Inhibitor Report for: Sulprofos

Sulprofos, disulfoton, azinphos-methyl, methamidophos, trichlorfon, and tebupirimphos were screened for neurotoxic potential, in accordance with U.S. EPA (FIFRA) requirements. Each organophosphate was administered through the diet for 13 weeks to separate groups of Fischer 344 rats at four dose levels, including a vehicle control. For each study, 12 rats/sex/dietary level were tested using a functional observational battery (FOB), automated measures of activity (figure-8 maze), and detailed clinical observations, with half of the animals perfused at term for microscopic examination of neural and muscle tissues. Separate groups of satellite animals (6/sex/dietary level) were used to measure the effect of each treatment on plasma, erythrocyte (RBC), and brain cholinesterase (ChE) activity. The results show that measures of ChE activity were consistently the most sensitive indices of exposure and assisted in the interpretation of findings. All treatment-related neurobehavioral findings were ascribed to cholinergic toxicity, occurring only at dietary levels that produced more than 20% inhibition of plasma, RBC, and brain ChE activity. Neurobehavioral tests provided no evidence of additional cumulative toxicity after 8 weeks of treatment. The FOB and motor activity findings did not alter the conclusions and generally did not reduce the neurobehavioral no-observed-effect level (NOEL) for any of the six compounds, relative to the results from detailed clinical observations as conducted in these studies. The one exception occurred with tebupirimphos, where the NOEL for motor activity was one dose level lower than the NOEL for the FOB and clinical observations. These results support the value of detailed clinical observations to screen for the neurotoxic potential of organophosphates and a general standard of more than 20% inhibition of brain ChE activity for cholinergic neurotoxicity.

Significant increase of sister-chromatid exchanges (SCE) in V79 cells treated with 2 organophosphorus pesticides (OPP), fenthion and oxydemeton-methyl, was observed. The other 7 compounds (6 OPP and 1 defoliant) namely, amaze, azinphos-methyl, bolstar, DEF-defoliant, fensulfothion, monitor and nemacur caused no increase of SCE frequencies at the doses tested. All the compounds except fensulfothion and oxydemeton-methyl induced cell-cycle delay in varying degrees. Cell-cycle delay caused by an OPP was found to be dose-dependent. Based on these data as well as others reported, it would appear that OPP which induce no SCE increase and no or slight cell-cycle delay could be considered as good candidates to substitute the pesticides that have been found to be harmful to the environment.