Influence of infrastructure on water quality and greenhouse gas dynamics in urban streams

Streams and rivers are significant sources of nitrous oxide (N<sub>2</sub>O), carbon dioxide (CO<sub>2</sub>), and methane (CH<sub>4</sub>) globally, and watershed management can alter greenhouse gas (GHG) emissions from streams. We hypothesized that urban infr...

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Main Authors: R. M. Smith, S. S. Kaushal, J. J. Beaulieu, M. J. Pennino, C. Welty
Format: Article
Language:English
Published: Copernicus Publications 2017-06-01
Series:Biogeosciences
Online Access:http://www.biogeosciences.net/14/2831/2017/bg-14-2831-2017.pdf
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author R. M. Smith
R. M. Smith
S. S. Kaushal
J. J. Beaulieu
M. J. Pennino
M. J. Pennino
C. Welty
spellingShingle R. M. Smith
R. M. Smith
S. S. Kaushal
J. J. Beaulieu
M. J. Pennino
M. J. Pennino
C. Welty
Influence of infrastructure on water quality and greenhouse gas dynamics in urban streams
Biogeosciences
author_facet R. M. Smith
R. M. Smith
S. S. Kaushal
J. J. Beaulieu
M. J. Pennino
M. J. Pennino
C. Welty
author_sort R. M. Smith
title Influence of infrastructure on water quality and greenhouse gas dynamics in urban streams
title_short Influence of infrastructure on water quality and greenhouse gas dynamics in urban streams
title_full Influence of infrastructure on water quality and greenhouse gas dynamics in urban streams
title_fullStr Influence of infrastructure on water quality and greenhouse gas dynamics in urban streams
title_full_unstemmed Influence of infrastructure on water quality and greenhouse gas dynamics in urban streams
title_sort influence of infrastructure on water quality and greenhouse gas dynamics in urban streams
publisher Copernicus Publications
series Biogeosciences
issn 1726-4170
1726-4189
publishDate 2017-06-01
description Streams and rivers are significant sources of nitrous oxide (N<sub>2</sub>O), carbon dioxide (CO<sub>2</sub>), and methane (CH<sub>4</sub>) globally, and watershed management can alter greenhouse gas (GHG) emissions from streams. We hypothesized that urban infrastructure significantly alters downstream water quality and contributes to variability in GHG saturation and emissions. We measured gas saturation and estimated emission rates in headwaters of two urban stream networks (Red Run and Dead Run) of the Baltimore Ecosystem Study Long-Term Ecological Research project. We identified four combinations of stormwater and sanitary infrastructure present in these watersheds, including: (1) stream burial, (2) inline stormwater wetlands, (3) riparian/floodplain preservation, and (4) septic systems. We selected two first-order catchments in each of these categories and measured GHG concentrations, emissions, and dissolved inorganic and organic carbon (DIC and DOC) and nutrient concentrations biweekly for 1 year. From a water quality perspective, the DOC : NO<sub>3</sub><sup>−</sup> ratio of streamwater was significantly different across infrastructure categories. Multiple linear regressions including DOC : NO<sub>3</sub><sup>−</sup> and other variables (dissolved oxygen, DO; total dissolved nitrogen, TDN; and temperature) explained much of the statistical variation in nitrous oxide (N<sub>2</sub>O, <i>r</i><sup>2</sup> =  0.78), carbon dioxide (CO<sub>2</sub>, <i>r</i><sup>2</sup> =  0.78), and methane (CH<sub>4</sub>, <i>r</i><sup>2</sup> =  0.50) saturation in stream water. We measured N<sub>2</sub>O saturation ratios, which were among the highest reported in the literature for streams, ranging from 1.1 to 47 across all sites and dates. N<sub>2</sub>O saturation ratios were highest in streams draining watersheds with septic systems and strongly correlated with TDN. The CO<sub>2</sub> saturation ratio was highly correlated with the N<sub>2</sub>O saturation ratio across all sites and dates, and the CO<sub>2</sub> saturation ratio ranged from 1.1 to 73. CH<sub>4</sub> was always supersaturated, with saturation ratios ranging from 3.0 to 2157. Longitudinal surveys extending form headwaters to third-order outlets of Red Run and Dead Run took place in spring and fall. Linear regressions of these data yielded significant negative relationships between each gas with increasing watershed size as well as consistent relationships between solutes (TDN or DOC, and DOC : TDN ratio) and gas saturation. Despite a decline in gas saturation between the headwaters and stream outlet, streams remained saturated with GHGs throughout the drainage network, suggesting that urban streams are continuous sources of CO<sub>2</sub>, CH<sub>4</sub>, and N<sub>2</sub>O. Our results suggest that infrastructure decisions can have significant effects on downstream water quality and greenhouse gases, and watershed management strategies may need to consider coupled impacts on urban water and air quality.
