Nutrient exports from watersheds with varying septic system densities in the North Carolina Piedmont.
Autor: | Iverson G; Coastal Resources Management Program, East Carolina University, 379 Flanagan, Greenville, NC 27858, USA. Electronic address: iversong06@students.ecu.edu., Humphrey CP Jr; Environmental Health Sciences Program, East Carolina University, 3408 Carol Belk Building, Greenville, NC 27858, USA; Coastal Water Resources Center, Institute for Coastal Science and Policy, East Carolina University, 354 Science and Technology Building, Greenville, NC 27858, USA., O'Driscoll MA; Department of Geological Sciences, East Carolina University, 204 Graham Building, Greenville, NC 27858, USA; Earth & Ocean Sciences, Nicholas School of the Environment, Duke University, A318 Levine Science Research Center, Durham, NC 27708, USA., Sanderford C; Environmental Health Sciences Program, East Carolina University, 3408 Carol Belk Building, Greenville, NC 27858, USA., Jernigan J; Environmental Health Sciences Program, East Carolina University, 3408 Carol Belk Building, Greenville, NC 27858, USA., Serozi B; Environmental Health Sciences Program, East Carolina University, 3408 Carol Belk Building, Greenville, NC 27858, USA. |
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Jazyk: | angličtina |
Zdroj: | Journal of environmental management [J Environ Manage] 2018 Apr 01; Vol. 211, pp. 206-217. Date of Electronic Publication: 2018 Feb 04. |
DOI: | 10.1016/j.jenvman.2018.01.063 |
Abstrakt: | Septic systems (SSs) have been shown to be a significant source of nitrogen and phosphorus to nutrient-sensitive coastal surface and groundwaters. However, few published studies have quantified the effects of SSs on nutrient inputs to water supply watersheds in the Piedmont region of the USA. This region consists of rolling hills at the surface underlain by clayey soils. There are nearly 1 million SSs in this region, which accounts for approximately 50% of all SSs in North Carolina. The goal of this study was to determine if significant differences in nutrient concentrations and exports exist between Piedmont watersheds with different densities of SSs. Water quality was assessed in watersheds with SSs (n = 11) and a sewer and a forested watershed, which were designated as controls. Stream flow and environmental readings were recorded and water samples were collected from the watersheds from January 2015-December 2016. Additional samples were collected from sand filter watersheds in April 2015-March 2016 to compare to septic and control watersheds. Samples were analyzed for total dissolved nitrogen (TDN) and orthophosphate (PO (Copyright © 2018 Elsevier Ltd. All rights reserved.) |
Databáze: | MEDLINE |
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