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Screening and Degradation Mechanism of a Cold-Resistant Nitrobenzene-Degrading Microorganism
A cold-resistant nitrobenzene-degrading strain was screened from river sediment. The strain was identified as Methylobacillus glycogens, which has never been reported to be capable of degrading nitrobenzene. The degradation rates of 900 μg/L nitrobenzene reached respectively 99.3% and 88.6% in 144 h...
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Published in: | Water environment research 2017-11, Vol.89 (11), p.1970-1980 |
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container_end_page | 1980 |
container_issue | 11 |
container_start_page | 1970 |
container_title | Water environment research |
container_volume | 89 |
creator | Qiu, Liping Wang, Hu Wang, Xuntao |
description | A cold-resistant nitrobenzene-degrading strain was screened from river sediment. The strain was identified as Methylobacillus glycogens, which has never been reported to be capable of degrading nitrobenzene. The degradation rates of 900 μg/L nitrobenzene reached respectively 99.3% and 88.6% in 144 h under both aerobic and anaerobic environments (30 mL inoculation volume at 12 ± 0.5 °C and pH7.0 ± 0.1). When aerobically degraded, nitrobenzene was firstly oxidized into o-nitrophenol, which was further oxidized into 1,2-benzenediol, meanwhile releasing NO2-. Then the 1,2-benzenediol was metabolized through either the ortho-cleavage into succinic acid and acetyl-CoA, or meta-cleavage into pyruvic acid and acetaldehyde, as well as other small molecule substances of non-toxicity or low-toxicity, which were finally decomposed into CO₂ and H₂O. When anaerobically degraded, nitrobenzene was firstly degraded into aniline (C₆H₅NH₂), which was further degraded into 4-amino benzoic acid. The benzoic acid was degraded into benzoyl, which was finally metabolized and decomposed. |
doi_str_mv | 10.2175/106143017X15051465918958 |
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The strain was identified as Methylobacillus glycogens, which has never been reported to be capable of degrading nitrobenzene. The degradation rates of 900 μg/L nitrobenzene reached respectively 99.3% and 88.6% in 144 h under both aerobic and anaerobic environments (30 mL inoculation volume at 12 ± 0.5 °C and pH7.0 ± 0.1). When aerobically degraded, nitrobenzene was firstly oxidized into o-nitrophenol, which was further oxidized into 1,2-benzenediol, meanwhile releasing NO2-. Then the 1,2-benzenediol was metabolized through either the ortho-cleavage into succinic acid and acetyl-CoA, or meta-cleavage into pyruvic acid and acetaldehyde, as well as other small molecule substances of non-toxicity or low-toxicity, which were finally decomposed into CO₂ and H₂O. When anaerobically degraded, nitrobenzene was firstly degraded into aniline (C₆H₅NH₂), which was further degraded into 4-amino benzoic acid. The benzoic acid was degraded into benzoyl, which was finally metabolized and decomposed.</description><identifier>ISSN: 1061-4303</identifier><identifier>EISSN: 1554-7531</identifier><identifier>DOI: 10.2175/106143017X15051465918958</identifier><identifier>PMID: 29080565</identifier><language>eng</language><publisher>United States: John Wiley and Sons, Inc</publisher><subject>Acetaldehyde ; aerobic pathway ; Anaerobic environments ; anaerobic pathway ; Aniline ; Benzoic acid ; Biodegradation ; Biodegradation, Environmental ; Carbon dioxide ; Cleavage ; Cold Temperature ; cold‐resistant strain ; Decomposition ; Degradation ; degradation mechanism ; Fluvial sediments ; Glycogens ; Inoculation ; Low temperature resistance ; Methylobacillus - metabolism ; Microorganisms ; Nitrobenzene ; Nitrobenzenes - metabolism ; Nitrogen dioxide ; Nitrophenol ; o-Nitrophenol ; Organic chemicals ; Pyruvic acid ; Rivers ; Rivers - microbiology ; Sediments ; Succinic acid ; Toxicity</subject><ispartof>Water environment research, 2017-11, Vol.89 (11), p.1970-1980</ispartof><rights>2017 Water Environment Federation</rights><rights>Copyright Water Environment Federation Nov 1, 