The potential importance of bacterial processes in regulating rate of lake acidification [Canadian Shield lakes; Canada]
Rates of microbial reduction of O2, Fe3+, Mn4+, NO3-, and SO42-, and total generation of CO2 and CH4 were measured in the hypolimnia of three Canadian Shield lakes. Methanogenesis accounted for 72-80% of anoxic carbon generation, while sulfate reduction contributed 16-20%. The remainder of anoxic ca...
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Veröffentlicht in: | Limnol. Oceanogr.; (United States) 1982-01, Vol.27 (5), p.868-882 |
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description | Rates of microbial reduction of O2, Fe3+, Mn4+, NO3-, and SO42-, and total generation of CO2 and CH4 were measured in the hypolimnia of three Canadian Shield lakes. Methanogenesis accounted for 72-80% of anoxic carbon generation, while sulfate reduction contributed 16-20%. The remainder of anoxic carbon generation (2-8%) originated from all of the other processes combined (nitrate, iron, and manganese reduction). In lakes affected by acid deposition,inputs of sulfate and nitrate will increase, and it is expected that reducing power normally going to methane production will be diverted to nitrate and sulfate reduction. The last two reduction reactions can result in alkalinity production, whereas methane production does not. A model was developed to predict the significance of hypolimnetic alkalinity production which could result from these reactions in lakes with known hypolimnetic reducing power (methane production). The model showed that the hypolimnia of two ELA lakes which have been made eutrophic artificially could potentially produce enough persistent alkalinity to neutralize "typical" acid deposition, while a lake that was not eutrophic could not. Besides trophic state, other factors important in determining a lake's capability for hypolimnetic alkalinity production were watershed area: surface area ratio, the watershed retentions of H+, SO42-, NO3-, and NH4+, and the degree of precipitation of FeS in the sediment. |
doi_str_mv | 10.4319/lo.1982.27.5.0868 |
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A. ; John W. M. Rudd ; Cook, R. B. ; Schindler, D. W.</creator><creatorcontrib>Kelly, C. A. ; John W. M. Rudd ; Cook, R. B. ; Schindler, D. W.</creatorcontrib><description>Rates of microbial reduction of O2, Fe3+, Mn4+, NO3-, and SO42-, and total generation of CO2 and CH4 were measured in the hypolimnia of three Canadian Shield lakes. Methanogenesis accounted for 72-80% of anoxic carbon generation, while sulfate reduction contributed 16-20%. The remainder of anoxic carbon generation (2-8%) originated from all of the other processes combined (nitrate, iron, and manganese reduction). In lakes affected by acid deposition,inputs of sulfate and nitrate will increase, and it is expected that reducing power normally going to methane production will be diverted to nitrate and sulfate reduction. The last two reduction reactions can result in alkalinity production, whereas methane production does not. A model was developed to predict the significance of hypolimnetic alkalinity production which could result from these reactions in lakes with known hypolimnetic reducing power (methane production). The model showed that the hypolimnia of two ELA lakes which have been made eutrophic artificially could potentially produce enough persistent alkalinity to neutralize "typical" acid deposition, while a lake that was not eutrophic could not. Besides trophic state, other factors important in determining a lake's capability for hypolimnetic alkalinity production were watershed area: surface area ratio, the watershed retentions of H+, SO42-, NO3-, and NH4+, and the degree of precipitation of FeS in the sediment.