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Identifying priorities for nutrient mitigation using river concentration–flow relationships: The Thames basin, UK
•Load Apportionment Model applied to multiple sites across the Thames basin, UK.•Phosphorus load dominated by sewage inputs during growing season at most sites.•Nitrogen load dominated by diffuse and groundwater inputs throughout year.•Modelling shows need for further P removal from sewage treatment...
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Published in: | Journal of hydrology (Amsterdam) 2014-09, Vol.517, p.1-12 |
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creator | Bowes, Michael J. Jarvie, Helen P. Naden, Pamela S. Old, Gareth H. Scarlett, Peter M. Roberts, Colin Armstrong, Linda K. Harman, Sarah A. Wickham, Heather D. Collins, Adrian L. |
description | •Load Apportionment Model applied to multiple sites across the Thames basin, UK.•Phosphorus load dominated by sewage inputs during growing season at most sites.•Nitrogen load dominated by diffuse and groundwater inputs throughout year.•Modelling shows need for further P removal from sewage treatment effluents.•Model provides simple and rapid method to identify best mitigation options.
The introduction of tertiary treatment to many of the sewage treatment works (STW) across the Thames basin in southern England has resulted in major reductions in river phosphorus (P) concentrations. Despite this, excessive phytoplankton growth is still a problem in the River Thames and many of its tributaries. There is an urgent need to determine if future resources should focus on P removal from the remaining STW, or on reducing agricultural inputs, to improve ecological status. Nutrient concentration–flow relationships for monitoring sites along the River Thames and 15 of its major tributaries were used to estimate the relative inputs of phosphorus and nitrogen from continuous (sewage point sources) and rain-related (diffuse and within-channel) sources, using the Load Apportionment Model (LAM). The model showed that diffuse sources and remobilisation of within-channel phosphorus contributed the majority of the annual P load at all monitoring sites. However, the majority of rivers in the Thames basin are still dominated by STW P inputs during the ecologically-sensitive spring-autumn growing season. Therefore, further STW improvements would be the most effective way of improving water quality and ecological status along the length of the River Thames, and 12 of the 15 tributaries. The LAM outputs were in agreement with other indicators of sewage input, such as sewered population density, phosphorus speciation and boron concentration. The majority of N inputs were from diffuse sources, and LAM suggests that introducing mitigation measures to reduce inputs from agriculture and groundwater would be most appropriate for all but one monitoring site in this study. The utilisation of nutrient concentration–flow data and LAM provide a simple, rapid and effective screening tool for determining nutrient sources and most effective mitigation options. |
doi_str_mv | 10.1016/j.jhydrol.2014.03.063 |
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The introduction of tertiary treatment to many of the sewage treatment works (STW) across the Thames basin in southern England has resulted in major reductions in river phosphorus (P) concentrations. Despite this, excessive phytoplankton growth is still a problem in the River Thames and many of its tributaries. There is an urgent need to determine if future resources should focus on P removal from the remaining STW, or on reducing agricultural inputs, to improve ecological status. Nutrient concentration–flow relationships for monitoring sites along the River Thames and 15 of its major tributaries were used to estimate the relative inputs of phosphorus and nitrogen from continuous (sewage point sources) and rain-related (diffuse and within-channel) sources, using the Load Apportionment Model (LAM). The model showed that diffuse sources and remobilisation of within-channel phosphorus contributed the majority of the annual P load at all monitoring sites. However, the majority of rivers in the Thames basin are still dominated by STW P inputs during the ecologically-sensitive spring-autumn growing season. Therefore, further STW improvements would be the most effective way of improving water quality and ecological status along the length of the River Thames, and 12 of the 15 tributaries. The LAM outputs were in agreement with other indicators of sewage input, such as sewered population density, phosphorus speciation and boron concentration. The majority of N inputs were from diffuse sources, and LAM suggests that introducing mitigation measures to reduce inputs from agriculture and groundwater would be most appropriate for all but one monitoring site in this study. The utilisation of nutrient concentration–flow data and LAM provide a simple, rapid and effective screening tool for determining nutrient sources and most effective mitigation options.