Methane oxidation coupled to denitrification under microaerobic and hypoxic conditions in leach bed bioreactors

Managing nitrogen and carbon cycles in landfills is an environmental challenge. In this study, our purpose was to test two types of methane oxidation processes coupled to denitrification inside landfills: microaerobic and hypoxic methane oxidation coupled to denitrification (MAME-D and HYME-D). Leac...

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Veröffentlicht in:The Science of the total environment 2019-02, Vol.649, p.1-11
Hauptverfasser: Cao, Qin, Liu, Xiaofeng, Ran, Yi, Li, Zhidong, Li, Dong
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Liu, Xiaofeng
Ran, Yi
Li, Zhidong
Li, Dong
description Managing nitrogen and carbon cycles in landfills is an environmental challenge. In this study, our purpose was to test two types of methane oxidation processes coupled to denitrification inside landfills: microaerobic and hypoxic methane oxidation coupled to denitrification (MAME-D and HYME-D). Leach bed bioreactors were designed and operated for >100 d with NO3−-N concentration ranging from 100 to 400 mg N/L. During six runs of the leach bed bioreactor experiment, leach bed bioreactor 2 (MAME-D) reached 100% denitrification efficiency and the highest average specific denitrification rate of 20.36 mg N/(L·d) in run 5, while leach bed bioreactor 3 (HYME-D) achieved 75% denitrification efficiency and the highest average specific denitrification rate of 8.09 mg N/(L·d) in run 6. Subsequently, waste from leach bed bioreactors 1, 2, and 3 was inoculated into anaerobic bottles to run a batch experiment for 13 d. The total consumed methane, oxygen, and nitrate amounts in the microaerobic system with no methane and oxygen supplement were 2.33, 2.38, and 2.04 mmol, respectively, which almost matched the theoretical equation of aerobic methane oxidation coupled to denitrification. In the hypoxic system, the total consumed methane and nitrate amounts were 0.23 and 0.41 mmol, respectively, the ratio of which closely matched the HYME-D. In addition, via the diverse functional community analysis, methane oxidation in the microaerobic system was confirmed to be conducted by methanotrophs (i.e., Methylobacter and Methylomonas) using oxygen as an electron acceptor. Subsequently, the generated organic compounds could support denitrifiers (i.e., Methylophilaceae) to complete denitrification. In the hypoxic system, Methylomonas and Methylobacter utilized nitrate as a direct electron acceptor to oxidize methane. The two landfill processes characterized here will expand our understanding of the environmental role of methanotrophs and methylotrophs in both carbon and nitrogen cycles. [Display omitted] •MAME-D and HYME-D have the potential to reduce CH4 and NO3− emissions in landfill.•C and N mass balances verify these two processes in cultured landfill samples.•Denitrification rates of MAME-D was higher than that of HYME-D.•Methylobacter and Methylomonas oxidized CH4 using NO3− in HYME-D and O2 in MAME-D.•Methylophilaceae involved in denitrification in the couple system.