url http://www.biogeosciences.net/14/2831/2017/bg-14-2831-2017.pdf
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spelling doaj-bc304160a87140f5804f684e05f8aea22020-11-24T22:34:17ZengCopernicus PublicationsBiogeosciences1726-41701726-41892017-06-01142831284910.5194/bg-14-2831-2017Influence of infrastructure on water quality and greenhouse gas dynamics in urban streamsR. M. Smith0R. M. Smith1S. S. Kaushal2J. J. Beaulieu3M. J. Pennino4M. J. Pennino5C. Welty6Department of Biology, University of Utah, Salt Lake City, UT 84112, USADepartment of Geology, Earth System Science Interdisciplinary Center, University of Maryland, College Park, MD 20742, USADepartment of Geology, Earth System Science Interdisciplinary Center, University of Maryland, College Park, MD 20742, USAUS Environmental Protection Agency, Office of Research and Development, National Risk Management Research Laboratory, Cincinnati, OH 45220, USAUS Environmental Protection Agency National Health and Environmental Effects Research Lab, Corvallis, OR 97333, USADepartment of Chemical, Biochemical, and Environmental Engineering, Center for Urban Environmental Research and Education, University of Maryland Baltimore County, Baltimore, MD 21250, USADepartment of Chemical, Biochemical, and Environmental Engineering, Center for Urban Environmental Research and Education, University of Maryland Baltimore County, Baltimore, MD 21250, USAStreams and rivers are significant sources of nitrous oxide (N<sub>2</sub>O), carbon dioxide (CO<sub>2</sub>), and methane (CH<sub>4</sub>) globally, and watershed management can alter greenhouse gas (GHG) emissions from streams. We hypothesized that urban infrastructure significantly alters downstream water quality and contributes to variability in GHG saturation and emissions. We measured gas saturation and estimated emission rates in headwaters of two urban stream networks (Red Run and Dead Run) of the Baltimore Ecosystem Study Long-Term Ecological Research project. We identified four combinations of stormwater and sanitary infrastructure present in these watersheds, including: (1) stream burial, (2) inline stormwater wetlands, (3) riparian/floodplain preservation, and (4) septic systems. We selected two first-order catchments in each of these categories and measured GHG concentrations, emissions, and dissolved inorganic and organic carbon (DIC and DOC) and nutrient concentrations biweekly for 1 year. From a water quality perspective, the DOC : NO<sub>3</sub><sup>−</sup> ratio of streamwater was significantly different across infrastructure categories. Multiple linear regressions including DOC : NO<sub>3</sub><sup>−</sup> and other variables (dissolved oxygen, DO; total dissolved nitrogen, TDN; and temperature) explained much of the statistical variation in nitrous oxide (N<sub>2</sub>O, <i>r</i><sup>2</sup> =  0.78), carbon dioxide (CO<sub>2</sub>, <i>r</i><sup>2</sup> =  0.78), and methane (CH<sub>4</sub>, <i>r</i><sup>2</sup> =  0.50) saturation in stream water. We measured N<sub>2</sub>O saturation ratios, which were among the highest reported in the literature for streams, ranging from 1.1 to 47 across all sites and dates. N<sub>2</sub>O saturation ratios were highest in streams draining watersheds with septic systems and strongly correlated with TDN. The CO<sub>2</sub> saturation ratio was highly correlated with the N<sub>2</sub>O saturation ratio across all sites and dates, and the CO<sub>2</sub> saturation ratio ranged from 1.1 to 73. CH<sub>4</sub> was always supersaturated, with saturation ratios ranging from 3.0 to 2157. Longitudinal surveys extending form headwaters to third-order outlets of Red Run and Dead Run took place in spring and fall. Linear regressions of these data yielded significant negative relationships between each gas with increasing watershed size as well as consistent relationships between solutes (TDN or DOC, and DOC : TDN ratio) and gas saturation. Despite a decline in gas saturation between the headwaters and stream outlet, streams remained saturated with GHGs throughout the drainage network, suggesting that urban streams are continuous sources of CO<sub>2</sub>, CH<sub>4</sub>, and N<sub>2</sub>O. Our results suggest that infrastructure decisions can have significant effects on downstream water quality and greenhouse gases, and watershed management strategies may need to consider coupled impacts on urban water and air quality.http://www.biogeosciences.net/14/2831/2017/bg-14-2831-2017.pdf