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Effect of operating parameters on molinate biodegradation
The effect of operating conditions during molinate degradation by the defined mixed bacterial culture DC, previously described as able to mineralize molinate, was evaluated in a batch reactor. Parameters such as the rate of molinate degradation, the dissolved organic carbon (DOC) consumption and the...
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Published in: | Water research (Oxford) 2006, Vol.40 (2), p.331-340 |
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creator | Correia, Patrícia Boaventura, Rui A.R. Reis, Maria A.M. Nunes, Olga C. |
description | The effect of operating conditions during molinate degradation by the defined mixed bacterial culture DC, previously described as able to mineralize molinate, was evaluated in a batch reactor. Parameters such as the rate of molinate degradation, the dissolved organic carbon (DOC) consumption and the accumulation of molinate degradation products were monitored along the culture growth. The effect of conditions such as temperature, pH, aeration rate, salinity, and presence of additional carbon and/or nitrogen sources, was tested independently. Degradation of molinate in river water was also evaluated. Culture DC was able to grow and to mineralize molinate at all the conditions assayed. Temperature was the factor with the strongest influence on bacterial growth and molinate mineralization. The lowest and the highest rate values of growth (0.010 and 0.110
h
−1) and of molinate degradation (0.027 and 0.180
g
molinate
g
−1
cell
dry
wt
h
−1) were obtained at 15 and 35
°C, respectively. In cultures with approximately 187
mg
l
−1 of molinate, 2-oxo-molinate was the major molinate degradation product accumulated in the medium, in concentrations below 0.133
mg
l
−1.
Degradation of molinate was also evaluated in a continuous stirred tank reactor (CSTR). Operating the CSTR at a hydraulic retention time (HRT) of 83
h, fed with medium containing molinate concentrations ranging from 1 to 3
mM, culture DC degraded the herbicide with specific degradation rates similar to those obtained in the batch systems. |
doi_str_mv | 10.1016/j.watres.2005.11.016 |
format | article |
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h
−1) and of molinate degradation (0.027 and 0.180
g
molinate
g
−1
cell
dry
wt
h
−1) were obtained at 15 and 35
°C, respectively. In cultures with approximately 187
mg
l
−1 of molinate, 2-oxo-molinate was the major molinate degradation product accumulated in the medium, in concentrations below 0.133
mg
l
−1.
Degradation of molinate was also evaluated in a continuous stirred tank reactor (CSTR). Operating the CSTR at a hydraulic retention time (HRT) of 83
h, fed with medium containing molinate concentrations ranging from 1 to 3
mM, culture DC degraded the herbicide with specific degradation rates similar to those obtained in the batch systems.</description><identifier>ISSN: 0043-1354</identifier><identifier>EISSN: 1879-2448</identifier><identifier>DOI: 10.1016/j.watres.2005.11.016</identifier><identifier>PMID: 16380149</identifier><identifier>CODEN: WATRAG</identifier><language>eng</language><publisher>Oxford: Elsevier Ltd</publisher><subject>2-oxo-molinate ; Applied sciences ; Azepines - metabolism ; bacteria ; Bacteria - growth & development ; biodegradation ; Biodegradation of pollutants ; Biodegradation, Environmental ; Biological and medical sciences ; Biological treatment of waters ; Bioreactors ; Biotechnology ; Carbon - metabolism ; Continental surface waters ; Earth sciences ; Earth, ocean, space ; Engineering and environment geology. Geothermics ; Environment and pollution ; Exact sciences and technology ; Fundamental and applied biological sciences. Psychology ; Herbicide biodegradation ; Herbicides - metabolism ; Hydrogen-Ion Concentration ; Industrial applications and implications. Economical aspects ; Kinetics ; microbial growth ; mineralization ; Molinate ; Natural water pollution ; Pollution ; Pollution, environment geology ; rivers ; Temperature ; Thiocarbamates - metabolism ; water pollution ; water treatment ; Water treatment and pollution ; Xenobiotic</subject><ispartof>Water research (Oxford), 2006, Vol.40 (2), p.331-340</ispartof><rights>2005 Elsevier Ltd</rights><rights>2006 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c445t-73c4439444bf6ed67cc665aa05b9b1b804b256fac15422c4a2604c04c9de61413</citedby><cites>FETCH-LOGICAL-c445t-73c4439444bf6ed67cc665aa05b9b1b804b256fac15422c4a2604c04c9de61413</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,4022,27921,27922,27923</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=17396869$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/16380149$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Correia, Patrícia</creatorcontrib><creatorcontrib>Boaventura, Rui A.R.</creatorcontrib><creatorcontrib>Reis, Maria A.M.</creatorcontrib><creatorcontrib>Nunes, Olga C.</creatorcontrib><title>Effect of operating parameters on molinate biodegradation</title><title>Water research (Oxford)</title><addtitle>Water Res</addtitle><description>The effect of operating conditions during molinate degradation by the defined mixed bacterial culture DC, previously described as able to mineralize molinate, was evaluated in a batch reactor. Parameters such as the rate of molinate degradation, the dissolved organic carbon (DOC) consumption and the accumulation of molinate degradation products were monitored along the culture growth. The effect of conditions such as temperature, pH, aeration rate, salinity, and presence of additional carbon and/or nitrogen sources, was tested independently. Degradation of molinate in river water was also evaluated. Culture DC was able to grow and to mineralize molinate at all the conditions assayed. Temperature was the factor with the strongest influence on bacterial growth and molinate mineralization. The lowest and the highest rate values of growth (0.010 and 0.110
h
−1) and of molinate degradation (0.027 and 0.180
g
molinate
g
−1
cell
dry
wt
h
−1) were obtained at 15 and 35
°C, respectively. In cultures with approximately 187
mg
l
−1 of molinate, 2-oxo-molinate was the major molinate degradation product accumulated in the medium, in concentrations below 0.133
mg
l
−1.
Degradation of molinate was also evaluated in a continuous stirred tank reactor (CSTR). Operating the CSTR at a hydraulic retention time (HRT) of 83
h, fed with medium containing molinate concentrations ranging from 1 to 3
mM, culture DC degraded the herbicide with specific degradation rates similar to those obtained in the batch systems.</description><subject>2-oxo-molinate</subject><subject>Applied sciences</subject><subject>Azepines - metabolism</subject><subject>bacteria</subject><subject>Bacteria - growth & development</subject><subject>biodegradation</subject><subject>Biodegradation of pollutants</subject><subject>Biodegradation, Environmental</subject><subject>Biological and medical sciences</subject><subject>Biological treatment of waters</subject><subject>Bioreactors</subject><subject>Biotechnology</subject><subject>Carbon - metabolism</subject><subject>Continental surface waters</subject><subject>Earth sciences</subject><subject>Earth, ocean, space</subject><subject>Engineering and environment geology. Geothermics</subject><subject>Environment and pollution</subject><subject>Exact sciences and technology</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Herbicide biodegradation</subject><subject>Herbicides - metabolism</subject><subject>Hydrogen-Ion Concentration</subject><subject>Industrial applications and implications. Economical aspects</subject><subject>Kinetics</subject><subject>microbial growth</subject><subject>mineralization</subject><subject>Molinate</subject><subject>Natural water pollution</subject><subject>Pollution</subject><subject>Pollution, environment geology</subject><subject>rivers</subject><subject>Temperature</subject><subject>Thiocarbamates - metabolism</subject><subject>water pollution</subject><subject>water treatment</subject><subject>Water treatment and