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Published online 27 October 2006
Published in J Environ Qual 35:2132-2145 (2006)
DOI: 10.2134/jeq2006.0157
© 2006 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
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Effects of Watershed-Scale Land Use Change on Stream Nitrate Concentrations

Keith E. Schillinga,* and Jean Spoonerb

a Iowa Department of Natural Resources, Iowa Geological Survey, 109 Trowbridge Hall, Iowa City, IA 52242-1319
b Soil & Water Environmental Technology Center (SWETC), North Carolina State University, Box 7637, Raleigh, NC 27695-7637


Figure 1
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Fig. 1. Location map including locations of prairie plantings, subbasins, and stream sampling locations.

 

Figure 2
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Fig. 2. Summary of annual prairie plantings by USFWS at the Neal Smith NWR.

 

Figure 3
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Fig. 3. Box plot of total discharge and average monthly baseflow percentage (open squares) by month at WNT2 and SQW2 gauging stations. Box plots illustrate the 25th, 50th, and 75th percentiles; the whiskers indicate the 10th and 90th percentiles; and the circles represent data outliers.

 

Figure 4
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Fig. 4. Time series of nitrate concentrations measured at upstream downstream sites in the Walnut and Squaw creek watersheds.

 

Figure 5
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Fig. 5. Box plot of nitrate concentrations by water year at upstream and downstream sites in the Walnut and Squaw creek watersheds.

 

Figure 6
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Fig. 6. Box plot of nitrate concentrations by water year at subbasin monitoring sites in the Walnut and Squaw creek watersheds.

 

Figure 7
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Fig. 7. Box plot of nitrate concentrations by month at upstream and downstream sites in the Walnut and Squaw creek watersheds.

 

Figure 8
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Fig. 8. Relation of nitrate concentrations at WNT2 to regression covariates.

 

Figure 9
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Fig. 9. Relation of change in nitrate in stream nitrate concentrations (as determined by statistical methods) to change in percentage of land cover in row crops in watersheds and subbasins.

 





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