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In this study, our purpose was to test two types of methane oxidation processes coupled to denitrification inside landfills: microaerobic and hypoxic methane oxidation coupled to denitrification (MAME-D and HYME-D). Leach bed bioreactors were designed and operated for &gt;100 d with NO3−-N concentration ranging from 100 to 400 mg N/L. During six runs of the leach bed bioreactor experiment, leach bed bioreactor 2 (MAME-D) reached 100% denitrification efficiency and the highest average specific denitrification rate of 20.36 mg N/(L·d) in run 5, while leach bed bioreactor 3 (HYME-D) achieved 75% denitrification efficiency and the highest average specific denitrification rate of 8.09 mg N/(L·d) in run 6. Subsequently, waste from leach bed bioreactors 1, 2, and 3 was inoculated into anaerobic bottles to run a batch experiment for 13 d. The total consumed methane, oxygen, and nitrate amounts in the microaerobic system with no methane and oxygen supplement were 2.33, 2.38, and 2.04 mmol, respectively, which almost matched the theoretical equation of aerobic methane oxidation coupled to denitrification. In the hypoxic system, the total consumed methane and nitrate amounts were 0.23 and 0.41 mmol, respectively, the ratio of which closely matched the HYME-D. In addition, via the diverse functional community analysis, methane oxidation in the microaerobic system was confirmed to be conducted by methanotrophs (i.e., Methylobacter and Methylomonas) using oxygen as an electron acceptor. Subsequently, the generated organic compounds could support denitrifiers (i.e., Methylophilaceae) to complete denitrification. In the hypoxic system, Methylomonas and Methylobacter utilized nitrate as a direct electron acceptor to oxidize methane. The two landfill processes characterized here will expand our understanding of the environmental role of methanotrophs and methylotrophs in both carbon and nitrogen cycles. [Display omitted] •MAME-D and HYME-D have the potential to reduce CH4 and NO3− emissions in landfill.•C and N mass balances verify these two processes in cultured landfill samples.•Denitrification rates of MAME-D was higher than that of HYME-D.•Methylobacter and Methylomonas oxidized CH4 using NO3− in HYME-D and O2 in MAME-D.•Methylophilaceae involved in denitrification in the couple system.</description><identifier>ISSN: 0048-9697</identifier><identifier>EISSN: 1879-1026</identifier><identifier>DOI: 10.1016/j.scitotenv.2018.08.289</identifier><identifier>PMID: 30153511</identifier><language>eng</language><publisher>Netherlands: Elsevier B.V</publisher><subject>Aerobiosis ; Bioreactors ; China ; Denitrification ; Hypoxic methane oxidation ; Landfill ; Leachate denitrification ; Methane - metabolism ; Microaerobic methane oxidation ; Microbial community ; Microbiota ; Nitrates - metabolism ; Oxidation-Reduction ; Refuse Disposal - instrumentation ; Refuse Disposal - methods ; Waste Disposal Facilities</subject><ispartof>The Science of the total environment, 2019-02, Vol.649, p.1-11</ispartof><rights>2018 Elsevier B.V.</rights><rights>Copyright © 2018 Elsevier B.V. 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In this study, our purpose was to test two types of methane oxidation processes coupled to denitrification inside landfills: microaerobic and hypoxic methane oxidation coupled to denitrification (MAME-D and HYME-D). Leach bed bioreactors were designed and operated for &gt;100 d with NO3−-N concentration ranging from 100 to 400 mg N/L. During six runs of the leach bed bioreactor experiment, leach bed bioreactor 2 (MAME-D) reached 100% denitrification efficiency and the highest average specific denitrification rate of 20.36 mg N/(L·d) in run 5, while leach bed bioreactor 3 (HYME-D) achieved 75% denitrification efficiency and the highest average specific denitrification rate of 8.09 mg N/(L·d) in run 6. Subsequently, waste from leach bed bioreactors 1, 2, and 3 was inoculated into anaerobic bottles to run a batch experiment for 13 d. The total