Impact of Microaeration and the Redox Mediator Anthraquinone‐2,6‐Disulfonate on Azo Dye Reduction and By‐Products Degradation
This work assessed the impact of microaeration and the redox mediator anthraquinone‐2,6‐disulfonate (AQDS) on both azo dye reduction and by‐products degradation (aromatic amines) in a mesophilic reactor. The experiment was carried out in an up‐flow anaerobic sludge blanket (UASB) reactor with 3.2 L...
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description | This work assessed the impact of microaeration and the redox mediator anthraquinone‐2,6‐disulfonate (AQDS) on both azo dye reduction and by‐products degradation (aromatic amines) in a mesophilic reactor. The experiment was carried out in an up‐flow anaerobic sludge blanket (UASB) reactor with 3.2 L of working volume and hydraulic retention time (HRT) of 24 h. The synthetic effluent contained 50 mg L−1 of the dye Reactive Red 2 (RR2). The reactor was initially operated under anaerobic conditions and, subsequently, was microaerated with atmospheric air (1 mL min−1) and then supplemented with the redox mediator (AQDS) at a concentration of 25 μM. The microaeration effect on dye reduction and by‐products formed was not evident. However, AQDS considerably enhanced RR2 reduction, and its regeneration is not affected by the presence of oxygen. It seems that the cleavage of the double bond between nitrogen groups is a much easier way to start the attack of the azo dye, and it is independent of the presence of oxygen. Thus, the introduction of hydroxyl groups into the aromatic ring was not playing a role in the color removal process. In terms of ecological parameters, the ecological niches were maintained, and the distribution of species increased, despite the majority being generalists, i.e., not specialized in dye degradation. Furthermore, anaerobic species are dominant over facultative species, which explains why there was no population diversity recovery after the microaeration started.
Anaerobic mineralization of azo dyes is hindered due to both electron transfer limitation and aromatic amines (AA) recalcitrance. Hence, this work assesses the association of anthraquinone‐2,6‐disulfonate (AQDS) addition for enhancing electron transfer for RR2 reduction and microaeration for AA removal. Although the microaeration effect is not evident on AA removal, AQDS significantly improves RR2 reduction under anaerobic and microaerobic conditions. |
doi_str_mv | 10.1002/clen.201700518 |
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Anaerobic mineralization of azo dyes is hindered due to both electron transfer limitation and aromatic amines (AA) recalcitrance. Hence, this work assesses the association of anthraquinone‐2,6‐disulfonate (AQDS) addition for enhancing electron transfer for RR2 reduction and microaeration for AA removal. Although the microaeration effect is not evident on AA removal, AQDS significantly improves RR2 reduction under anaerobic and microaerobic conditions.</description><identifier>ISSN: 1863-0650</identifier><identifier>EISSN: 1863-0669</identifier><identifier>DOI: 10.1002/clen.201700518</identifier><language>eng</language><publisher>Weinheim: Wiley Subscription Services, Inc</publisher><subject>Amines ; Anaerobic conditions ; anaerobic treatment ; Anoxic conditions ; Anthraquinone ; AQDS ; aromatic amines mineralization ; Aromatic compounds ; Azo dyes ; Biodiversity ; Color removal ; Colour ; Degradation ; Dyes ; Ecological distribution ; Ecological niches ; Hydraulic retention time ; Hydroxyl groups ; microaerobic system ; Niches ; Oxidoreductions ; Oxygen ; Products ; Reactors ; Reduction ; Regeneration ; Regeneration (biological) ; Removal ; Retention time ; Sludge ; Species ; Upflow anaerobic sludge blanket reactors</subject><ispartof>Clean : soil, air, water, 2018-08, Vol.46 (8), p.n/a</ispartof><rights>2018 WILEY-VCH Verlag GmbH & Co. KGaA, Weinheim</rights><rights>2018 WILEY‐VCH Verlag GmbH & Co. KGaA, Weinheim</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c3548-d2a8cc28838abd5ae053c3455cb65bc19ab689397074f2103065051b787e2b743</citedby><cites>FETCH-LOGICAL-c3548-d2a8cc28838abd5ae053c3455cb65bc19ab689397074f2103065051b787e2b743</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://onlinelibrary.wiley.com/doi/pdf/10.1002%2Fclen.201700518$$EPDF$$P50$$Gwiley$$H</linktopdf><linktohtml>$$Uhttps://onlinelibrary.wiley.com/doi/full/10.1002%2Fclen.201700518$$EHTML$$P50$$Gwiley$$H</linktohtml><link.rule.ids>314,776,780,1411,27901,27902,45550,45551</link.rule.ids></links><search><creatorcontrib>de Barros, Amanda N.</creatorcontrib><creatorcontrib>da Silva, Marcos E. R.</creatorcontrib><creatorcontrib>Firmino, Paulo I. M.</creatorcontrib><creatorcontrib>de Vasconcelos, Eduardo A. F.</creatorcontrib><creatorcontrib>dos Santos, André B.