</description><identifier>ISSN: 0024-3590</identifier><identifier>EISSN: 1939-5590</identifier><identifier>DOI: 10.4319/lo.1982.27.5.0868</identifier><language>eng</language><publisher>United States: American Society of Limnology and Oceanography</publisher><subject>520200 - Environment, Aquatic- Chemicals Monitoring & Transport- (-1989) ; 550700 - Microbiology ; Acidification ; Alkalinity ; ALKANES ; BACTERIA ; BASIC BIOLOGICAL SCIENCES ; BIODEGRADATION ; BIOLOGICAL MODELS ; CANADA ; CARBON COMPOUNDS ; CARBON DIOXIDE ; CARBON OXIDES ; CHALCOGENIDES ; CHEMICAL REACTIONS ; DECOMPOSITION ; ELEMENTS ; ENVIRONMENTAL SCIENCES ; Freshwater ; HYDROCARBONS ; IRON COMPOUNDS ; LAKES ; LIMNOLOGY ; MANGANESE ; METALS ; METHANE ; Methane production ; MICROORGANISMS ; NITRATES ; NITROGEN COMPOUNDS ; NONMETALS ; NORTH AMERICA ; ORGANIC COMPOUNDS ; OXIDES ; OXYGEN ; OXYGEN COMPOUNDS ; PH VALUE ; REDUCTION ; Sediments ; SULFATES ; SULFUR COMPOUNDS ; SURFACE WATERS ; TRANSITION ELEMENT COMPOUNDS ; TRANSITION ELEMENTS ; Watersheds</subject><ispartof>Limnol. Oceanogr.; (United States), 1982-01, Vol.27 (5), p.868-882</ispartof><rights>Copyright 1982 American Society of Limnology and Oceanography, Inc.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/2835971$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/2835971$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,780,784,803,885,27924,27925,58017,58250</link.rule.ids><backlink>$$Uhttps://www.osti.gov/biblio/6193038$$D View this record in Osti.gov$$Hfree_for_read</backlink></links><search><creatorcontrib>Kelly, C. A.</creatorcontrib><creatorcontrib>John W. M. Rudd</creatorcontrib><creatorcontrib>Cook, R. B.</creatorcontrib><creatorcontrib>Schindler, D. W.</creatorcontrib><title>The potential importance of bacterial processes in regulating rate of lake acidification [Canadian Shield lakes; Canada]</title><title>Limnol. Oceanogr.; (United States)</title><description>Rates of microbial reduction of O2, Fe3+, Mn4+, NO3-, and SO42-, and total generation of CO2 and CH4 were measured in the hypolimnia of three Canadian Shield lakes. Methanogenesis accounted for 72-80% of anoxic carbon generation, while sulfate reduction contributed 16-20%. The remainder of anoxic carbon generation (2-8%) originated from all of the other processes combined (nitrate, iron, and manganese reduction). In lakes affected by acid deposition,inputs of sulfate and nitrate will increase, and it is expected that reducing power normally going to methane production will be diverted to nitrate and sulfate reduction. The last two reduction reactions can result in alkalinity production, whereas methane production does not. A model was developed to predict the significance of hypolimnetic alkalinity production which could result from these reactions in lakes with known hypolimnetic reducing power (methane production). The model showed that the hypolimnia of two ELA lakes which have been made eutrophic artificially could potentially produce enough persistent alkalinity to neutralize "typical" acid deposition, while a lake that was not eutrophic could not. Besides trophic state, other factors important in determining a lake's capability for hypolimnetic alkalinity production were watershed area: surface area ratio, the watershed retentions of H+, SO42-, NO3-, and NH4+, and the degree of precipitation of FeS in the sediment.