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Charles R. Kratzer
Journal of the American Water Resources Association, vol. 35, no. 2,
p. 375-395, April 1999
Abstract:
Most of the application of the organophosphate insecticide diazinon
in the San Joaquin River Basin occurs in winter to control wood boring
insects in dormant almond orchards. A federal-state collaborative study
found that diazinon accounted for most of the observed toxicity of San
Joaquin River water in February 1993. Previous studies focused mainly on
west-side inputs to the San Joaquin River. In this 1994 study, the three
major east-side tributaries to the San Joaquin River - the Merced, Tuolumne,
and Stanislaus Rivers - and a downstream site on the San Joaquin River
were sampled throughout the hydrographs of a late January and an early
February storm. In both storms, the Tuolumne River had the highest concentrations
of diazinon and transported the largest load of the three tributaries.
The Stanislaus River was a small source in both storms. On the basis of
previous storm sampling and estimated traveltimes, ephemeral west-side
creeks probably were the main diazinon source early in the storms, whereas
the Tuolumne and Merced Rivers and east-side drainages directly to the
San Joaquin River were the main sources later. Although 74 percent of diazinon
transport in the San Joaquin River during 19911993 occurred in January
and February, transport during each of the two 1994 storms was only 0.05
percent of the amount applied during preceding dry periods. Nevertheless,
some of the diazinon concentrations in the San Joaquin River during the
January storm exceeded 0.35 micrograms per liter, a concentration shown
to be acutely toxic to water fleas. On the basis of this study and previous
studies diazinon concentrations and streamflow are highly variable during
January and February storms, and frequent sampling is requeired to evaluate
transport in the San Joaquin River Basin.
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