Human activities cause distinct dissolved organic matter composition across freshwater ecosystems
Dissolved organic matter (DOM) composition in freshwater ecosystems is influenced by the interactions among physical, chemical, and biological processes that are controlled, at one level, by watershed landscape, hydrology, and their connections. Against this environmental template, humans may strong...
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Veröffentlicht in: | Global change biology 2016-02, Vol.22 (2), p.613-626 |
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creator | Williams, Clayton J. Frost, Paul C. Morales-Williams, Ana M. Larson, James H. Richardson, William B. Chiandet, Aisha S. Xenopoulos, Marguerite A. |
description | Dissolved organic matter (DOM) composition in freshwater ecosystems is influenced by the interactions among physical, chemical, and biological processes that are controlled, at one level, by watershed landscape, hydrology, and their connections. Against this environmental template, humans may strongly influence DOM composition. Yet, we lack a comprehensive understanding of DOM composition variation across freshwater ecosystems differentially affected by human activity. Using optical properties, we described DOM variation across five ecosystem groups of the Laurentian Great Lakes region: large lakes, Kawartha Lakes, Experimental Lakes Area, urban stormwater ponds, and rivers (n = 184 sites). We determined how between ecosystem variation in DOM composition related to watershed size, land use and cover, water quality measures (conductivity, dissolved organic carbon (DOC), nutrient concentration, chlorophyll a), and human population density. The five freshwater ecosystem groups had distinctive DOM composition from each other. These significant differences were not explained completely through differences in watershed size nor spatial autocorrelation. Instead, multivariate partial least squares regression showed that DOM composition was related to differences in human impact across freshwater ecosystems. In particular, urban/developed watersheds with higher human population densities had a unique DOM composition with a clear anthropogenic influence that was distinct from DOM composition in natural land cover and/or agricultural watersheds. This nonagricultural, human developed impact on aquatic DOM was most evident through increased levels of a microbial, humic‐like parallel factor analysis component (C6). Lotic and lentic ecosystems with low human population densities had DOM compositions more typical of clear water to humic‐rich freshwater ecosystems but C6 was only present at trace to background levels. Consequently, humans are strongly altering the quality of DOM in waters nearby or flowing through highly populated areas, which may alter carbon cycles in anthropogenically disturbed ecosystems at broad scales. |
doi_str_mv | 10.1111/gcb.13094 |
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Against this environmental template, humans may strongly influence DOM composition. Yet, we lack a comprehensive understanding of DOM composition variation across freshwater ecosystems differentially affected by human activity. Using optical properties, we described DOM variation across five ecosystem groups of the Laurentian Great Lakes region: large lakes, Kawartha Lakes, Experimental Lakes Area, urban stormwater ponds, and rivers (n = 184 sites). We determined how between ecosystem variation in DOM composition related to watershed size, land use and cover, water quality measures (conductivity, dissolved organic carbon (DOC), nutrient concentration, chlorophyll a), and human population density. The five freshwater ecosystem groups had distinctive DOM composition from each other. These significant differences were not explained completely through differences in watershed size nor spatial autocorrelation. Instead, multivariate partial least squares regression showed that DOM composition was related to differences in human impact across freshwater ecosystems. In particular, urban/developed watersheds with higher human population densities had a unique DOM composition with a clear anthropogenic influence that was distinct from DOM composition in natural land cover and/or agricultural watersheds. This nonagricultural, human developed impact on aquatic DOM was most evident through increased levels of a microbial, humic‐like parallel factor analysis component (C6). Lotic and lentic ecosystems with low human population densities had DOM compositions more typical of clear water to humic‐rich freshwater ecosystems but C6 was only present at trace to background levels. Consequently, humans are strongly altering the quality of DOM in waters nearby or flowing through highly populated areas, which may alter carbon cycles in anthropogenically disturbed ecosystems at broad scales.