</description><subject>520200 - Environment, Aquatic- Chemicals Monitoring & Transport- (-1989)</subject><subject>550700 - Microbiology</subject><subject>Acidification</subject><subject>Alkalinity</subject><subject>ALKANES</subject><subject>BACTERIA</subject><subject>BASIC BIOLOGICAL SCIENCES</subject><subject>BIODEGRADATION</subject><subject>BIOLOGICAL MODELS</subject><subject>CANADA</subject><subject>CARBON COMPOUNDS</subject><subject>CARBON DIOXIDE</subject><subject>CARBON OXIDES</subject><subject>CHALCOGENIDES</subject><subject>CHEMICAL REACTIONS</subject><subject>DECOMPOSITION</subject><subject>ELEMENTS</subject><subject>ENVIRONMENTAL SCIENCES</subject><subject>Freshwater</subject><subject>HYDROCARBONS</subject><subject>IRON COMPOUNDS</subject><subject>LAKES</subject><subject>LIMNOLOGY</subject><subject>MANGANESE</subject><subject>METALS</subject><subject>METHANE</subject><subject>Methane production</subject><subject>MICROORGANISMS</subject><subject>NITRATES</subject><subject>NITROGEN COMPOUNDS</subject><subject>NONMETALS</subject><subject>NORTH AMERICA</subject><subject>ORGANIC COMPOUNDS</subject><subject>OXIDES</subject><subject>OXYGEN</subject><subject>OXYGEN COMPOUNDS</subject><subject>PH VALUE</subject><subject>REDUCTION</subject><subject>Sediments</subject><subject>SULFATES</subject><subject>SULFUR COMPOUNDS</subject><subject>SURFACE WATERS</subject><subject>TRANSITION ELEMENT COMPOUNDS</subject><subject>TRANSITION ELEMENTS</subject><subject>Watersheds</subject><issn>0024-3590</issn><issn>1939-5590</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1982</creationdate><recordtype>article</recordtype><recordid>eNqFkU1LJDEQhsOisOPHDxBEwh721m0-uxM8LcOuCoIH9STS1KSTmWhPMptkQP_9xpm9e6qinoeCqhehM0pawam-nGJLtWIt61vZEtWpb2hGNdeNlJocoBkhTDS89t_RUc6vhBAtpZyh98eVxZtYbCgeJuzXm5gKBGNxdHgBptj0Od-kaGzONmMfcLLL7QTFhyVOUHbmBG8Wg_Gjd95UFAN-nkOA0UPADytvp3Hn5Cu8G8PLCTp0MGV7-r8eo6c_vx_nN83d_fXt_Ndd45hSpVEdpcJpt9DdSNgoOKN9D1JRIRxI5xZGaVvByEwve9FrDsyM2hEJQnQLxY_Rj_3emIsfsvHFmpWJIVhThq6-iPBP6edeqnf-3dpchrXPxk4TBBu3eaBSCtpL8bXIVddpoqt4vhdfc4lp2CS_hvQxMFUz6GnFF3vsIA6wTD4PTw81QE6U6gQR_B_1BYzr</recordid><startdate>19820101</startdate><enddate>19820101</enddate><creator>Kelly, C. A.</creator><creator>John W. M. Rudd</creator><creator>Cook, R. B.</creator><creator>Schindler, D. W.</creator><general>American Society of Limnology and Oceanography</general><scope>FBQ</scope><scope>7QH</scope><scope>7QL</scope><scope>7SN</scope><scope>C1K</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope><scope>OTOTI</scope></search><sort><creationdate>19820101</creationdate><title>The potential importance of bacterial processes in regulating rate of lake acidification [Canadian Shield lakes; Canada]</title><author>Kelly, C. A. ; John W. M. Rudd ; Cook, R. B. ; Schindler, D. W.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-f288t-86114f9fb96d02d432177a58144fa5ffbc89e02dd2c7574793a2cd9f05a446b83</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1982</creationdate><topic>520200 - Environment, Aquatic- Chemicals Monitoring & Transport- (-1989)</topic><topic>550700 - Microbiology</topic><topic>Acidification</topic><topic>Alkalinity</topic><topic>ALKANES</topic><topic>BACTERIA</topic><topic>BASIC BIOLOGICAL SCIENCES</topic><topic>BIODEGRADATION</topic><topic>BIOLOGICAL MODELS</topic><topic>CANADA</topic><topic>CARBON COMPOUNDS</topic><topic>CARBON DIOXIDE</topic><topic>CARBON OXIDES</topic><topic>CHALCOGENIDES</topic><topic>CHEMICAL REACTIONS</topic><topic>DECOMPOSITION</topic><topic>ELEMENTS</topic><topic>ENVIRONMENTAL SCIENCES</topic><topic>Freshwater</topic><topic>HYDROCARBONS</topic><topic>IRON COMPOUNDS</topic><topic>LAKES</topic><topic>LIMNOLOGY</topic><topic>MANGANESE</topic><topic>METALS</topic><topic>METHANE</topic><topic>Methane production</topic><topic>MICROORGANISMS</topic><topic>NITRATES</topic><topic>NITROGEN COMPOUNDS</topic><topic>NONMETALS</topic><topic>NORTH AMERICA</topic><topic>ORGANIC COMPOUNDS</topic><topic>OXIDES</topic><topic>OXYGEN</topic><topic>OXYGEN COMPOUNDS</topic><topic>PH VALUE</topic><topic>REDUCTION</topic><topic>Sediments</topic><topic>SULFATES</topic><topic>SULFUR COMPOUNDS</topic><topic>SURFACE WATERS</topic><topic>TRANSITION ELEMENT COMPOUNDS</topic><topic>TRANSITION ELEMENTS</topic><topic>Watersheds</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Kelly, C. A.