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Denitrification and Dissimilatory Nitrate Reduction to Ammonium (DNRA) Activities in Freshwater Sludge and Biofloc from Nile Tilapia Aquaculture Systems
Suspended organic sludge from freshwater and biofloc Nile tilapia systems were examined for the presence of denitrifying and dissimilatory nitrate reduction to ammonium (DNRA) activities under nitrate and sulfide stimulation. Initial nitrate concentrations at 25 and 100 mg NO3--N/L were added to the...
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Published in: | Journal of Water and Environment Technology 2014, Vol.12(4), pp.347-356 |
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creator | CHUTIVISUT, Pokchat PUNGRASMI, Wiboonluk POWTONGSOOK, Sorawit |
description | Suspended organic sludge from freshwater and biofloc Nile tilapia systems were examined for the presence of denitrifying and dissimilatory nitrate reduction to ammonium (DNRA) activities under nitrate and sulfide stimulation. Initial nitrate concentrations at 25 and 100 mg NO3--N/L were added to the freshwater sludge and biofloc samples to simulate low and high nitrate levels that are normally found in aquaculture systems. The results showed that freshwater sludge and biofloc both had denitrifying activity immediately after nitrate addition. However, ammonium accumulated in the biofloc reactors but not in the freshwater reactors, indicating the activity of DNRA in the high C/N biofloc particles. The influence of sulfide on nitrate reduction was also studied by adding different concentrations of sulfide along with 100 mg NO3--N/L. The results showed that elevated sulfide concentrations partially inhibited denitrification in the freshwater sludge and caused nitrite and ammonium accumulation, in which ammonium formation was probably responsible by DNRA activity. In sulfide-added biofloc reactors, ammonium accumulated at the same level as found in the biofloc reactors without sulfide. Therefore, DNRA bacteria residing in the biofloc aquaculture system were more likely to be heterotrophs that did not use sulfide as their electron donor. |
doi_str_mv | 10.2965/jwet.2014.347 |
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Initial nitrate concentrations at 25 and 100 mg NO3--N/L were added to the freshwater sludge and biofloc samples to simulate low and high nitrate levels that are normally found in aquaculture systems. The results showed that freshwater sludge and biofloc both had denitrifying activity immediately after nitrate addition. However, ammonium accumulated in the biofloc reactors but not in the freshwater reactors, indicating the activity of DNRA in the high C/N biofloc particles. The influence of sulfide on nitrate reduction was also studied by adding different concentrations of sulfide along with 100 mg NO3--N/L. The results showed that elevated sulfide concentrations partially inhibited denitrification in the freshwater sludge and caused nitrite and ammonium accumulation, in which ammonium formation was probably responsible by DNRA activity. In sulfide-added biofloc reactors, ammonium accumulated at the same level as found in the biofloc reactors without sulfide. Therefore, DNRA bacteria residing in the biofloc aquaculture system were more likely to be heterotrophs that did not use sulfide as their electron donor.</description><identifier>ISSN: 1348-2165</identifier><identifier>ISSN: 0913-8277</identifier><identifier>EISSN: 1348-2165</identifier><identifier>DOI: 10.2965/jwet.2014.347</identifier><language>eng</language><publisher>Tokyo: Japan Society on Water Environment</publisher><subject>biofloc ; Brackish ; denitrification ; dissimilatory nitrate reduction to ammonium (DNRA) ; freshwater aquaculture sludge ; Nile tilapia ; Oreochromis niloticus ; sulfide</subject><ispartof>Journal of Water and Environment Technology, 2014, Vol.12(4), pp.347-356</ispartof><rights>2014 Japan Society on Water Environment</rights><rights>Copyright Japan Science and Technology Agency 2014</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c3037-d00d513bd26b82c00f564ca74bfe45259522f0741264155d96e99694c47786b43</citedby><cites>FETCH-LOGICAL-c3037-d00d513bd26b82c00f564ca74bfe45259522f0741264155d96e99694c47786b43</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,1876,27901,27902</link.rule.ids></links><search><creatorcontrib>CHUTIVISUT, Pokchat</creatorcontrib><creatorcontrib>PUNGRASMI, Wiboonluk</creatorcontrib><creatorcontrib>POWTONGSOOK, Sorawit</creatorcontrib><title>Denitrification and Dissimilatory Nitrate Reduction to Ammonium (DNRA) Activities in Freshwater Sludge and Biofloc from Nile Tilapia Aquaculture Systems</title><title>Journal of Water and Environment Technology</title><addtitle>J. of Wat. & Envir. Tech.</addtitle><description>Suspended organic sludge from freshwater and biofloc Nile tilapia systems were examined for the presence of denitrifying and dissimilatory nitrate reduction to ammonium (DNRA) activities under nitrate and sulfide stimulation. Initial nitrate concentrations at 25 and 100 mg NO3--N/L were added to the freshwater sludge and biofloc samples to simulate low and high nitrate levels that are normally found in aquaculture systems. The results showed that freshwater sludge and biofloc both had denitrifying activity immediately after nitrate addition. However, ammonium accumulated in the biofloc reactors but not in the freshwater reactors, indicating the activity of DNRA in the high C/N biofloc particles. The influence of sulfide on nitrate reduction was also studied by adding different concentrations of sulfide along with 100 mg NO3--N/L. The results showed that elevated sulfide concentrations partially inhibited denitrification in the freshwater sludge and caused nitrite and ammonium accumulation, in which ammonium formation was probably responsible by DNRA activity. In sulfide-added biofloc reactors, ammonium accumulated at the same level as found in the biofloc reactors without sulfide. Therefore, DNRA bacteria residing in the biofloc aquaculture system were more likely to be heterotrophs that did not use sulfide as their electron donor.