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Carbaryl, Carbofuran, and Methomyl - National Marine Fisheries ...

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decreased to 0.2 mg/L when covered by 18 inches of water. Concentrations of carbaryl were<br />

variable among sites. For example, at one of the sampling sites carbaryl was not detected until<br />

the water was 7 inches deep. A peak concentration of 8 mg/L was detected at this site when the<br />

water depth was 11 inches. This sample station was located 300 ft from a treated area.<br />

Maximum carbaryl concentrations detected at other sites were 17.4, 7.8, <strong>and</strong> 4 mg/L with<br />

samples collected at depths of 6, 4, <strong>and</strong> 13 inches from the bottom. <strong>Carbaryl</strong>’s primary toxic<br />

degradate, 1-naphthol, was detected at concentrations as high as 1.4 mg/L. Average<br />

concentrations of carbaryl detected in tide pools <strong>and</strong> small streams ranged from 3.6 to 11.2 mg/L.<br />

The 11.2 mg/L detection was associated with application of 5 lbs carbaryl/acre. An average<br />

concentration of 7.8 mg/L in tide pools <strong>and</strong> streams was associated with an application rate of 4<br />

lbs carbaryl/acre, approximately half the maximum rate allowed. Similarly, a more recent study<br />

found a peak of 820 μg/L in the water column 50 ft from the application site following a typical<br />

treatment application at the maximum rate of 8 lbs/acre (n=3) (Weisskopf <strong>and</strong> Felsot 1998).<br />

Several studies demonstrate that carbaryl dissipates fairly rapidly from over the treatment site<br />

due to degradation, metabolism, dilution, <strong>and</strong> off-site transport (Hurlburt 1986; Creekman <strong>and</strong><br />

Hurlburt 1987; Tufts 1989; Tufts 1990; Weisskopf <strong>and</strong> Felsot 1998). In 2006 <strong>and</strong> 2007, samples<br />

collected at the mouth of channels adjacent to treated oyster beds in Willapa Bay had maximum<br />

concentrations of 29.1 µg/L after 6 h (high tide), 38 µg/L after 12 h (low tide), <strong>and</strong> 21.1 µg/L<br />

after 24 h (low tide) (Major, Grue et al. 2005).<br />

The NPDES permit for Willapa Bay <strong>and</strong> Grays Harbor requires annual monitoring of water<br />

column concentrations in treated areas. It specifies an acute effluent limit of 3 µg/L <strong>and</strong> a<br />

chronic limit of 0.06 µg/L. However, those data are of highly questionable value because the<br />

monitoring plan specifies that monitoring is suspended for the first 48 h following application to<br />

assess the acute effluent, <strong>and</strong> further suspends monitoring for 30 days from the last application to<br />

assess the chronic limit. We expect that most of the carbaryl will be degraded <strong>and</strong> transported to<br />

other locations by the time carbaryl monitoring is initiated.<br />

<strong>Carbaryl</strong> sprayed on mud flats can be transported substantial distances at concentrations that may<br />

have ecological impacts. Researchers found that close to 100% of Dungeness crabs were killed<br />

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