</description><identifier>ISSN: 1354-1013</identifier><identifier>EISSN: 1365-2486</identifier><identifier>DOI: 10.1111/gcb.13094</identifier><identifier>PMID: 26390994</identifier><language>eng</language><publisher>England: Blackwell Science</publisher><subject>anthropogenic ; Aquatic ecosystems ; Biogeochemistry ; Canada ; Carbon - analysis ; carbon cycling ; Chlorophyll - analysis ; cultural eutrophication ; Ecosystem ; fluorescence spectroscopy ; Freshwater ; Human Activities ; Human influences ; Humans ; Lakes ; land use ; Nitrates - analysis ; Nitrites - analysis ; parallel factor analysis modeling ; Phosphorus - analysis ; Ponds ; Population Density ; Rivers ; United States ; urban ; UV-visible absorbance ; Water Pollutants - analysis ; Water Quality</subject><ispartof>Global change biology, 2016-02, Vol.22 (2), p.613-626</ispartof><rights>2015 John Wiley & Sons Ltd</rights><rights>2015 John Wiley & Sons Ltd.</rights><rights>Copyright © 2016 John Wiley & Sons Ltd</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4994-363b4dacb85e96720eee3b56563587c81148be61b31983f6d262f45891f62b33</citedby><cites>FETCH-LOGICAL-c4994-363b4dacb85e96720eee3b56563587c81148be61b31983f6d262f45891f62b33</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://onlinelibrary.wiley.com/doi/pdf/10.1111%2Fgcb.13094$$EPDF$$P50$$Gwiley$$H</linktopdf><linktohtml>$$Uhttps://onlinelibrary.wiley.com/doi/full/10.1111%2Fgcb.13094$$EHTML$$P50$$Gwiley$$H</linktohtml><link.rule.ids>314,776,780,1411,27901,27902,45550,45551</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/26390994$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Williams, Clayton J.</creatorcontrib><creatorcontrib>Frost, Paul C.</creatorcontrib><creatorcontrib>Morales-Williams, Ana M.</creatorcontrib><creatorcontrib>Larson, James H.</creatorcontrib><creatorcontrib>Richardson, William B.</creatorcontrib><creatorcontrib>Chiandet, Aisha S.</creatorcontrib><creatorcontrib>Xenopoulos, Marguerite A.</creatorcontrib><title>Human activities cause distinct dissolved organic matter composition across freshwater ecosystems</title><title>Global change biology</title><addtitle>Glob Change Biol</addtitle><description>Dissolved organic matter (DOM) composition in freshwater ecosystems is influenced by the interactions among physical, chemical, and biological processes that are controlled, at one level, by watershed landscape, hydrology, and their connections. Against this environmental template, humans may strongly influence DOM composition. Yet, we lack a comprehensive understanding of DOM composition variation across freshwater ecosystems differentially affected by human activity. Using optical properties, we described DOM variation across five ecosystem groups of the Laurentian Great Lakes region: large lakes, Kawartha Lakes, Experimental Lakes Area, urban stormwater ponds, and rivers (n = 184 sites). We determined how between ecosystem variation in DOM composition related to watershed size, land use and cover, water quality measures (conductivity, dissolved organic carbon (DOC), nutrient concentration, chlorophyll a), and human population density. The five freshwater ecosystem groups had distinctive DOM composition from each other. These significant differences were not explained completely through differences in watershed size nor spatial autocorrelation. Instead, multivariate partial least squares regression showed that DOM composition was related to differences in human impact across freshwater ecosystems. In particular, urban/developed watersheds with higher human population densities had a unique DOM composition with a clear anthropogenic influence that was distinct from DOM composition in natural land cover and/or agricultural watersheds. This nonagricultural, human developed impact on aquatic DOM was most evident through increased levels of a microbial, humic‐like parallel factor analysis component (C6). Lotic and lentic ecosystems with low human population densities had DOM compositions more typical of clear water to humic‐rich freshwater ecosystems but C6 was only present at trace to background levels. Consequently, humans are strongly altering the quality of DOM in waters nearby or flowing through highly populated areas, which may alter carbon cycles in anthropogenically disturbed ecosystems at broad scales.