</description><subject>biofloc</subject><subject>Brackish</subject><subject>denitrification</subject><subject>dissimilatory nitrate reduction to ammonium (DNRA)</subject><subject>freshwater aquaculture sludge</subject><subject>Nile tilapia</subject><subject>Oreochromis niloticus</subject><subject>sulfide</subject><issn>1348-2165</issn><issn>0913-8277</issn><issn>1348-2165</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2014</creationdate><recordtype>article</recordtype><recordid>eNpdkU1rFEEQhgdRMEaP3hu8xMOs_T0zF2HMmiiECEk8N709NUkvPdOb_kjYf-LPTU9WgnipKnifeqvgraqPBK9oJ8WX7SOkFcWErxhvXlVHhPG2pkSK1__Mb6t3MW4xFg2W8qj6s4bZpmBHa3SyfkZ6HtDaxmgn63TyYY8ui64ToCsYsnlmkkf9NPnZ5gmdrC-v-s-oL8qDTRYisjM6CxDvHstSQNcuD7fwbPvN-tF5g8bgp-LqAN2UGzurUX-ftcku5QDoeh8TTPF99WbULsKHv_24-n32_eb0R33x6_znaX9RG4ZZUw8YD4KwzUDlpqUG41FIbnTDNyNwQUUnKB1xwwmVnAgxdBK6Tnbc8KZp5Yaz4-rk4LsL_j5DTGqy0YBzegafoyJCypYVm6agn_5Dtz6HuXy3UJhR2nZdoeoDZYKPMcCodsFOOuwVwWrJSS05qSUnVXIq_NcDv41J38ILrUOyxsGBJlTxpZSFF8Hc6aBgZk-_I52v</recordid><startdate>20140101</startdate><enddate>20140101</enddate><creator>CHUTIVISUT, Pokchat</creator><creator>PUNGRASMI, Wiboonluk</creator><creator>POWTONGSOOK, Sorawit</creator><general>Japan Society on Water Environment</general><general>Japan Science and Technology Agency</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><scope>H98</scope></search><sort><creationdate>20140101</creationdate><title>Denitrification and Dissimilatory Nitrate Reduction to Ammonium (DNRA) Activities in Freshwater Sludge and Biofloc from Nile Tilapia Aquaculture Systems</title><author>CHUTIVISUT, Pokchat ; PUNGRASMI, Wiboonluk ; POWTONGSOOK, Sorawit</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c3037-d00d513bd26b82c00f564ca74bfe45259522f0741264155d96e99694c47786b43</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2014</creationdate><topic>biofloc</topic><topic>Brackish</topic><topic>denitrification</topic><topic>dissimilatory nitrate reduction to ammonium (DNRA)</topic><topic>freshwater aquaculture sludge</topic><topic>Nile tilapia</topic><topic>Oreochromis niloticus</topic><topic>sulfide</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>CHUTIVISUT, Pokchat</creatorcontrib><creatorcontrib>PUNGRASMI, Wiboonluk</creatorcontrib><creatorcontrib>POWTONGSOOK, Sorawit</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><collection>Aquatic Science & Fisheries Abstracts (ASFA) Aquaculture Abstracts</collection><jtitle>Journal of Water and Environment Technology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>CHUTIVISUT, Pokchat</au><au>PUNGRASMI, Wiboonluk</au><au>POWTONGSOOK, Sorawit</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Denitrification and Dissimilatory Nitrate Reduction to Ammonium (DNRA) Activities in Freshwater Sludge and Biofloc from Nile Tilapia Aquaculture Systems</atitle><jtitle>Journal of Water and Environment Technology</jtitle><addtitle>J. of Wat. & Envir. Tech.</addtitle><date>2014-01-01</date><risdate>2014</risdate><volume>12</volume><issue>4</issue><spage>347</spage><epage>356</epage><pages>347-356</pages><issn>1348-2165</issn><issn>0913-8277</issn><eissn>1348-2165</eissn><abstract>Suspended organic sludge from freshwater and biofloc Nile tilapia systems were examined for the presence of denitrifying and dissimilatory nitrate reduction to ammonium (DNRA) activities under nitrate and sulfide stimulation. Initial nitrate concentrations at 25 and 100 mg NO3--N/L were added to the freshwater sludge and biofloc samples to simulate low and high nitrate levels that are normally found in aquaculture systems. The results showed that freshwater sludge and biofloc both had denitrifying activity immediately after nitrate addition. However, ammonium accumulated in the biofloc reactors but not in the freshwater reactors, indicating the activity of DNRA in the high C/N biofloc particles. The influence of sulfide on nitrate reduction was also studied by adding different concentrations of sulfide along with 100 mg NO3--N/L. The results showed that elevated sulfide concentrations partially inhibited denitrification in the freshwater sludge and caused nitrite and ammonium accumulation, in which ammonium formation was probably responsible by DNRA activity. In sulfide-added biofloc reactors, ammonium accumulated at the same level as found in the biofloc reactors without sulfide. Therefore, DNRA bacteria residing in the biofloc aquaculture system were more likely to be heterotrophs that did not use sulfide as their electron donor.</abstract><cop>Tokyo</cop><pub>Japan Society on Water Environment</pub><doi>10.2965/jwet.2014.347</doi><tpages>10</tpages><oa>free_for_read</oa></addata></record> |
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subjects | biofloc Brackish denitrification dissimilatory nitrate reduction to ammonium (DNRA) freshwater aquaculture sludge Nile tilapia Oreochromis niloticus sulfide |
title | Denitrification and Dissimilatory Nitrate Reduction to Ammonium (DNRA) Activities in Freshwater Sludge and Biofloc from Nile Tilapia Aquaculture Systems |
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