Toxicology and fate of Pestanal® and commercial propetamphos formulations in river and estuarine sediment

• Published in: The Science of the total environment 2006-08, Vol.366 (2), p.826-836
• Main Authors: García-Ortega, Susana, Holliman, Peter J., Jones, Davey L.
• Format: Article
• Language: English
• Subjects: Adsorption; Agronomy. Soil science and plant productions; Animal, plant and microbial ecology; Applied ecology; Applied sciences; Bacteria - drug effects; Bacteria - metabolism; Bioavailability; Biodegradation, Environmental; Biological and medical sciences; Biological and physicochemical properties of pollutants. Interaction in the soil; Earth sciences; Earth, ocean, space; Ecotoxicology, biological effects of pollution; Engineering and environment geology. Geothermics; Exact sciences and technology; Fate; Fresh water environment; Freshwater; Fundamental and applied biological sciences. Psychology; Geologic Sediments - microbiology; Insecticides - analysis; Insecticides - metabolism; Insecticides - toxicity; Marine; Organothiophosphorus Compounds - analysis; Organothiophosphorus Compounds - metabolism; Organothiophosphorus Compounds - toxicity; Pesticide formulation; Pollution; Pollution, environment geology; Rivers; Safrotin; Seawater; Sheep dip; Soil and sediments pollution; Soil and water pollution; Soil science; Toxicology; Water Pollutants, Chemical - analysis; Water Pollutants, Chemical - metabolism; Water Pollutants, Chemical - toxicity
• ISSN: 0048-9697; 1879-1026
• DOI: 10.1016/j.scitotenv.2005.08.008

To quantify the impact of organophosphate pesticides on aquatic ecosystems requires a mechanistic understanding of their behaviour in a range of environmental matrices. The objective of this study was to compare the sorption/desorption, biodegradation and toxic effects of the Pestanal® grade and commercial formulation (Ectomort Centenary) of the organophosphate insecticide propetamphos in river and estuarine sediments. For both formulations, the sorption of propetamphos onto sediment was initially very rapid followed by a slower sorption phase. Similarly, the initial rate of desorption was rapid, followed by a much slower rate. In both sorption and desorption experiments, the level of sorbed propetamphos was considerably higher for the commercial formulation of propetamphos ( K d = 7–11) than for the Pestanal® grade ( K d = 4–10). The rate of propetamphos biodegradation was sediment dependent but was most rapid where microbial activity and nutrients were the highest and sorption was the lowest. Propetamphos was more rapidly degraded in sediments under aerobic ( t 1 / 2 = 15 d) compared to anaerobic conditions ( t 1 / 2 = 19 d). However, no significant difference in the biodegradation rates of the Pestanal® grade and commercial formulations of propetamphos were observed. The toxic effect of propetamphos on sediment microbial communities was significantly greater for the commercial formulation than for the Pestanal® grade of propetamphos based on EC 50 (21 versus 236 μg g − 1) and EC 10 values (0.3 versus 54 μg g − 1). In conclusion, our results highlight the importance of using commercial pesticide formulations when carrying out ecotoxicological testing.