</creatorcontrib><creatorcontrib>John W. M. Rudd</creatorcontrib><creatorcontrib>Cook, R. B.</creatorcontrib><creatorcontrib>Schindler, D. W.</creatorcontrib><collection>AGRIS</collection><collection>Aqualine</collection><collection>Bacteriology Abstracts (Microbiology B)</collection><collection>Ecology 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>OSTI.GOV</collection><jtitle>Limnol. Oceanogr.; (United States)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Kelly, C. A.</au><au>John W. M. Rudd</au><au>Cook, R. B.</au><au>Schindler, D. W.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>The potential importance of bacterial processes in regulating rate of lake acidification [Canadian Shield lakes; Canada]</atitle><jtitle>Limnol. Oceanogr.; (United States)</jtitle><date>1982-01-01</date><risdate>1982</risdate><volume>27</volume><issue>5</issue><spage>868</spage><epage>882</epage><pages>868-882</pages><issn>0024-3590</issn><eissn>1939-5590</eissn><abstract>Rates of microbial reduction of O2, Fe3+, Mn4+, NO3-, and SO42-, and total generation of CO2 and CH4 were measured in the hypolimnia of three Canadian Shield lakes. Methanogenesis accounted for 72-80% of anoxic carbon generation, while sulfate reduction contributed 16-20%. The remainder of anoxic carbon generation (2-8%) originated from all of the other processes combined (nitrate, iron, and manganese reduction). In lakes affected by acid deposition,inputs of sulfate and nitrate will increase, and it is expected that reducing power normally going to methane production will be diverted to nitrate and sulfate reduction. The last two reduction reactions can result in alkalinity production, whereas methane production does not. A model was developed to predict the significance of hypolimnetic alkalinity production which could result from these reactions in lakes with known hypolimnetic reducing power (methane production). The model showed that the hypolimnia of two ELA lakes which have been made eutrophic artificially could potentially produce enough persistent alkalinity to neutralize "typical" acid deposition, while a lake that was not eutrophic could not. Besides trophic state, other factors important in determining a lake's capability for hypolimnetic alkalinity production were watershed area: surface area ratio, the watershed retentions of H+, SO42-, NO3-, and NH4+, and the degree of precipitation of FeS in the sediment.</abstract><cop>United States</cop><pub>American Society of Limnology and Oceanography</pub><doi>10.4319/lo.1982.27.5.0868</doi><tpages>15</tpages></addata></record> |
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source | JSTOR Archive Collection A-Z Listing; EZB-FREE-00999 freely available EZB journals; Alma/SFX Local Collection |
subjects | 520200 - Environment, Aquatic- Chemicals Monitoring & Transport- (-1989) 550700 - Microbiology Acidification Alkalinity ALKANES BACTERIA BASIC BIOLOGICAL SCIENCES BIODEGRADATION BIOLOGICAL MODELS CANADA CARBON COMPOUNDS CARBON DIOXIDE CARBON OXIDES CHALCOGENIDES CHEMICAL REACTIONS DECOMPOSITION ELEMENTS ENVIRONMENTAL SCIENCES Freshwater HYDROCARBONS IRON COMPOUNDS LAKES LIMNOLOGY MANGANESE METALS METHANE Methane production MICROORGANISMS NITRATES NITROGEN COMPOUNDS NONMETALS NORTH AMERICA ORGANIC COMPOUNDS OXIDES OXYGEN OXYGEN COMPOUNDS PH VALUE REDUCTION Sediments SULFATES SULFUR COMPOUNDS SURFACE WATERS TRANSITION ELEMENT COMPOUNDS TRANSITION ELEMENTS Watersheds |
title | The potential importance of bacterial processes in regulating rate of lake acidification [Canadian Shield lakes; Canada] |
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