1995
DOI: 10.2307/1352640
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Inputs, Transformations, and Transport of Nitrogen and Phosphorus in Chesapeake Bay and Selected Tributaries

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Cited by 525 publications
(359 citation statements)
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“…1). The watershed drains to a 137-km 2 subestuary of Chesapeake Bay (Boynton et al 1995;Hagy et al 2000). The northwestern 28% of the watershed is in the Piedmont physiographic province and the remainder is in the Coastal Plain (Langland et al 1995).…”
Section: Watershed Datamentioning
confidence: 99%
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“…1). The watershed drains to a 137-km 2 subestuary of Chesapeake Bay (Boynton et al 1995;Hagy et al 2000). The northwestern 28% of the watershed is in the Piedmont physiographic province and the remainder is in the Coastal Plain (Langland et al 1995).…”
Section: Watershed Datamentioning
confidence: 99%
“…During the first, relatively wet year of our study, PS supplied 5% of the water, 22% of the N, and 7% of the P delivered to the estuary . In the second, drier year, PS were more important, supplying 14% of the water, 46% of the N, and 34% of the P. PS were formerly the largest sources of N and P, but improved treatment methods have reduced nutrient concentrations in wastewater discharges and NPS discharges are now dominant (Boynton et al 1995;Sprague et al 2000;D'Elia et al 2003). However, the volumes of discharge from the largest treatment plants in the watershed are still increasing (Sprague et al 2000) and will continue to do so as the watershed's population increases (D'Elia et al 2003).…”
Section: Nutrient Sources and Effects Of Watershed Changesmentioning
confidence: 99%
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“…While field-based studies [Burns, 1998;Peterson et al, 2001;Duff et al, 2008;Mulholland et al, 2008Mulholland et al, , 2009Tank et al, 2008;Hall et al, 2009;Mulholland and Webster, 2010] and modeling approaches [Jaworski et al, 1992;Boynton et al, 1995;Alexander et al, 2000Alexander et al, , 2009Seitzinger et al, 2002;Boyer et al, 2006;Runkel, 2007;Ator and Denver, 2012] have provided much needed information on reach and watershed-scale nitrate dynamics, the limited spatial extent and/or low temporal resolution of discrete data collection continues to be a challenge for quantifying loads and interpreting drivers of change in watersheds. Recent studies have demonstrated that the collection and interpretation of high-frequency nitrate data collected using water quality sensors can be used to better quantify nitrate loads to sensitive stream and coastal environments [Ferrant et al, 2013;Bieroza et al, 2014;Pellerin et al, 2014], and provide insights into temporal nitrate dynamics that would otherwise be difficult to obtain using traditional field-based mass balance, solute injection, and/or isotopic tracer studies [Pellerin et al, 2009[Pellerin et al, , 2012Heffernan and Cohen, 2010;Sandford et al, 2013;Carey et al, 2014;Hensley et al, 2014Hensley et al, , 2015Outram et al, 2014;Crawford et al, 2015].…”
Section: Introductionmentioning
confidence: 99%
“…The high biomass and diversity attained by such tropical vegetation patches contrasts with the coastal landscape, dominated by the mangrove and deciduous forest communities. The amount of organic matter in shallow coastal ecosystems is a controlling factor of the microbial reduction of nitrate, or denitrification, and further loss to the atmosphere or transfer to other metabolic pathways within the system (Boynton et al, 1995). Thus, the overall low nitrate concentrations observed across the lagoon in rainfalls may …”
mentioning
confidence: 99%