consumed methane, oxygen, and nitrate amounts in the microaerobic system with no methane and oxygen supplement were 2.33, 2.38, and 2.04 mmol, respectively, which almost matched the theoretical equation of aerobic methane oxidation coupled to denitrification. In the hypoxic system, the total consumed methane and nitrate amounts were 0.23 and 0.41 mmol, respectively, the ratio of which closely matched the HYME-D. In addition, via the diverse functional community analysis, methane oxidation in the microaerobic system was confirmed to be conducted by methanotrophs (i.e., Methylobacter and Methylomonas) using oxygen as an electron acceptor. Subsequently, the generated organic compounds could support denitrifiers (i.e., Methylophilaceae) to complete denitrification. In the hypoxic system, Methylomonas and Methylobacter utilized nitrate as a direct electron acceptor to oxidize methane. The two landfill processes characterized here will expand our understanding of the environmental role of methanotrophs and methylotrophs in both carbon and nitrogen cycles. [Display omitted] •MAME-D and HYME-D have the potential to reduce CH4 and NO3− emissions in landfill.•C and N mass balances verify these two processes in cultured landfill samples.•Denitrification rates of MAME-D was higher than that of HYME-D.•Methylobacter and Methylomonas oxidized CH4 using NO3− in HYME-D and O2 in MAME-D.•Methylophilaceae involved in denitrification in the couple system.</description><subject>Aerobiosis</subject><subject>Bioreactors</subject><subject>China</subject><subject>Denitrification</subject><subject>Hypoxic methane oxidation</subject><subject>Landfill</subject><subject>Leachate denitrification</subject><subject>Methane - metabolism</subject><subject>Microaerobic methane oxidation</subject><subject>Microbial community</subject><subject>Microbiota</subject><subject>Nitrates - metabolism</subject><subject>Oxidation-Reduction</subject><subject>Refuse Disposal - instrumentation</subject><subject>Refuse Disposal - methods</subject><subject>Waste Disposal Facilities</subject><issn>0048-9697</issn><issn>1879-1026</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2019</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqFkEtvFDEQhC0EIkvgL4CPXGZoe2b8OEYRAaQgLnC2_OjRejU7XmxPRP49Xm3Ilb5YLddXrSpCPjDoGTDx6dAXH2uquD70HJjqQfVc6Rdkx5TUHQMuXpIdwKg6LbS8Im9KOUAbqdhrcjUAm4aJsR1J37Hu7Yo0_YnB1phW6tN2WjDQmmjANdYc5-gvX9saMNNj9DlZzMlFT-0a6P7x1HDfyDXEs7DQuNIFrd9T15xcTLktNeXylrya7VLw3dN7TX7dff55-7W7__Hl2-3NfefHQdbOc3Azd2LWcpKcDyC5Dl5oy8HOg4TRD9Y6x7XSaBHcNDGBbmxs0ErBOFyTjxffU06_NyzVHGPxuCwta9qK4aDFJJRgsknlRdpSlZJxNqccjzY_Ggbm3LY5mOe2zbltA8q0thv5_unI5o4Ynrl_9TbBzUWALepDxHw2wtVjiBl9NSHF_x75C49pl6A</recordid><startdate>20190201</startdate><enddate>20190201</enddate><creator>Cao, Qin</creator><creator>Liu, Xiaofeng</creator><creator>Ran, Yi</creator><creator>Li, Zhidong</creator><creator>Li, Dong</creator><general>Elsevier B.V</general><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>7X8</scope><orcidid>https://orcid.org/0000-0002-8581-8658</orcidid></search><sort><creationdate>20190201</creationdate><title>Methane oxidation coupled to denitrification under microaerobic and hypoxic conditions in leach bed bioreactors</title><author>Cao, Qin ; Liu, Xiaofeng ; Ran, Yi ; Li, Zhidong ; Li, Dong</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c437t-c20bf2b6f97572230729dc69a20af3704c3aabb2989eae0b5516eb4437d988043</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2019</creationdate><topic>Aerobiosis</topic><topic>Bioreactors</topic><topic>China</topic><topic>Denitrification</topic><topic>Hypoxic methane oxidation</topic><topic>Landfill</topic><topic>Leachate denitrification</topic><topic>Methane - metabolism</topic><topic>Microaerobic methane oxidation</topic><topic>Microbial community</topic><topic>Microbiota</topic><topic>Nitrates - metabolism</topic><topic>Oxidation-Reduction</topic><topic>Refuse Disposal - instrumentation</topic><topic>Refuse Disposal - methods</topic><topic>Waste Disposal