</description><subject>anthropogenic</subject><subject>Aquatic ecosystems</subject><subject>Biogeochemistry</subject><subject>Canada</subject><subject>Carbon - analysis</subject><subject>carbon cycling</subject><subject>Chlorophyll - analysis</subject><subject>cultural eutrophication</subject><subject>Ecosystem</subject><subject>fluorescence spectroscopy</subject><subject>Freshwater</subject><subject>Human Activities</subject><subject>Human influences</subject><subject>Humans</subject><subject>Lakes</subject><subject>land use</subject><subject>Nitrates - analysis</subject><subject>Nitrites - analysis</subject><subject>parallel factor analysis modeling</subject><subject>Phosphorus - analysis</subject><subject>Ponds</subject><subject>Population Density</subject><subject>Rivers</subject><subject>United States</subject><subject>urban</subject><subject>UV-visible absorbance</subject><subject>Water Pollutants - analysis</subject><subject>Water Quality</subject><issn>1354-1013</issn><issn>1365-2486</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2016</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqNks1u1DAUhS0EomVgwQtAJDawSOv_xEsY6BSpAiGKWFq2czO4JPFgJy3zNjwLT4bTtF0gIWHJ8pXud47se4zQU4KPSF7HW2ePCMOK30OHhElRUl7L-3MteEkwYQfoUUoXGGNGsXyIDqhkCivFD5E9nXozFMaN_tKPHlLhzJSgaHwa_eDGuUihu4SmCHFrBu-K3owjxN-_XOh3IWVRmPUxpFS0EdK3K5PbBbiQ9mmEPj1GD1rTJXhyc67Q-cm78_VpefZx8379-qx0PF-lZJJZ3hhnawFKVhQDALNCCslEXbmaEF5bkMQyomrWyoZK2nJRK9JKahlboZeL7S6GHxOkUfc-Oeg6M0CYkiZVJWX2UvQ_UElwpTid0Rd_oRdhikN-x0zhvKVQmXq1UNdjiNDqXfS9iXtNsJ4j0jkifR1RZp_dOE62h-aOvM0kA8cLcOU72P_bSW_Wb24ty0WRQ4OfdwoTv2tZsUrorx82mnw62bC3mGXxCj1f-NYEbbbRJ_3lM8VE4vxXRE0q9gc4NrMC</recordid><startdate>201602</startdate><enddate>201602</enddate><creator>Williams, Clayton J.</creator><creator>Frost, Paul C.</creator><creator>Morales-Williams, Ana M.</creator><creator>Larson, James H.</creator><creator>Richardson, William B.</creator><creator>Chiandet, Aisha S.</creator><creator>Xenopoulos, Marguerite A.</creator><general>Blackwell Science</general><general>Blackwell Publishing Ltd</general><scope>FBQ</scope><scope>BSCLL</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7SN</scope><scope>7UA</scope><scope>C1K</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope><scope>7X8</scope><scope>7QH</scope><scope>7ST</scope><scope>7U6</scope><scope>SOI</scope></search><sort><creationdate>201602</creationdate><title>Human activities cause distinct dissolved organic matter composition across freshwater ecosystems</title><author>Williams, Clayton J. ; Frost, Paul C. ; Morales-Williams, Ana M. ; Larson, James H. ; Richardson, William B. ; Chiandet, Aisha S. ; Xenopoulos, Marguerite A.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4994-363b4dacb85e96720eee3b56563587c81148be61b31983f6d262f45891f62b33</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2016</creationdate><topic>anthropogenic</topic><topic>Aquatic ecosystems</topic><topic>Biogeochemistry</topic><topic>Canada</topic><topic>Carbon - analysis</topic><topic>carbon cycling</topic><topic>Chlorophyll - analysis</topic><topic>cultural eutrophication</topic><topic>Ecosystem</topic><topic>fluorescence spectroscopy</topic><topic>Freshwater</topic><topic>Human Activities</topic><topic>Human influences</topic><topic>Humans</topic><topic>Lakes</topic><topic>land use</topic><topic>Nitrates - analysis</topic><topic>Nitrites - analysis</topic><topic>parallel factor analysis modeling</topic><topic>Phosphorus - analysis</topic><topic>Ponds</topic><topic>Population Density</topic><topic>Rivers</topic><topic>United States</topic><topic>urban</topic><topic>UV-visible absorbance</topic><topic>Water Pollutants - analysis</topic><topic>Water Quality</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Williams, Clayton J.</creatorcontrib><creatorcontrib>Frost, Paul C.</creatorcontrib><creatorcontrib>Morales-Williams, Ana M.