong>in</strong>tervals up to 20 days after dos<strong>in</strong>g.<br />

Samples of blood and ur<strong>in</strong>e were subjected to acid hydrolysis to convert all forms of haloxyfop<br />

<strong>in</strong>to the acid form. Then the samples were analysed by GC with an electron-capture detector.<br />

No adverse effects on health were reported <strong>in</strong> any segment of the study.<br />

Orally adm<strong>in</strong>istered racemic haloxyfop sodium salt was rapidly absorbed with a half-life of<br />

0.9 h. Peak plasma concentrations (C max<br />

) of haloxyfop of 1.4–2.2 μg/g were detected at 4–12 h after<br />

dos<strong>in</strong>g. The removal from plasma <strong>in</strong>to ur<strong>in</strong>e had a half-life of 6.3 days. Based on the amount of<br />

haloxyfop detected <strong>in</strong> ur<strong>in</strong>e, the volunteer <strong>in</strong> the pilot study absorbed and excreted 100% of the oral<br />

dose <strong>in</strong>to the ur<strong>in</strong>e and the three volunteers <strong>in</strong> the second segment excreted 65–74% of the oral dose<br />

<strong>in</strong>to the ur<strong>in</strong>e.<br />

Racemic haloxyfop methyl ester was absorbed across sk<strong>in</strong> slowly with a half-life of 36.5 h and<br />

peak plasma concentrations of haloxyfop of 0.1–0.2 μg/g were detected at 3 days after dos<strong>in</strong>g. The<br />

haloxyfop was removed from plasma <strong>in</strong>to the ur<strong>in</strong>e with a half-life of 5.8 days. An average of 2.4%<br />

of the haloxyfop applied to the sk<strong>in</strong> was recovered <strong>in</strong> the ur<strong>in</strong>e.<br />

The Meet<strong>in</strong>g concluded that oral doses of haloxyfop methyl ester are rapidly and extensively<br />

absorbed. In contrast, dermal uptake of haloxyfop sodium is limited and slow. Ur<strong>in</strong>e was the pr<strong>in</strong>cipal<br />

route of excretion (65–100% of the excreted radiolabel) (Nolan et al., 1985).<br />

A study <strong>in</strong> human volunteers was performed with Verdict Herbicide (a water-emulsifiable<br />

concentrate conta<strong>in</strong><strong>in</strong>g 25.7% haloxyfop-R methyl ester as its active <strong>in</strong>gredient). Detectable levels<br />

(limit of detection, LOD, and tissue not stated) were identified <strong>in</strong> only three out of eight volunteers<br />

after field application accord<strong>in</strong>g to label <strong>in</strong>structions: dilut<strong>in</strong>g 5 US quarts (2.4 l) of the Verdict<br />

concentrate (conta<strong>in</strong><strong>in</strong>g 2.5 lbs [1.1 kg] of haloxyfop-R methyl ester) with 100 US gallons (378.5 l)<br />

of water and spray<strong>in</strong>g 400 US gallons (1514 l) of diluted herbicide onto 20 acres of cropland us<strong>in</strong>g an<br />

open cab self-propelled or tractor-drawn boom spray. The sk<strong>in</strong> exposure was assessed from patches<br />

placed under the cloth<strong>in</strong>g of the applicators. Inhalation exposure was estimated from air sampl<strong>in</strong>g.<br />

All of the ur<strong>in</strong>e passed <strong>in</strong> the 2 days after spray<strong>in</strong>g was collected for biomonitor<strong>in</strong>g analysis. Average<br />

sk<strong>in</strong> exposure dur<strong>in</strong>g mix<strong>in</strong>g was estimated to be 959 μg per lb (2114 μg/kg) of active <strong>in</strong>gredient<br />

handled and dur<strong>in</strong>g spray<strong>in</strong>g it was 30 μg per lb (66 mg/kg) of active <strong>in</strong>gredient. The average<br />

<strong>in</strong>haled dose of active <strong>in</strong>gredient dur<strong>in</strong>g mix<strong>in</strong>g was 9.1 μg/m 3 and dur<strong>in</strong>g spray<strong>in</strong>g it was 2.1 μg/m 3 .<br />

The average absorbed dose of haloxyfop was 0.31 μg/kg bw, based on biomonitor<strong>in</strong>g by ur<strong>in</strong>ary<br />

excretion. Detectable absorbed doses of haloxyfop were found <strong>in</strong> only three of the eight applicators<br />

with estimated absorbed doses rang<strong>in</strong>g from < 0.04 to 1.4 μg/kg bw. No adverse health effects were<br />

reported <strong>in</strong> any of the applicators (Scortich<strong>in</strong>i et al., 1987; Nolan et al., 1991)<br />

HALOXYFOP X-X JMPR <strong>2006</strong>

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