</creatorcontrib><title>Impact of Microaeration and the Redox Mediator Anthraquinone‐2,6‐Disulfonate on Azo Dye Reduction and By‐Products Degradation</title><title>Clean : soil, air, water</title><description>This work assessed the impact of microaeration and the redox mediator anthraquinone‐2,6‐disulfonate (AQDS) on both azo dye reduction and by‐products degradation (aromatic amines) in a mesophilic reactor. The experiment was carried out in an up‐flow anaerobic sludge blanket (UASB) reactor with 3.2 L of working volume and hydraulic retention time (HRT) of 24 h. The synthetic effluent contained 50 mg L−1 of the dye Reactive Red 2 (RR2). The reactor was initially operated under anaerobic conditions and, subsequently, was microaerated with atmospheric air (1 mL min−1) and then supplemented with the redox mediator (AQDS) at a concentration of 25 μM. The microaeration effect on dye reduction and by‐products formed was not evident. However, AQDS considerably enhanced RR2 reduction, and its regeneration is not affected by the presence of oxygen. It seems that the cleavage of the double bond between nitrogen groups is a much easier way to start the attack of the azo dye, and it is independent of the presence of oxygen. Thus, the introduction of hydroxyl groups into the aromatic ring was not playing a role in the color removal process. In terms of ecological parameters, the ecological niches were maintained, and the distribution of species increased, despite the majority being generalists, i.e., not specialized in dye degradation. Furthermore, anaerobic species are dominant over facultative species, which explains why there was no population diversity recovery after the microaeration started.
Anaerobic mineralization of azo dyes is hindered due to both electron transfer limitation and aromatic amines (AA) recalcitrance. Hence, this work assesses the association of anthraquinone‐2,6‐disulfonate (AQDS) addition for enhancing electron transfer for RR2 reduction and microaeration for AA removal. Although the microaeration effect is not evident on AA removal, AQDS significantly improves RR2 reduction under anaerobic and microaerobic conditions.</description><subject>Amines</subject><subject>Anaerobic conditions</subject><subject>anaerobic treatment</subject><subject>Anoxic conditions</subject><subject>Anthraquinone</subject><subject>AQDS</subject><subject>aromatic amines mineralization</subject><subject>Aromatic compounds</subject><subject>Azo dyes</subject><subject>Biodiversity</subject><subject>Color removal</subject><subject>Colour</subject><subject>Degradation</subject><subject>Dyes</subject><subject>Ecological distribution</subject><subject>Ecological niches</subject><subject>Hydraulic retention time</subject><subject>Hydroxyl groups</subject><subject>microaerobic system</subject><subject>Niches</subject><subject>Oxidoreductions</subject><subject>Oxygen</subject><subject>Products</subject><subject>Reactors</subject><subject>Reduction</subject><subject>Regeneration</subject><subject>Regeneration (biological)</subject><subject>Removal</subject><subject>Retention time</subject><subject>Sludge</subject><subject>Species</subject><subject>Upflow anaerobic sludge blanket reactors</subject><issn>1863-0650</issn><issn>1863-0669</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2018</creationdate><recordtype>article</recordtype><recordid>eNqFkLFOwzAQhi0EEqWwMltiJeVsx4kzlrZApRYQgtlyHIemSuPiJIIwIfECPCNPQtKiMrLcnU7_d7_uR-iUwIAA0Audm2JAgYQAnIg91CMiYB4EQbS_mzkcoqOyXAIEQALSQ5_T1VrpCtsUzzPtrDJOVZktsCoSXC0MfjCJfcNzk2Sqsg4Pi2rh1EudFbYw3x9f9Dxo6zgr6zy1haoMbtnhu8XjZsPWenftsmmV9852uxKPzbNTycbrGB2kKi_NyW_vo6eryePoxpvdXU9Hw5mnGfeFl1AltKZCMKHihCsDnGnmc67jgMeaRCoORMSiEEI_pQRY9y4ncShCQ-PQZ310tr27dvalNmUll7Z2RWspKYgwAsZp1KoGW1WbRlk6k8q1y1bKNZKA7IKWXdByF3QLRFvgNctN849ajmaT2z_2ByUHhQQ</recordid><startdate>201808</startdate><enddate>201808</enddate><creator>de Barros, Amanda N.</creator><creator>da Silva, Marcos E. R.</creator><creator>Firmino, Paulo I. M.</creator><creator>de Vasconcelos, Eduardo A. F.</creator><creator>dos Santos, André B.</creator><general>Wiley Subscription Services, Inc</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7QH</scope><scope>7ST</scope><scope>7UA</scope><scope>C1K</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope><scope>SOI</scope></search><sort><creationdate>201808</creationdate><title>Impact of Microaeration and the Redox Mediator Anthraquinone‐2,6‐Disulfonate on Azo Dye Reduction and By‐Products Degradation</title><author>de Barros, Amanda N. ; da Silva, Marcos E. R. ; Firmino, Paulo I. M. ; de Vasconcelos, Eduardo A. F. ; dos Santos, André B.