</description><identifier>ISSN: 0022-1694</identifier><identifier>EISSN: 1879-2707</identifier><identifier>DOI: 10.1016/j.jhydrol.2014.03.063</identifier><identifier>CODEN: JHYDA7</identifier><language>eng</language><publisher>Kidlington: Elsevier B.V</publisher><subject>Animal and plant ecology ; Animal, plant and microbial ecology ; Basins ; Biological and medical sciences ; Diffuse source ; Diffusion ; Earth sciences ; Earth, ocean, space ; Ecology ; Engineering and environment geology. Geothermics ; Exact sciences and technology ; Fresh water ecosystems ; Freshwater ; Fundamental and applied biological sciences. Psychology ; Hydrology ; Hydrology. Hydrogeology ; Load Apportionment Model ; Monitoring ; Nitrogen ; Nutrients ; Phosphorus ; Point source ; Pollution, environment geology ; Rivers ; Synecology ; Thames Initiative ; Tributaries</subject><ispartof>Journal of hydrology (Amsterdam), 2014-09, Vol.517, p.1-12</ispartof><rights>2014</rights><rights>2015 INIST-CNRS</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-a508t-f1b89d1f7342a5f5913e8652e6dd5e866608d1565efbbf49a8879139228711a33</citedby><cites>FETCH-LOGICAL-a508t-f1b89d1f7342a5f5913e8652e6dd5e866608d1565efbbf49a8879139228711a33</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27924,27925</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=28689670$$DView record in Pascal Francis$$Hfree_for_read</backlink></links><search><creatorcontrib>Bowes, Michael J.</creatorcontrib><creatorcontrib>Jarvie, Helen P.</creatorcontrib><creatorcontrib>Naden, Pamela S.</creatorcontrib><creatorcontrib>Old, Gareth H.</creatorcontrib><creatorcontrib>Scarlett, Peter M.</creatorcontrib><creatorcontrib>Roberts, Colin</creatorcontrib><creatorcontrib>Armstrong, Linda K.</creatorcontrib><creatorcontrib>Harman, Sarah A.</creatorcontrib><creatorcontrib>Wickham, Heather D.</creatorcontrib><creatorcontrib>Collins, Adrian L.</creatorcontrib><title>Identifying priorities for nutrient mitigation using river concentration–flow relationships: The Thames basin, UK</title><title>Journal of hydrology (Amsterdam)</title><description>•Load Apportionment Model applied to multiple sites across the Thames basin, UK.•Phosphorus load dominated by sewage inputs during growing season at most sites.•Nitrogen load dominated by diffuse and groundwater inputs throughout year.•Modelling shows need for further P removal from sewage treatment effluents.•Model provides simple and rapid method to identify best mitigation options.
The introduction of tertiary treatment to many of the sewage treatment works (STW) across the Thames basin in southern England has resulted in major reductions in river phosphorus (P) concentrations. Despite this, excessive phytoplankton growth is still a problem in the River Thames and many of its tributaries. There is an urgent need to determine if future resources should focus on P removal from the remaining STW, or on reducing agricultural inputs, to improve ecological status. Nutrient concentration–flow relationships for monitoring sites along the River Thames and 15 of its major tributaries were used to estimate the relative inputs of phosphorus and nitrogen from continuous (sewage point sources) and rain-related (diffuse and within-channel) sources, using the Load Apportionment Model (LAM). The model showed that diffuse sources and remobilisation of within-channel phosphorus contributed the majority of the annual P load at all monitoring sites. However, the majority of rivers in the Thames basin are still dominated by STW P inputs during the ecologically-sensitive spring-autumn growing season. Therefore, further STW improvements would be the most effective way of improving water quality and ecological status along the length of the River Thames, and 12 of the 15 tributaries. The LAM outputs were in agreement with other indicators of sewage input, such as sewered population density, phosphorus speciation and boron concentration. The majority of N inputs were from diffuse sources, and LAM suggests that introducing mitigation measures to reduce inputs from agriculture and groundwater would be most appropriate for all but one monitoring site in this study. The utilisation of nutrient concentration–flow data and LAM provide a simple, rapid and effective screening tool for determining nutrient sources and most effective mitigation options.