N retention in urbanizing headwater catchments
Urbanization can potentially alter watershed nitrogen (N) retention via combined changes in N loading, water runoff, and N processing potential. We examined N export and retention for two headwater catchments (∼4${\rm km}^{2}$) of contrasting land use (16% vs. 79% urban) in the Plum Island Ecosystem...
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Veröffentlicht in: | Ecosystems (New York) 2005-12, Vol.8 (8), p.871-884 |
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description | Urbanization can potentially alter watershed nitrogen (N) retention via combined changes in N loading, water runoff, and N processing potential. We examined N export and retention for two headwater catchments (∼4${\rm km}^{2}$) of contrasting land use (16% vs. 79% urban) in the Plum Island Ecosystem (PIE-LTER) watershed, MA. The study period included a dry year (2001-2002 water year) and a wet year (2002-2003 water year). We generalized results by comparing dissolved inorganic nitrogen (DIN) concentrations from 16 additional headwater catchments (0.6-4.2${\rm km}^{2}$) across a range of urbanization (6-90%). Water runoff was 25-40% higher in the urban compared to the forested catchment, corresponding with an increased proportion of impervious surfaces (25% vs. 8%). Estimated N loading was 45% higher and N flux 6.5 times higher in the urban than in the forested catchment. N retention (1 - measured stream export / estimated loading) was 65-85% in the urban site and 93-97% in the forested site, with lower retention rates during the wetter year. The mechanisms by which N retention stays relatively high in urban systems are poorly known. We show that N retention is related to the amount of impervious surface in a catchment because of associated changes in N loading (maximized at moderate levels of imperviousness), runoff (which continues to increase with imperviousness), and biological processes that retain N. Continued declines in N retention due to urbanization have important negative implications for downstream aquatic systems including the coastal zone. |
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We examined N export and retention for two headwater catchments (∼4${\rm km}^{2}$) of contrasting land use (16% vs. 79% urban) in the Plum Island Ecosystem (PIE-LTER) watershed, MA. The study period included a dry year (2001-2002 water year) and a wet year (2002-2003 water year). We generalized results by comparing dissolved inorganic nitrogen (DIN) concentrations from 16 additional headwater catchments (0.6-4.2${\rm km}^{2}$) across a range of urbanization (6-90%). Water runoff was 25-40% higher in the urban compared to the forested catchment, corresponding with an increased proportion of impervious surfaces (25% vs. 8%). Estimated N loading was 45% higher and N flux 6.5 times higher in the urban than in the forested catchment. N retention (1 - measured stream export / estimated loading) was 65-85% in the urban site and 93-97% in the forested site, with lower retention rates during the wetter year. The mechanisms by which N retention stays relatively high in urban systems are poorly known. We show that N retention is related to the amount of impervious surface in a catchment because of associated changes in N loading (maximized at moderate levels of imperviousness), runoff (which continues to increase with imperviousness), and biological processes that retain N. Continued declines in N retention due to urbanization have important negative implications for downstream aquatic systems including the coastal zone.</description><identifier>ISSN: 1432-9840</identifier><identifier>EISSN: 1435-0629</identifier><identifier>DOI: 10.1007/s10021-005-0178-3</identifier><language>eng</language><publisher>New York, NY: Springer Science+Business Media</publisher><subject>Animal and plant ecology ; Animal, plant and microbial ecology ; Aquatic environment ; Biological and medical sciences ; Catchments ; Coastal zone ; Forest watersheds ; Forested watersheds ; Fundamental and applied biological sciences. 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We examined N export and retention for two headwater catchments (∼4${\rm km}^{2}$) of contrasting land use (16% vs. 79% urban) in the Plum Island Ecosystem (PIE-LTER) watershed, MA. The study period included a dry year (2001-2002 water year) and a wet year (2002-2003 water year). We generalized results by comparing dissolved inorganic nitrogen (DIN) concentrations from 16 additional headwater catchments (0.6-4.2${\rm km}^{2}$) across a range of urbanization (6-90%). Water runoff was 25-40% higher in the urban compared to the forested catchment, corresponding with an increased proportion of impervious surfaces (25% vs. 8%). Estimated N loading was 45% higher and N flux 6.5 times higher in the urban than in the forested catchment. N retention (1 - measured stream export / estimated loading) was 65-85% in the urban site and 93-97% in the forested site, with lower retention rates during the wetter year. The mechanisms by which N retention stays relatively high in urban systems are poorly known. We show that N retention is related to the amount of impervious surface in a catchment because of associated changes in N loading (maximized at moderate levels of imperviousness), runoff (which continues to increase with imperviousness), and biological processes that retain N. Continued declines in N retention due to urbanization have important negative implications for downstream aquatic systems including the coastal zone.