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Journal of Environmental Science and Health, Part B
Pesticides, Food Contaminants, and Agricultural Wastes
Volume 41, 2006 - Issue 4
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Original Articles

Experimental Variability in Characterization of Cyfluthrin Sorption to Soil

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Pages 323-331 | Received 22 Sep 2005, Published online: 06 Feb 2007
 

To assess the risk of a pesticide to leach to groundwater or to run off to surface water after application, it is necessary to characterize the sorption of the pesticide to soil. For pyrethroids, their hydrophobicity, strong sorption to various materials, and low solubility make it difficult to accurately characterize sorption processes. The objective of this research was to evaluate the variability in cyfluthrin ((RS)-α -cyano-4-fluoro-3-phenoxybenzyl (1RS,3RS;1RS,3SR)-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylate) sorption to soil as affected by experiment conditions. To minimize cyfluthrin sorption on the walls of glass, silanized-glass, stainless steel, and PTFE centrifuge tubes, cyfluthrin solution was added to aqueous soil slurries or directly to soil, after which it was equilibrated with aqueous solution. Depending on the soil, variation in sorption coefficients, K oc, obtained using different experimental methodologies with one soil can be comparable to the variation in K oc values obtained for soils with different physical and chemical properties using one method. K oc values for cyfluthrin ranged from 56,000 to 300,000 L kg−1. Sorption methodology needs to be evaluated before sorption coefficients are used in predictive transport models.

Notes

1Sn:Sl = solution:soil (g:g).

2Cy = 14C-cyfluthrin concentration (% solvent): 4 μ g L−1 (0.4%), 0.7 and 1 μ g L−1 (0.1%).

3KS = Kansas clay loam sediment, CA = Fresno sandy loam, G = glass vessel, GD = dichloromethylsilane treated glass vessel, GS = Surfasil treated glass vessel, PFT = polytetrafluoroethylene bottle.

1KS = Kansas clay loam sediment, CA = Fresno sandy loam, ND = Gardena clay loam, FL = Vero Beach sand.

2Cyfluthrin applied to either the 0.01 M CaCl2 solution or directly to the soil prior to addition of the CaCl2 solution. Solution:soil (g:g) = 200:1. Cyfluthrin concentration = 1 μ g L−1 (0.1% solvent) or 0.2 μ g g−1.

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