</description><subject>Animal and plant ecology</subject><subject>Animal, plant and microbial ecology</subject><subject>Basins</subject><subject>Biological and medical sciences</subject><subject>Diffuse source</subject><subject>Diffusion</subject><subject>Earth sciences</subject><subject>Earth, ocean, space</subject><subject>Ecology</subject><subject>Engineering and environment geology. Geothermics</subject><subject>Exact sciences and technology</subject><subject>Fresh water ecosystems</subject><subject>Freshwater</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Hydrology</subject><subject>Hydrology. Hydrogeology</subject><subject>Load Apportionment Model</subject><subject>Monitoring</subject><subject>Nitrogen</subject><subject>Nutrients</subject><subject>Phosphorus</subject><subject>Point source</subject><subject>Pollution, environment geology</subject><subject>Rivers</subject><subject>Synecology</subject><subject>Thames Initiative</subject><subject>Tributaries</subject><issn>0022-1694</issn><issn>1879-2707</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2014</creationdate><recordtype>article</recordtype><recordid>eNqNkc9uGyEQxlHVSnXTPkIlLpV66G4ZWFjopaqi_okaqZfkjDA7xFjrxYV1It_6Dn3DPElxbPWaICEG5vfNiPkIeQusBQbq47pdr_ZDTmPLGXQtEy1T4hlZgO5Nw3vWPycLxjhvQJnuJXlVyprVJUS3IOViwGmOYR-nG7rNMeU4Ryw0pEyn3ZxjzdJNfbtxc0wT3ZUDmOMtZurT5Gs6P2Tu__wNY7qjGceHe1nFbflEr1ZYt9vUkktXtR_o9c_X5EVwY8E3p_OMXH_7enX-o7n89f3i_Mtl4yTTcxNgqc0AoRcddzJIAwK1khzVMMgaKcX0AFJJDMtl6IzT9b8gDOe6B3BCnJH3x7rbnH7vsMx2E4vHcXQTpl2xYMAY2WnxBFR1XDBuuH4CynvTS5CmovKI-pxKyRhsnfDG5b0FZg_W2bU9WWcP1lkmbLWu6t6dWrji3Riym3ws_8VcK21Uzyr3-chhneJtxGyLr4Z5HGJGP9shxUc6_QOftrON</recordid><startdate>20140901</startdate><enddate>20140901</enddate><creator>Bowes, Michael J.</creator><creator>Jarvie, Helen P.</creator><creator>Naden, Pamela S.</creator><creator>Old, Gareth H.</creator><creator>Scarlett, Peter M.</creator><creator>Roberts, Colin</creator><creator>Armstrong, Linda K.</creator><creator>Harman, Sarah A.</creator><creator>Wickham, Heather D.</creator><creator>Collins, Adrian L.</creator><general>Elsevier B.V</general><general>Elsevier</general><scope>IQODW</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QH</scope><scope>7ST</scope><scope>7TG</scope><scope>7TV</scope><scope>7UA</scope><scope>C1K</scope><scope>F1W</scope><scope>H96</scope><scope>KL.</scope><scope>L.G</scope><scope>SOI</scope><scope>7SU</scope><scope>8FD</scope><scope>FR3</scope><scope>KR7</scope><scope>H97</scope></search><sort><creationdate>20140901</creationdate><title>Identifying priorities for nutrient mitigation using river concentration–flow relationships: The Thames basin, UK</title><author>Bowes, Michael J. ; Jarvie, Helen P. ; Naden, Pamela S. ; Old, Gareth H. ; Scarlett, Peter M. ; Roberts, Colin ; Armstrong, Linda K. ; Harman, Sarah A. ; Wickham, Heather D. ; Collins, Adrian L.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-a508t-f1b89d1f7342a5f5913e8652e6dd5e866608d1565efbbf49a8879139228711a33</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2014</creationdate><topic>Animal and plant ecology</topic><topic>Animal, plant and microbial ecology</topic><topic>Basins</topic><topic>Biological and medical sciences</topic><topic>Diffuse source</topic><topic>Diffusion</topic><topic>Earth sciences</topic><topic>Earth, ocean, space</topic><topic>Ecology</topic><topic>Engineering and environment geology. 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Hydrogeology</topic><topic>Load Apportionment Model</topic><topic>Monitoring</topic><topic>Nitrogen</topic><topic>Nutrients</topic><topic>Phosphorus</topic><topic>Point source</topic><topic>Pollution, environment geology</topic><topic>Rivers</topic><topic>Synecology</topic><topic>Thames Initiative</topic><topic>Tributaries</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Bowes, Michael J.</creatorcontrib><creatorcontrib>Jarvie, Helen P.</creatorcontrib><creatorcontrib>Naden, Pamela S.</creatorcontrib><creatorcontrib>Old, Gareth H.</creatorcontrib><creatorcontrib>Scarlett, Peter M.</creatorcontrib><creatorcontrib>Roberts, Colin</creatorcontrib><creatorcontrib>Armstrong, Linda K.</creatorcontrib><creatorcontrib>Harman, Sarah A.</creatorcontrib><creatorcontrib>Wickham, Heather D.</creatorcontrib><creatorcontrib>Collins, Adrian L.