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Published online 9 August 2005
Published in J Environ Qual 34:1620-1631 (2005)
DOI: 10.2134/jeq2004.0462
© 2005 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
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Corn Residue Level and Manure Application Timing Effects on Phosphorus Losses in Runoff

Joseph D. Grandea, K. G. Karthikeyana,*, Paul S. Millera and J. Mark Powellb

a Biological Systems Engineering Department, 460 Henry Mall, University of Wisconsin, Madison, WI 53706
b USDA-ARS, Dairy Forage Research Center, Madison, WI 53706



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Fig. 1. Arrangement of treatment plots showing details of microplot location.

 


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Fig. 2. Effect of crop residue cover (%) on dissolved reactive phosphorus (DRP) concentration in runoff for three manure treatments. Data points are an average of four replicates from each of the four seasons. Residue cover ranges for the three harvesting schemes (G, grain; SH, high-cut silage; SL, low-cut silage) are highlighted. For clarity, confidence intervals are not plotted.

 


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Fig. 3. Effect of crop residue cover (%) on dissolved reactive phosphorus (DRP) load for three manure treatments. Data points are an average of four replicates from each of the four seasons. Residue cover ranges for the three harvesting schemes (G, grain; SH, high-cut silage; SL, low-cut silage) are highlighted. For clarity, confidence intervals are not plotted.

 


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Fig. 4. Influence of time since manure application on runoff volume and its impact on dissolved reactive phosphorus (DRP) load. Note that a change in runoff does not affect the DRP load due to the dependence on DRP concentration (see text for details). Data points are an average of four replicates. Trend lines correspond to all residue levels (G, grain; SH, high-cut silage; SL, low-cut silage) for Years I (2002) and II (2003). For clarity, confidence intervals are not plotted.

 


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Fig. 5. Effect of crop residue cover (%) on total phosphorus (TP) load for three manure treatments. Data points are an average of four replicates from each of the four seasons. Residue cover ranges for the three harvesting schemes (G, grain; SH, high-cut silage; SL, low-cut silage) are highlighted. For clarity, confidence intervals are not plotted.

 


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Fig. 6. Fraction of total phosphorus in the dissolved phase for spring and fall runoff (DRP, dissolved reactive phosphorus; TP, total phosphorus). Mean and standard deviation values correspond to three or four replicates (G, grain; SH, high-cut silage; SL, low-cut silage; N, no manure; F, fall manure; S, spring manure).

 


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Fig. 7. Phosphorus partitioning, on a mass basis, among the four particle size classes (from the top: 0–2, 2–10, 10–50, and 50–500 µm) for nine treatments (G, grain; SH, high-cut silage; SL, low-cut silage; N, no manure; F, fall manure; S, spring manure). Each bar represents a composite distribution of 9 to 15 replicates, based on the number of available samples, averaged over the four seasons.

 


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Fig. 8. Phosphorus enrichment ratios of eroded sediments from spring and fall rainfall experiments. Mean and standard deviation values of one to eight replicates represent combined data from Years I (2002) and II (2003). Bars with the same letter are not significantly different at the 0.05 probability level (G, grain; SH, high-cut silage; SL, low-cut silage; N, no manure; F, fall manure; S, spring manure).

 





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