</description><subject>Animal and plant ecology</subject><subject>Animal, plant and microbial ecology</subject><subject>Aquatic environment</subject><subject>Biological and medical sciences</subject><subject>Catchments</subject><subject>Coastal zone</subject><subject>Forest watersheds</subject><subject>Forested watersheds</subject><subject>Fundamental and applied biological sciences. 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Psychology</topic><topic>General aspects</topic><topic>Groundwater</topic><topic>Headwaters</topic><topic>Land use</topic><topic>Nitrogen</topic><topic>pollution load</topic><topic>Prunus</topic><topic>Retention</topic><topic>Runoff</topic><topic>Stormwater</topic><topic>Surface runoff</topic><topic>Synecology</topic><topic>Urban areas</topic><topic>Urban runoff</topic><topic>Urbanization</topic><topic>Watersheds</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Wollheim, W.M</creatorcontrib><creatorcontrib>Pellerin, B.A</creatorcontrib><creatorcontrib>Vorosmarty, C.J</creatorcontrib><creatorcontrib>Hopkinson, C.S</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Ecology Abstracts</collection><collection>Environment Abstracts</collection><collection>ProQuest Central (purchase pre-March 2016)</collection><collection>Science Database (Alumni Edition)</collection><collection>ProQuest Central (Alumni) (purchase pre-March 2016)</collection><collection>Research Library (Alumni Edition)</collection><collection>ProQuest Central (Alumni Edition)</collection><collection>ProQuest One Sustainability</collection><collection>ProQuest Central UK/Ireland</collection><collection>Agricultural & Environmental Science Collection</collection><collection>ProQuest Central Essentials</collection><collection>ProQuest Central</collection><collection>Natural Science Collection</collection><collection>Earth, Atmospheric & Aquatic Science Collection</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central Korea</collection><collection>ProQuest Central Student</collection><collection>Research Library Prep</collection><collection>SciTech Premium Collection</collection><collection>Research Library</collection><collection>Science Database</collection><collection>Research Library (Corporate)</collection><collection>Environmental Science Database</collection><collection>Earth, Atmospheric & Aquatic Science Database</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>Environmental Science Collection</collection><collection>ProQuest Central Basic</collection><collection>Environment Abstracts</collection><collection>Pollution Abstracts</collection><collection>Sustainability Science Abstracts</collection><collection>Water Resources Abstracts</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><jtitle>Ecosystems (New York)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Wollheim, W.M</au><au>Pellerin, B.A</au><au>Vorosmarty, C.J</au><au>Hopkinson, C.S</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>N retention in urbanizing headwater catchments</atitle><jtitle>Ecosystems (New York)</jtitle><date>2005-12-01</date><risdate>2005</risdate><volume>8</volume><issue>8</issue><spage>871</spage><epage>884</epage><pages>871-884</pages><issn>1432-9840</issn><eissn>1435-0629</eissn><abstract>Urbanization can potentially alter watershed nitrogen (N) retention via combined changes in N loading, water runoff, and N processing potential. We examined N export and retention for two headwater catchments (∼4${\rm km}^{2}$) of contrasting land use (16% vs. 79% urban) in the Plum Island Ecosystem (PIE-LTER) watershed, MA. The study period included a dry year (2001-2002 water year) and a wet year (2002-2003 water year). We generalized results by comparing dissolved inorganic nitrogen (DIN) concentrations from 16 additional headwater catchments (0.6-4.2${\rm km}^{2}$) across a range of urbanization (6-90%). Water runoff was 25-40% higher in the urban compared to the forested catchment, corresponding with an increased proportion of impervious surfaces (25% vs. 8%). Estimated N loading was 45% higher and N flux 6.5 times higher in the urban than in the forested catchment. N retention (1 - measured stream export / estimated loading) was 65-85% in the urban site and 93-97% in the forested site, with lower retention rates during the wetter year. The mechanisms by which N retention stays relatively high in urban systems are poorly known. We show that N retention is related to the amount of impervious surface in a catchment because of associated changes in N loading (maximized at moderate levels of imperviousness), runoff (which continues to increase with imperviousness), and biological processes that retain N. Continued declines in N retention due to urbanization have important negative implications for downstream aquatic systems including the coastal zone.</abstract><cop>New York, NY</cop><pub>Springer Science+Business Media</pub><doi>10.1007/s10021-005-0178-3</doi><tpages>14</tpages></addata></record> |
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subjects | Animal and plant ecology Animal, plant and microbial ecology Aquatic environment Biological and medical sciences Catchments Coastal zone Forest watersheds Forested watersheds Fundamental and applied biological sciences. Psychology General aspects Groundwater Headwaters Land use Nitrogen pollution load Prunus Retention Runoff Stormwater Surface runoff Synecology Urban areas Urban runoff Urbanization Watersheds |
title | N retention in urbanizing headwater catchments |
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