</creatorcontrib><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>Aqualine</collection><collection>Environment Abstracts</collection><collection>Meteorological & Geoastrophysical Abstracts</collection><collection>Pollution Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 2: Ocean Technology, Policy & Non-Living Resources</collection><collection>Meteorological & Geoastrophysical Abstracts - Academic</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Environment Abstracts</collection><collection>Environmental Engineering Abstracts</collection><collection>Technology Research Database</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><jtitle>Journal of hydrology (Amsterdam)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Bowes, Michael J.</au><au>Jarvie, Helen P.</au><au>Naden, Pamela S.</au><au>Old, Gareth H.</au><au>Scarlett, Peter M.</au><au>Roberts, Colin</au><au>Armstrong, Linda K.</au><au>Harman, Sarah A.</au><au>Wickham, Heather D.</au><au>Collins, Adrian L.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Identifying priorities for nutrient mitigation using river concentration–flow relationships: The Thames basin, UK</atitle><jtitle>Journal of hydrology (Amsterdam)</jtitle><date>2014-09-01</date><risdate>2014</risdate><volume>517</volume><spage>1</spage><epage>12</epage><pages>1-12</pages><issn>0022-1694</issn><eissn>1879-2707</eissn><coden>JHYDA7</coden><abstract>•Load Apportionment Model applied to multiple sites across the Thames basin, UK.•Phosphorus load dominated by sewage inputs during growing season at most sites.•Nitrogen load dominated by diffuse and groundwater inputs throughout year.•Modelling shows need for further P removal from sewage treatment effluents.•Model provides simple and rapid method to identify best mitigation options.
The introduction of tertiary treatment to many of the sewage treatment works (STW) across the Thames basin in southern England has resulted in major reductions in river phosphorus (P) concentrations. Despite this, excessive phytoplankton growth is still a problem in the River Thames and many of its tributaries. There is an urgent need to determine if future resources should focus on P removal from the remaining STW, or on reducing agricultural inputs, to improve ecological status. Nutrient concentration–flow relationships for monitoring sites along the River Thames and 15 of its major tributaries were used to estimate the relative inputs of phosphorus and nitrogen from continuous (sewage point sources) and rain-related (diffuse and within-channel) sources, using the Load Apportionment Model (LAM). The model showed that diffuse sources and remobilisation of within-channel phosphorus contributed the majority of the annual P load at all monitoring sites. However, the majority of rivers in the Thames basin are still dominated by STW P inputs during the ecologically-sensitive spring-autumn growing season. Therefore, further STW improvements would be the most effective way of improving water quality and ecological status along the length of the River Thames, and 12 of the 15 tributaries. The LAM outputs were in agreement with other indicators of sewage input, such as sewered population density, phosphorus speciation and boron concentration. The majority of N inputs were from diffuse sources, and LAM suggests that introducing mitigation measures to reduce inputs from agriculture and groundwater would be most appropriate for all but one monitoring site in this study. The utilisation of nutrient concentration–flow data and LAM provide a simple, rapid and effective screening tool for determining nutrient sources and most effective mitigation options.</abstract><cop>Kidlington</cop><pub>Elsevier B.V</pub><doi>10.1016/j.jhydrol.2014.03.063</doi><tpages>12</tpages><oa>free_for_read</oa></addata></record> |
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subjects | Animal and plant ecology Animal, plant and microbial ecology Basins Biological and medical sciences Diffuse source Diffusion Earth sciences Earth, ocean, space Ecology Engineering and environment geology. Geothermics Exact sciences and technology Fresh water ecosystems Freshwater Fundamental and applied biological sciences. Psychology Hydrology Hydrology. Hydrogeology Load Apportionment Model Monitoring Nitrogen Nutrients Phosphorus Point source Pollution, environment geology Rivers Synecology Thames Initiative Tributaries |
title | Identifying priorities for nutrient mitigation using river concentration–flow relationships: The Thames basin, UK |
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