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Published online 5 July 2005
Published in J Environ Qual 34:1354-1362 (2005)
DOI: 10.2134/jeq2004.0226
© 2005 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
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Fertilizer, Tillage, and Dairy Manure Contributions to Nitrate and Herbicide Leaching

C. S. Stoddarda, J. H. Groveb,*, M. S. Coyneb and W. O. Thomb

a University of California Cooperative Extension Service-Merced County, 2145 Wardrobe Avenue, Merced, CA 95340-6496
b Department of Plant and Soil Sciences, N-122 Agricultural Science-North, University of Kentucky, Lexington, KY 40546-0091



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Fig. 1. Flow-weighted leachate NO3–N, by seasonal period, as affected by spring manuring and fertilizer N applications, averaged across the two tillage systems. The horizontal line at 10 mg NO3–N L–1 is the USEPA drinking water standard.

 


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Fig. 2. Flow-weighted leachate NO3–N, by seasonal period, as affected by the timing of manure application to no-tillage soil. The horizontal line at 10 mg NO3–N L–1 is the USEPA drinking water standard.

 


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Fig. 3. Relationship between fall (after harvest) soil profile (90 cm) nitrate to overwinter (November–April) flow-weighted leachate NO3–N concentration. Dashed lines represent 95% confidence limits. The horizontal line at 10 mg NO3–N L–1 is the USEPA drinking water standard.

 


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Fig. 4. Event average leachate atrazine and alachlor concentrations. Horizontal lines at 2 and 3 µg herbicide L–1 are the alachlor and atrazine maximum contaminant levels (MCLs), respectively.

 





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