</creatorcontrib><creatorcontrib>Larson, James H.</creatorcontrib><creatorcontrib>Richardson, William B.</creatorcontrib><creatorcontrib>Chiandet, Aisha S.</creatorcontrib><creatorcontrib>Xenopoulos, Marguerite A.</creatorcontrib><collection>AGRIS</collection><collection>Istex</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Ecology 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) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>MEDLINE - Academic</collection><collection>Aqualine</collection><collection>Environment Abstracts</collection><collection>Sustainability Science Abstracts</collection><collection>Environment Abstracts</collection><jtitle>Global change biology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Williams, Clayton J.</au><au>Frost, Paul C.</au><au>Morales-Williams, Ana M.</au><au>Larson, James H.</au><au>Richardson, William B.</au><au>Chiandet, Aisha S.</au><au>Xenopoulos, Marguerite A.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Human activities cause distinct dissolved organic matter composition across freshwater ecosystems</atitle><jtitle>Global change biology</jtitle><addtitle>Glob Change Biol</addtitle><date>2016-02</date><risdate>2016</risdate><volume>22</volume><issue>2</issue><spage>613</spage><epage>626</epage><pages>613-626</pages><issn>1354-1013</issn><eissn>1365-2486</eissn><abstract>Dissolved organic matter (DOM) composition in freshwater ecosystems is influenced by the interactions among physical, chemical, and biological processes that are controlled, at one level, by watershed landscape, hydrology, and their connections. Against this environmental template, humans may strongly influence DOM composition. Yet, we lack a comprehensive understanding of DOM composition variation across freshwater ecosystems differentially affected by human activity. Using optical properties, we described DOM variation across five ecosystem groups of the Laurentian Great Lakes region: large lakes, Kawartha Lakes, Experimental Lakes Area, urban stormwater ponds, and rivers (n = 184 sites). We determined how between ecosystem variation in DOM composition related to watershed size, land use and cover, water quality measures (conductivity, dissolved organic carbon (DOC), nutrient concentration, chlorophyll a), and human population density. The five freshwater ecosystem groups had distinctive DOM composition from each other. These significant differences were not explained completely through differences in watershed size nor spatial autocorrelation. Instead, multivariate partial least squares regression showed that DOM composition was related to differences in human impact across freshwater ecosystems. In particular, urban/developed watersheds with higher human population densities had a unique DOM composition with a clear anthropogenic influence that was distinct from DOM composition in natural land cover and/or agricultural watersheds. This nonagricultural, human developed impact on aquatic DOM was most evident through increased levels of a microbial, humic‐like parallel factor analysis component (C6). Lotic and lentic ecosystems with low human population densities had DOM compositions more typical of clear water to humic‐rich freshwater ecosystems but C6 was only present at trace to background levels. Consequently, humans are strongly altering the quality of DOM in waters nearby or flowing through highly populated areas, which may alter carbon cycles in anthropogenically disturbed ecosystems at broad scales.</abstract><cop>England</cop><pub>Blackwell Science</pub><pmid>26390994</pmid><doi>10.1111/gcb.13094</doi><tpages>14</tpages></addata></record> |
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subjects | anthropogenic Aquatic ecosystems Biogeochemistry Canada Carbon - analysis carbon cycling Chlorophyll - analysis cultural eutrophication Ecosystem fluorescence spectroscopy Freshwater Human Activities Human influences Humans Lakes land use Nitrates - analysis Nitrites - analysis parallel factor analysis modeling Phosphorus - analysis Ponds Population Density Rivers United States urban UV-visible absorbance Water Pollutants - analysis Water Quality |
title | Human activities cause distinct dissolved organic matter composition across freshwater ecosystems |
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