2017</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4070-ff8a8927c4b6791604e08631edf8a2c41861be28ebfde50d9eaedae32ee54f2b3</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/26662160$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/26662160$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,780,784,27924,27925,58238,58471</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/29080565$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Qiu, Liping</creatorcontrib><creatorcontrib>Wang, Hu</creatorcontrib><creatorcontrib>Wang, Xuntao</creatorcontrib><title>Screening and Degradation Mechanism of a Cold-Resistant Nitrobenzene-Degrading Microorganism</title><title>Water environment research</title><addtitle>Water Environ Res</addtitle><description>A cold-resistant nitrobenzene-degrading strain was screened from river sediment. The strain was identified as Methylobacillus glycogens, which has never been reported to be capable of degrading nitrobenzene. The degradation rates of 900 μg/L nitrobenzene reached respectively 99.3% and 88.6% in 144 h under both aerobic and anaerobic environments (30 mL inoculation volume at 12 ± 0.5 °C and pH7.0 ± 0.1). When aerobically degraded, nitrobenzene was firstly oxidized into o-nitrophenol, which was further oxidized into 1,2-benzenediol, meanwhile releasing NO2-. Then the 1,2-benzenediol was metabolized through either the ortho-cleavage into succinic acid and acetyl-CoA, or meta-cleavage into pyruvic acid and acetaldehyde, as well as other small molecule substances of non-toxicity or low-toxicity, which were finally decomposed into CO₂ and H₂O. When anaerobically degraded, nitrobenzene was firstly degraded into aniline (C₆H₅NH₂), which was further degraded into 4-amino benzoic acid. The benzoic acid was degraded into benzoyl, which was finally metabolized and decomposed.</description><subject>Acetaldehyde</subject><subject>aerobic pathway</subject><subject>Anaerobic environments</subject><subject>anaerobic pathway</subject><subject>Aniline</subject><subject>Benzoic acid</subject><subject>Biodegradation</subject><subject>Biodegradation, Environmental</subject><subject>Carbon dioxide</subject><subject>Cleavage</subject><subject>Cold Temperature</subject><subject>cold‐resistant strain</subject><subject>Decomposition</subject><subject>Degradation</subject><subject>degradation mechanism</subject><subject>Fluvial sediments</subject><subject>Glycogens</subject><subject>Inoculation</subject><subject>Low temperature resistance</subject><subject>Methylobacillus - metabolism</subject><subject>Microorganisms</subject><subject>Nitrobenzene</subject><subject>Nitrobenzenes - metabolism</subject><subject>Nitrogen dioxide</subject><subject>Nitrophenol</subject><subject>o-Nitrophenol</subject><subject>Organic chemicals</subject><subject>Pyruvic acid</subject><subject>Rivers</subject><subject>Rivers - microbiology</subject><subject>Sediments</subject><subject>Succinic acid</subject><subject>Toxicity</subject><issn>1061-4303</issn><issn>1554-7531</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2017</creationdate><recordtype>article</recordtype><recordid>eNp1kFtLw0AQhRdRbK3-BCXgc3Rns7c8-CC1XqBVqIo-CGGTTGpKu1s3KVJ_vVvr5cmnGTjfOcMcQiKgJwyUOAUqgScU1DMIKoBLkYJOhd4iXRCCx0oksB32gMWBSzpkr2mmlAJjlO-SDkuppkKKLnm5Lzyire0kMraMLnDiTWna2tlohMWrsXUzj1wVmajvZmU8xqZuWmPb6LZuvcvRfqDFeGNbh4zqwjvnJ1_GfbJTmVmDB9-zRx4vBw_963h4d3XTPx_GBaeKxlWljU6ZKnguVQqScqRaJoBlEFjBQUvIkWnMqxIFLVM0WBpMGKLgFcuTHjne5C68e1ti02ZTt_Q2nMwg1VzJkKACdfRNLfM5ltnC13PjV9lPGQE42wDv9QxXvzrQbF169l_p2dNgDKmiwX-48U-b1vm_fCklC18ln-lffhk</recordid><startdate>201711</startdate><enddate>201711</enddate><creator>Qiu, Liping</creator><creator>Wang, Hu</creator><creator>Wang, Xuntao</creator><general>John Wiley and Sons, Inc</general><general>Water Environment Federation</general><general>Blackwell Publishing Ltd</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>7QH</scope><scope>7QO</scope><scope>7ST</scope><scope>7T7</scope><scope>7U7</scope><scope>7UA</scope><scope>8FD</scope><scope>C1K</scope><scope>F1W</scope><scope>FR3</scope><scope>H97</scope><scope>K9.