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Published online 8 September 2005
Published in J Environ Qual 34:1828-1842 (2005)
DOI: 10.2134/jeq2004.0338
© 2005 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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Nitrate Movement in Shallow Ground Water from Swine-Lagoon-Effluent Spray Fields Managed under Current Application Regulations

Daniel W. Israela,*, William J. Showersb, Matthew Fountainb and John Fountainb

a USDA-ARS and Department of Soil Science, North Carolina State University, Box 7619, Raleigh, NC 27695
b J. Fountain, Department of Marine, Earth and Atmospheric Sciences, Box 8208, North Carolina State University, Raleigh, NC 27695



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Fig. 1. Map of the study site.

 


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Fig. 2. Water table contours (meters above sea level) for Waste Application Field (WAF) 1 with horizontal gradient vectors at two different dates to show seasonal consistency. Black symbols indicate location of well nests and dashed line represents the stream. The contour interval is 0.5 m. The length of vectors represents size of the hydraulic gradient. Transect 1, {blacksquare}; Transect 2, •; Transect 3, {blacktriangleup}.

 


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Fig. 3. Water table contours (meters above sea level) for Waste Application Field (WAF) 2 with horizontal gradient vectors at two different dates to show seasonal consistency. Black symbols indicate location of well nests and dashed line represents the stream. The contour interval is 0.2 m. The length of vectors represents size of the hydraulic gradient. Transect 1, {blacksquare}; Transect 2, •; Transect 3, {blacktriangleup}.

 


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Fig. 4. Chloride concentrations in ground water from shallow and deep wells averaged over the 36-mo sampling period.

 


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Fig. 5. Nitrate N and Cl concentrations and [Cl] to [nitrate N] ratios in shallow ground water moving from waste application fields (WAFs) to stream. Values are means for all samples taken from the shallow wells at each nest over a 36-mo period.

 


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Fig. 6. Dissolved organic carbon (DOC) concentrations in shallow ground water moving from waste application fields (WAFs) to the stream. Values are means for all samples taken from the shallow wells of each nest over a 36-mo period.

 


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Fig. 7. {delta}15N natural abundance ratios for nitrate N in shallow ground water moving from waste application fields (WAFs) to the stream. The horizontal dashed lines represent the upper end of the range of {delta}15N natural abundance ratios reported for fertilizer N sources.

 


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Fig. 8. Relationships between {delta}18O of nitrate and {delta}15N of nitrate in shallow ground water moving from waste application fields (WAFs) to the stream. Solid line represents the predicted {delta}18O-nitrate vs. {delta}15N-nitrate relationship when nitrate N is denitrified in the system. Dashed lines represent predicted {delta}18O-nitrate vs. {delta}15N-nitrate relationships when fertilizer N and animal waste N are nitrified.

 


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Fig. 9. Comparison {delta}15N natural abundance ratios for nitrate N in water from the stream and from wells in the waste application fields (WAFs) over a 24-mo period.

 





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