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Herbicide concentration and dissipation from surface wind-erodible soil

Published online by Cambridge University Press:  20 January 2017

Sharon A. Clay ,
Thomas M. DeSutter  and
David E. Clay
Thomas M. DeSutter
Affiliation:
Plant Science Department, South Dakota State University, Brookings, SD 57007
David E. Clay
Affiliation:
Plant Science Department, South Dakota State University, Brookings, SD 57007
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Abstract

Soil lost through wind erosion may transport herbicides to nontarget areas. Shallow incorporation may reduce herbicide concentrations at the soil surface, thereby reducing loss on wind-erodible sediment (particles and aggregates less than 1 mm in diameter). Atrazine, alachlor, and acetochlor concentrations on and dissipation rates from surface wind-erodible sediment and larger size fractions from two soil types in undisturbed and incorporated (5 cm deep) treatments were compared. The surface 1 cm of soil was removed by vacuum 1, 7, and 21 d after herbicide treatment (DAT). This soil was dry-sieved into six size fractions (four fractions considered wind-erodible and two larger size fractions), and herbicide concentrations were determined on each size fraction. About 50% of the recovered material was classified as wind erodible sediment. Incorporation reduced herbicide concentrations on all size fractions and results were similar between soil types. Wind-erodible sediments from undisturbed and incorporated treatments contained about 65 and 8% of the applied herbicides, respectively, 1 DAT. Herbicide concentrations were similar among size fractions within a treatment 7 and 21 DAT; however, incorporation reduced soil herbicide concentrations from 50 to 80% compared to concentrations on soil from undisturbed areas. Shallow incorporation did not affect weed control ratings measured 30 DAT or herbicide dissipation. However, 50% dissipation rates (DT50) for each herbicide were about 15 d for wind-erodible sediments and ranged from 30 to 55 d for size fractions ≥1.68 mm.

Keywords

AcetochloralachloratrazineHerbicide transportnonpoint source contaminationwind erosion
Type
Research Article
Information
Weed Science , Volume 49 , Issue 3 , June 2001 , pp. 431 - 436
Copyright
Copyright © Weed Science Society of America 

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References

Literature Cited

Ahrens, W. H., ed. 1994. Herbicide Handbook. Champaign, IL: Weed Science Society of America. 352 p.Google Scholar
Bode, L. 1982. Efficiency of herbicide incorporation equipment. Pages 135–136 in Proceedings of the North Central Weed Control Conference.Google Scholar
Chepil, W. S. 1945. Dynamics of wind erosion: I. Nature of movement of soil by wind. Soil Sci. 60:305–320.Google Scholar
Cihacek, L. J., Sweeney, M. D., and Deibert, E. J. 1993. Characterization of wind erosion sediments in the Red River Valley of North Dakota. J. Environ. Qual. 22:305–310.Google Scholar
Clay, S. A., Scholes, K. A., and Clay, D. E. 1994. Fertilizer shank placement impact on atrazine movement in a ridge tillage system. Weed Sci. 42:86–91.Google Scholar
DeSutter, T. M., Clay, S. A., and Clay, D. E. 1998. Atrazine, alachlor, and total inorganic nitrogen concentrations of winter wind-eroded sediment samples. J. Environ. Sci. Health B 33:683–691.CrossRefGoogle ScholarPubMed
Dowell, F. E., Siemens, J. C., and Bode, L. E. 1988. Cultivator speed and sweep spacing effects on herbicide incorporation. Trans. Am. Soc. Agric. Eng. 31:1315–1321.Google Scholar
Ghadiri, H. and Rose, C. W. 1991. Sorbed chemical transport in overland flow: I. A nutrient and pesticide enrichment mechanism. J. Environ. Qual. 20:628–633.Google Scholar
Hagen, L. J. and Lyles, L. 1985. Amount and nutrient content of particles produced by soil aggregate abrasion. Pages 117–129 In Erosion and Soil Productivity. American Society of Agricultural Engineers publication 885.Google Scholar
Khan, S. U. 1982. Bound pesticide residues in soil and plants. Residue Rev. 84:1–25.Google ScholarPubMed
Kohl, R. A., Carlson, C. G., and Wangemann, S. G. 1994. Herbicide leaching potential through road ditches in thin soils over an outwash aquifer. Appl. Eng. Agric. 10:497–503.Google Scholar
Koskinen, W. C. and Clay, S. A. 1997. Factors affecting atrazine fate in north central U.S. soils. Rev. Environ. Contam. Toxicol. 151:117–165.Google Scholar
Li, J., Langford, C. H., and Gamble, D. S. 1996. Atrazine sorption by a mineral soil: effects of soil size fractions and temperature. J. Agric. Food Chem. 44:3680–3684.Google Scholar
Malo, D. D. 1993. Soil Particle Size Analysis Methods. Brookings, SD: South Dakota State University, Plant Science Department Pedology Report 93–5. 16 p.Google Scholar
Novak, J. M., Moorman, T. B., and Karlen, D. L. 1994. Influence of soil aggregate size on atrazine sorption kinetics. J. Agric. Food Chem. 42:1809–1812.Google Scholar
Paul, E. A. and Clark, F. E. 1989. Dynamics of residue decomposition and soil organic matter turnover. Pages 115–130 In Soil Microbiology and Biochemistry. San Diego, CA: Academic Press.Google Scholar
[SAS] Statistical Analysis Systems. 1991. System for Linear Models. 3rd ed. Cary, NC: Statistical Analysis Systems Institute. 329 p.Google Scholar
Schulte, E. E. 1988. Recommended soil organic matter tests. Pages 29–32 In Dahnke, W. C., ed. Recommended Chemical Soil Test Procedures for the North Central Region. NCR Publication 221 (Revised).Google Scholar
[USDA] United States Department of Agriculture. 1994. Summary Report: 1992 National Resources Inventory. Washington, DC: USDA Natural Resources Conservation Service. 54 p.Google Scholar
Wauchope, R. D. and Myers, R. S. 1985. Adsorption-desorption kinetics of atrazine and linuron in freshwater-sediment aqueous slurries. J. Environ. Qual. 14:132–136.Google Scholar
Zobeck, T. M. 1989. Fast-Vac—A vacuum system to rapidly sample loose granular material. Trans. Am. Soc. Agric. Eng. 32:1316–1318.Google Scholar