Investigations were made to find out the cause of inactivation of some organophosphorous insecticides after mixed with polluted water. Fourth instar larvae of the mosquito, Culex pipiens pallens, DK strain, were used for test of the effectiveness of the insecticides. Results of experiments to expose the larvae at 28℃ for 24 hours to buffer solutions with various pH values have shown that 50% levels were 11.8 and 2.4 and no deaths were seen between pH 3 and pH 10. Further tests were made on the residual effects of insecticides mixed in buffer solutions with varying pH values from 3 to 10. At the observations made after 16 days, no considerable reduction in the effectiveness was seen for dieldrin, lindane, p-p' DDT, fenthion (Baytex), fenitrothion (Sumithion), parathion and methyl-parathion, while remarkable reductions in effectiveness were seen at all pH levels for ronnel, at alcaline solutions over 7 for dichlorovos (DDVP) and malathion, and at acid solutions below 4 for diazinon. The loss of activity of some insecticides when mixed with polluted water discussed below is therefore considered not due to the direct effect of hydrogen ion concentrations. Experiments were carried out to see the effects of bacterial growth in media containing insecticides. The insecticidal activity of parathion, methylparathion and fenitothion was found to be remerkably reduced or almost completely lost within 4 days when these were mixed into polluted water prepared with a animal food from natural environments or into unsterilized bacterial culture media such as 1.0% peptone solution. The media containing pure culture of Bacillus subtilis was found to cause the same inactivating effects on the insecticides, while the insecticidal activity was kept unchanged when these were mixed after the media had been sterilized. Both fenthion and diazinon were stable under the same condition and no reduction in the effectiveness was seen for a period of 16 days. The above inactivation of some insecticides in polluted waters was found to be due to bacterial decomposition of substances non-toxic or less toxic to the insects. For example, Bacillus subtilis was demonstrated to decompose parathion to amino-parathion, and fenitrothion to amino-fenitrothon or to methylparathion and further to aminomethylparathion. LC 50 levels against C. p. pallens larvae of amino-parathion, amino-methylparathion and amino-fenitrothion were estimated to be 5.37, 60.3 and 115 ppm., respectively. The chemical structures of amino-parathion, amino-methylparathion and amino-fenitrothion are O, O-diethyl O-para-aminophenyl phosphorothioate, and O, O-dimethyl O-(3-methyl-4-aminophenyl) phosphorothioate, respectively.
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