University of Alaska, Institute of Water Resources
Abstract
Completion Report
OWRT Agreement No. 14-34-0001-6002
Project No. A-057-ALASThis is the final completion report for a two-year project which
began 1 November 1975. The original completion date was extended to 30
September 1977 to allow collection of samples and data through the
summer of 1977.
Malathion is a thiophosphate insecticide, 0,0-dimethly-S-(l,2dicarbethoxyethyl)
phosphorodithioate:
It is less toxic than DDT and decomposes over a much shorter period of
time. With the suspension of DDT in pest control programs in 1965,
use of malathion has been increasingly widespread in Alaska's interior.
In spite of its low toxicity to animals, malathion is poisonous at
some level. Lethal doses for domestic sheep and cattle are 150 mg/kg
and 200 mg/kg. of body weight, respectively. The fatal dose of malathion
for a 70 kg man has been estimated to be 60 g, with some clinical exceptions
(McKee and Wolfe, 1963; Hayes, 1964). Dietary levels (ppm) producing
minimal or no effect after continuous feeding for 90 days to 2 years to
rats and dogs have been reported as 100-1000 and 100, respectively
(Lehman, 1965). On the other hand, malathion has been identified by gas
chromatography in extracts of water associated with several fish kills
(Garrison, Keith, and Alford, 1972).
In a study of malathion persistence in the soil near Fairbanks,
Alaska, during the summer of 1967, half of the sampling sites showed the
presence of malathion and its oxidation product, malaoxon, prior to
aerial spraying (Holty, 1970). Since there had been no ground spraying
since the summer of 1966, this would indicate that malathion was not
degrading in the environment as fast as anticipated. This is important
since it is then possible for the spring runoff to carry significant
quantities of the pesticide and its degradation products into streams
and rivers in the area. Retention of the malathion appears to depend on
the amount of rainfall, and the summer of 1966 had been very dry.
During the wetter summer of 1967, the post-spray soil samples showed a
rapid drop in the level of malathion except at sampling sites in "mucky"
soils which also increased noticeably in moisture as the amount of
rainfall accumulated (Figure 1).
Very little has been known about the aqueous photodecomposition of
malathion and nothing was known of its vapor phase stability under
atmospheric conditions and exposure to sunlight prior to this study.The work upon which this completion report is based was supported by
funds provided by the U. S. Department of the Interior, Office of Water
Research and Technology as authorized under the Water Resources Research
Act of 1964, Public Law 88-379, as amended