</scope><scope>L.G</scope><scope>M7N</scope><scope>P64</scope><scope>SOI</scope></search><sort><creationdate>201711</creationdate><title>Screening and Degradation Mechanism of a Cold-Resistant Nitrobenzene-Degrading Microorganism</title><author>Qiu, Liping ; Wang, Hu ; Wang, Xuntao</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4070-ff8a8927c4b6791604e08631edf8a2c41861be28ebfde50d9eaedae32ee54f2b3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2017</creationdate><topic>Acetaldehyde</topic><topic>aerobic pathway</topic><topic>Anaerobic environments</topic><topic>anaerobic pathway</topic><topic>Aniline</topic><topic>Benzoic acid</topic><topic>Biodegradation</topic><topic>Biodegradation, Environmental</topic><topic>Carbon dioxide</topic><topic>Cleavage</topic><topic>Cold Temperature</topic><topic>cold‐resistant strain</topic><topic>Decomposition</topic><topic>Degradation</topic><topic>degradation mechanism</topic><topic>Fluvial sediments</topic><topic>Glycogens</topic><topic>Inoculation</topic><topic>Low temperature resistance</topic><topic>Methylobacillus - metabolism</topic><topic>Microorganisms</topic><topic>Nitrobenzene</topic><topic>Nitrobenzenes - metabolism</topic><topic>Nitrogen dioxide</topic><topic>Nitrophenol</topic><topic>o-Nitrophenol</topic><topic>Organic chemicals</topic><topic>Pyruvic acid</topic><topic>Rivers</topic><topic>Rivers - microbiology</topic><topic>Sediments</topic><topic>Succinic acid</topic><topic>Toxicity</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Qiu, Liping</creatorcontrib><creatorcontrib>Wang, Hu</creatorcontrib><creatorcontrib>Wang, Xuntao</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>Aqualine</collection><collection>Biotechnology Research Abstracts</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Toxicology Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Engineering Research Database</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>ProQuest Health & Medical Complete (Alumni)</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Algology Mycology and Protozoology Abstracts (Microbiology C)</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Environment Abstracts</collection><jtitle>Water environment research</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Qiu, Liping</au><au>Wang, Hu</au><au>Wang, Xuntao</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Screening and Degradation Mechanism of a Cold-Resistant Nitrobenzene-Degrading Microorganism</atitle><jtitle>Water environment research</jtitle><addtitle>Water Environ Res</addtitle><date>2017-11</date><risdate>2017</risdate><volume>89</volume><issue>11</issue><spage>1970</spage><epage>1980</epage><pages>1970-1980</pages><issn>1061-4303</issn><eissn>1554-7531</eissn><abstract>A cold-resistant nitrobenzene-degrading strain was screened from river sediment. The strain was identified as Methylobacillus glycogens, which has never been reported to be capable of degrading nitrobenzene. The degradation rates of 900 μg/L nitrobenzene reached respectively 99.3% and 88.6% in 144 h under both aerobic and anaerobic environments (30 mL inoculation volume at 12 ± 0.5 °C and pH7.0 ± 0.1). When aerobically degraded, nitrobenzene was firstly oxidized into o-nitrophenol, which was further oxidized into 1,2-benzenediol, meanwhile releasing NO2-. Then the 1,2-benzenediol was metabolized through either the ortho-cleavage into succinic acid and acetyl-CoA, or meta-cleavage into pyruvic acid and acetaldehyde, as well as other small molecule substances of non-toxicity or low-toxicity, which were finally decomposed into CO₂ and H₂O. When anaerobically degraded, nitrobenzene was firstly degraded into aniline (C₆H₅NH₂), which was further degraded into 4-amino benzoic acid. The benzoic acid was degraded into benzoyl, which was finally metabolized and decomposed.</abstract><cop>United States</cop><pub>John Wiley and Sons, Inc</pub><pmid>29080565</pmid><doi>10.2175/106143017X15051465918958</doi><tpages>11</tpages></addata></record> |
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subjects | Acetaldehyde aerobic pathway Anaerobic environments anaerobic pathway Aniline Benzoic acid Biodegradation Biodegradation, Environmental Carbon dioxide Cleavage Cold Temperature cold‐resistant strain Decomposition Degradation degradation mechanism Fluvial sediments Glycogens Inoculation Low temperature resistance Methylobacillus - metabolism Microorganisms Nitrobenzene Nitrobenzenes - metabolism Nitrogen dioxide Nitrophenol o-Nitrophenol Organic chemicals Pyruvic acid Rivers Rivers - microbiology Sediments Succinic acid Toxicity |
title | Screening and Degradation Mechanism of a Cold-Resistant Nitrobenzene-Degrading Microorganism |
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