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toxicological profile for malathion - Agency for Toxic Substances and ...

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MALATHION 195<br />

6. POTENTIAL FOR HUMAN EXPOSURE<br />

Carolina, was detected (detection limit of 0.5 ng/L) in the subsurface water at a maximum mean<br />

concentration of 32 ng/L, with a range in individual samples of below the limit of detection to 47 ng/L.<br />

In the surface microlayer (top #1 mm) samples, <strong>malathion</strong> was detected at a maximum mean<br />

concentration of 32 ng/L, with a range in individual samples of below the limit of detection to 57 ng/L.<br />

Monitoring studies have been conducted to determine the presence of numerous pesticides, including<br />

<strong>malathion</strong>, in groundwater in the United States. In a review of pesticides in groundwater monitoring data<br />

in the literature, Ritter (1990) reported that <strong>malathion</strong> occurrence in groundwater from normal agricultural<br />

use was reported in the literature <strong>for</strong> only one state. In a database of pesticides in groundwater that was<br />

compiled by EPA from data available <strong>for</strong> 1971–1991, results indicated that <strong>malathion</strong> was detected in a<br />

total of 12 wells in three states (Cali<strong>for</strong>nia, Mississippi, <strong>and</strong> Virginia) at concentrations ranging from<br />

0.007 to 6.17 µg/L; monitoring data were reported <strong>for</strong> a total of 3,252 wells (EPA 1992). Forty-one l<strong>and</strong>use<br />

studies were conducted in 1993–1995 at a total of 1,034 agricultural <strong>and</strong> urban sites representing<br />

20 major hydrologic basins throughout the United States to assess the occurrence of 46 pesticides,<br />

including <strong>malathion</strong>, in shallow groundwater <strong>for</strong> the National Water-Quality Assessment (NAWQA)<br />

program; 31 of the studies were in agricultural areas <strong>and</strong> 10 were in urban areas (Kolpin et al. 1998).<br />

Malathion was detected (detection limit of 0.005 µg/L) at 0.2% of all sites, with detection frequencies of<br />

0.4% <strong>for</strong> sites where corn <strong>and</strong> alfalfa growth accounted <strong>for</strong> >20% of the crops grown there, <strong>and</strong> 1.7% <strong>for</strong><br />

sites where orchards or vineyards accounted <strong>for</strong> >50% of the crops (Kolpin et al. 1998).<br />

6.4.3 Sediment <strong>and</strong> Soil<br />

To estimate soil concentrations following an aerial application of <strong>malathion</strong>, at a target rate of<br />

23.8 mg/m 2 , to urban/residential areas (1,500 km 2 ) of southern Cali<strong>for</strong>nia between August 1989 <strong>and</strong> July<br />

1990 <strong>for</strong> the eradication of medflies, mass deposition data <strong>for</strong> <strong>malathion</strong> <strong>and</strong> its primary oxidation<br />

product, malaoxon, were obtained from the CDFA Environmental Monitoring Branch (Bradman et al.<br />

1994). Based on measured values of mass deposition, daily <strong>malathion</strong> <strong>and</strong> malaoxon residue levels in soil<br />

were estimated <strong>for</strong> a single application using two sample mixing depths. Based on a mixing depth of<br />

1 cm, soil concentrations of the parent <strong>and</strong> its degradate were estimated as 1.4 <strong>and</strong> 0.01 µg/g,<br />

respectively; based on a mixing depth of 0.1 cm, the corresponding estimated concentrations in soil were<br />

14.1 <strong>and</strong> 0.10 µg/g (Bradman et al. 1994).<br />

In a study of 49 r<strong>and</strong>omly chosen agrichemical facilities located throughout Illinois, <strong>malathion</strong> was<br />

detected in soil samples at 6 of the 18 sites that h<strong>and</strong>led the compound (Krapac et al. 1995). Malathion

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