Facilities</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Cao, Qin</creatorcontrib><creatorcontrib>Liu, Xiaofeng</creatorcontrib><creatorcontrib>Ran, Yi</creatorcontrib><creatorcontrib>Li, Zhidong</creatorcontrib><creatorcontrib>Li, Dong</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>MEDLINE - Academic</collection><jtitle>The Science of the total environment</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Cao, Qin</au><au>Liu, Xiaofeng</au><au>Ran, Yi</au><au>Li, Zhidong</au><au>Li, Dong</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Methane oxidation coupled to denitrification under microaerobic and hypoxic conditions in leach bed bioreactors</atitle><jtitle>The Science of the total environment</jtitle><addtitle>Sci Total Environ</addtitle><date>2019-02-01</date><risdate>2019</risdate><volume>649</volume><spage>1</spage><epage>11</epage><pages>1-11</pages><issn>0048-9697</issn><eissn>1879-1026</eissn><abstract>Managing nitrogen and carbon cycles in landfills is an environmental challenge. In this study, our purpose was to test two types of methane oxidation processes coupled to denitrification inside landfills: microaerobic and hypoxic methane oxidation coupled to denitrification (MAME-D and HYME-D). Leach bed bioreactors were designed and operated for &gt;100 d with NO3−-N concentration ranging from 100 to 400 mg N/L. During six runs of the leach bed bioreactor experiment, leach bed bioreactor 2 (MAME-D) reached 100% denitrification efficiency and the highest average specific denitrification rate of 20.36 mg N/(L·d) in run 5, while leach bed bioreactor 3 (HYME-D) achieved 75% denitrification efficiency and the highest average specific denitrification rate of 8.09 mg N/(L·d) in run 6. Subsequently, waste from leach bed bioreactors 1, 2, and 3 was inoculated into anaerobic bottles to run a batch experiment for 13 d. The total consumed methane, oxygen, and nitrate amounts in the microaerobic system with no methane and oxygen supplement were 2.33, 2.38, and 2.04 mmol, respectively, which almost matched the theoretical equation of aerobic methane oxidation coupled to denitrification. In the hypoxic system, the total consumed methane and nitrate amounts were 0.23 and 0.41 mmol, respectively, the ratio of which closely matched the HYME-D. In addition, via the diverse functional community analysis, methane oxidation in the microaerobic system was confirmed to be conducted by methanotrophs (i.e., Methylobacter and Methylomonas) using oxygen as an electron acceptor. Subsequently, the generated organic compounds could support denitrifiers (i.e., Methylophilaceae) to complete denitrification. In the hypoxic system, Methylomonas and Methylobacter utilized nitrate as a direct electron acceptor to oxidize methane. The two landfill processes characterized here will expand our understanding of the environmental role of methanotrophs and methylotrophs in both carbon and nitrogen cycles. [Display omitted] •MAME-D and HYME-D have the potential to reduce CH4 and NO3− emissions in landfill.•C and N mass balances verify these two processes in cultured landfill samples.•Denitrification rates of MAME-D was higher than that of HYME-D.•Methylobacter and Methylomonas oxidized CH4 using NO3− in HYME-D and O2 in MAME-D.•Methylophilaceae involved in denitrification in the couple system.</abstract><cop>Netherlands</cop><pub>Elsevier B.V</pub><pmid>30153511</pmid><doi>10.1016/j.scitotenv.2018.08.289</doi><tpages>11</tpages><orcidid>https://orcid.org/0000-0002-8581-8658</orcidid></addata></record>
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subjects Aerobiosis
Bioreactors
China
Denitrification
Hypoxic methane oxidation
Landfill
Leachate denitrification
Methane - metabolism
Microaerobic methane oxidation
Microbial community
Microbiota
Nitrates - metabolism
Oxidation-Reduction
Refuse Disposal - instrumentation
Refuse Disposal - methods
Waste Disposal Facilities
title Methane oxidation coupled to denitrification under microaerobic and hypoxic conditions in leach bed bioreactors
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