Published online 9 January 2007
Published in J Environ Qual 36:194-207 (2007)
DOI: 10.2134/jeq2006.0022
© 2007 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
Substrate Organic Matter to Improve Nitrate Removal in Surface-Flow Constructed Wetlands
Michael R. Burchell, IIa,*,
R. Wayne Skaggsb,
Charles R. Leec,
Steven Broomed,
George M. Chescheire and
Jason Osbornef
a Dep. of Biological and Agric. Engineering, North Carolina State Univ., Box 7625, Raleigh, NC 27695-7625
b Dep. of Biological and Agric. Engineering, North Carolina State Univ., Box 7625, Raleigh, NC 27695-7625
c RSMT, 3919 Fisher Ferry Rd., Vicksburg, MS 39180
d Dep. of Soil Science, North Carolina State Univ., Box 7619, Raleigh, NC 27695-7619
e Dep. of Biological and Agric. Engineering, North Carolina State Univ., Box 7625, Raleigh, NC 27695-7625
f Dep. of Statistics, North Carolina State Univ., Box 8203, Raleigh, NC 27695-8203

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Fig. 3. Batch 1 (12 Feb. through 6 Mar. 2002) average NO3N concentrations from the (a) site soil-based wetlands and (b) dredged material-based wetlands. Different letters indicate significant differences in NO3N treatment at the P = 0.05 level.
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Fig. 4. Batch 2 (722 May 2002) average NO3N concentrations from the (a) site soil-based wetlands and (b) dredged material-based wetlands. Different letters indicate significant differences in NO3N treatment at the P = 0.05 level.
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Fig. 5. Batch 3 (1126 June 2002) average NO3N concentrations from the (a) site soil-based wetlands and (b) dredged material-based wetlands. Different letters indicate significant differences in NO3N treatment at the P = 0.05 level.
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Fig. 6. Batch 4 (224 July 2002) average NO3N concentrations from the (a) site soil-based wetlands and (b) dredged material-based wetlands. Different letters indicate significant differences in NO3N treatment at the P = 0.05 level.
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Fig. 7. Average days required for the (a) site soil-based wetlands and (b) dredged material-based wetlands to remove 90% of the initial NO3N concentrations in Batch studies 1 through 4. Means noted in the legend exclude Batch 1.
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Fig. 8. Above-ground Schoenoplectus tabernaemontani (a.k.a. Scirpus validus) biomass harvested from the (a) site soil-based wetlands and (b) dredged material-based wetlands. Error bars indicate one standard deviation. Different letters indicate significant differences in production within that year at the P = 0.05 level.
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Copyright © 2007 by the American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America.