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c3548-d2a8cc28838abd5ae053c3455cb65bc19ab689397074f2103065051b787e2b743</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2018</creationdate><topic>Amines</topic><topic>Anaerobic conditions</topic><topic>anaerobic treatment</topic><topic>Anoxic conditions</topic><topic>Anthraquinone</topic><topic>AQDS</topic><topic>aromatic amines mineralization</topic><topic>Aromatic compounds</topic><topic>Azo dyes</topic><topic>Biodiversity</topic><topic>Color removal</topic><topic>Colour</topic><topic>Degradation</topic><topic>Dyes</topic><topic>Ecological distribution</topic><topic>Ecological niches</topic><topic>Hydraulic retention time</topic><topic>Hydroxyl groups</topic><topic>microaerobic system</topic><topic>Niches</topic><topic>Oxidoreductions</topic><topic>Oxygen</topic><topic>Products</topic><topic>Reactors</topic><topic>Reduction</topic><topic>Regeneration</topic><topic>Regeneration (biological)</topic><topic>Removal</topic><topic>Retention time</topic><topic>Sludge</topic><topic>Species</topic><topic>Upflow anaerobic sludge blanket reactors</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>de Barros, Amanda N.</creatorcontrib><creatorcontrib>da Silva, Marcos E. R.</creatorcontrib><creatorcontrib>Firmino, Paulo I. M.</creatorcontrib><creatorcontrib>de Vasconcelos, Eduardo A. F.</creatorcontrib><creatorcontrib>dos Santos, André B.</creatorcontrib><collection>CrossRef</collection><collection>Aqualine</collection><collection>Environment 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>Environment Abstracts</collection><jtitle>Clean : soil, air, water</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>de Barros, Amanda N.</au><au>da Silva, Marcos E. R.</au><au>Firmino, Paulo I. M.</au><au>de Vasconcelos, Eduardo A. F.</au><au>dos Santos, André B.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Impact of Microaeration and the Redox Mediator Anthraquinone‐2,6‐Disulfonate on Azo Dye Reduction and By‐Products Degradation</atitle><jtitle>Clean : soil, air, water</jtitle><date>2018-08</date><risdate>2018</risdate><volume>46</volume><issue>8</issue><epage>n/a</epage><issn>1863-0650</issn><eissn>1863-0669</eissn><abstract>This work assessed the impact of microaeration and the redox mediator anthraquinone‐2,6‐disulfonate (AQDS) on both azo dye reduction and by‐products degradation (aromatic amines) in a mesophilic reactor. The experiment was carried out in an up‐flow anaerobic sludge blanket (UASB) reactor with 3.2 L of working volume and hydraulic retention time (HRT) of 24 h. The synthetic effluent contained 50 mg L−1 of the dye Reactive Red 2 (RR2). The reactor was initially operated under anaerobic conditions and, subsequently, was microaerated with atmospheric air (1 mL min−1) and then supplemented with the redox mediator (AQDS) at a concentration of 25 μM. The microaeration effect on dye reduction and by‐products formed was not evident. However, AQDS considerably enhanced RR2 reduction, and its regeneration is not affected by the presence of oxygen. It seems that the cleavage of the double bond between nitrogen groups is a much easier way to start the attack of the azo dye, and it is independent of the presence of oxygen. Thus, the introduction of hydroxyl groups into the aromatic ring was not playing a role in the color removal process. In terms of ecological parameters, the ecological niches were maintained, and the distribution of species increased, despite the majority being generalists, i.e., not specialized in dye degradation. Furthermore, anaerobic species are dominant over facultative species, which explains why there was no population diversity recovery after the microaeration started.
Anaerobic mineralization of azo dyes is hindered due to both electron transfer limitation and aromatic amines (AA) recalcitrance. Hence, this work assesses the association of anthraquinone‐2,6‐disulfonate (AQDS) addition for enhancing electron transfer for RR2 reduction and microaeration for AA removal. Although the microaeration effect is not evident on AA removal, AQDS significantly improves RR2 reduction under anaerobic and microaerobic conditions.</abstract><cop>Weinheim</cop><pub>Wiley Subscription Services, Inc</pub><doi>10.1002/clen.201700518</doi><tpages>9</tpages></addata></record> |
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subjects | Amines Anaerobic conditions anaerobic treatment Anoxic conditions Anthraquinone AQDS aromatic amines mineralization Aromatic compounds Azo dyes Biodiversity Color removal Colour Degradation Dyes Ecological distribution Ecological niches Hydraulic retention time Hydroxyl groups microaerobic system Niches Oxidoreductions Oxygen Products Reactors Reduction Regeneration Regeneration (biological) Removal Retention time Sludge Species Upflow anaerobic sludge blanket reactors |
title | Impact of Microaeration and the Redox Mediator Anthraquinone‐2,6‐Disulfonate on Azo Dye Reduction and By‐Products Degradation |
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