pollution</subject><subject>Xenobiotic</subject><issn>0043-1354</issn><issn>1879-2448</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2006</creationdate><recordtype>article</recordtype><recordid>eNp90VGL1DAQB_AgireefgPRvuhbayZJ0-ZFkOO8Ew580HsO03SyZGmbNekqfnuzdOHehMDA8Jsh-Yext8Ab4KA_HZo_uCbKjeC8bQCa0nzGdtB3phZK9c_ZjnMla5CtumKvcj5wzoWQ5iW7Ai17DsrsmLn1ntxaRV_FIyVcw7KvjphwppVSruJSzXEKC65UDSGOtE84FhWX1-yFxynTm0u9Zo9fb3_e3NcP3---3Xx5qJ1S7Vp3slRplFKD1zTqzjmtW0TeDmaAoedqEK326KBVQjiFQnPlyjEjaVAgr9nHbe8xxV8nyqudQ3Y0TbhQPGULRknd9rJAtUGXYs6JvD2mMGP6a4Hbc2T2YLfI7DkyC2BLs4y9u-w_DTONT0OXjAr4cAGYHU4-4eJCfnKdNLrXZ_d-cx6jxX0q5vGH4CA58PIS0xXxeRNU8vodKNnsAi2OxpDKJ9gxhv_f9R_1L5Qa</recordid><startdate>2006</startdate><enddate>2006</enddate><creator>Correia, Patrícia</creator><creator>Boaventura, Rui A.R.</creator><creator>Reis, Maria A.M.</creator><creator>Nunes, Olga C.</creator><general>Elsevier Ltd</general><general>Elsevier Science</general><scope>FBQ</scope><scope>IQODW</scope><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>7QH</scope><scope>7QL</scope><scope>7QO</scope><scope>7T7</scope><scope>7TV</scope><scope>7UA</scope><scope>8FD</scope><scope>C1K</scope><scope>F1W</scope><scope>FR3</scope><scope>H96</scope><scope>L.G</scope><scope>P64</scope></search><sort><creationdate>2006</creationdate><title>Effect of operating parameters on molinate biodegradation</title><author>Correia, Patrícia ; Boaventura, Rui A.R. ; Reis, Maria A.M. ; Nunes, Olga C.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c445t-73c4439444bf6ed67cc665aa05b9b1b804b256fac15422c4a2604c04c9de61413</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2006</creationdate><topic>2-oxo-molinate</topic><topic>Applied sciences</topic><topic>Azepines - metabolism</topic><topic>bacteria</topic><topic>Bacteria - growth & development</topic><topic>biodegradation</topic><topic>Biodegradation of pollutants</topic><topic>Biodegradation, Environmental</topic><topic>Biological and medical sciences</topic><topic>Biological treatment of waters</topic><topic>Bioreactors</topic><topic>Biotechnology</topic><topic>Carbon - metabolism</topic><topic>Continental surface waters</topic><topic>Earth sciences</topic><topic>Earth, ocean, space</topic><topic>Engineering and environment geology. Geothermics</topic><topic>Environment and pollution</topic><topic>Exact sciences and technology</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Herbicide biodegradation</topic><topic>Herbicides - metabolism</topic><topic>Hydrogen-Ion Concentration</topic><topic>Industrial applications and implications. Economical aspects</topic><topic>Kinetics</topic><topic>microbial growth</topic><topic>mineralization</topic><topic>Molinate</topic><topic>Natural water pollution</topic><topic>Pollution</topic><topic>Pollution, environment geology</topic><topic>rivers</topic><topic>Temperature</topic><topic>Thiocarbamates - metabolism</topic><topic>water pollution</topic><topic>water treatment</topic><topic>Water treatment and pollution</topic><topic>Xenobiotic</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Correia, Patrícia</creatorcontrib><creatorcontrib>Boaventura, Rui A.R.</creatorcontrib><creatorcontrib>Reis, Maria A.M.</creatorcontrib><creatorcontrib>Nunes, Olga C.</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Aqualine</collection><collection>Bacteriology Abstracts (Microbiology B)</collection><collection>Biotechnology Research Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Pollution 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) 2: Ocean Technology, Policy & Non-Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Biotechnology and BioEngineering Abstracts</collection><jtitle>Water research (Oxford)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Correia, Patrícia</au><au>Boaventura, Rui A.R.</au><au>Reis, Maria A.M.</au><au>Nunes, Olga C.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Effect of operating parameters on molinate biodegradation</atitle><jtitle>Water research (Oxford)</jtitle><addtitle>Water Res</addtitle><date>2006</date><risdate>2006</risdate><volume>40</volume><issue>2</issue><spage>331</spage><epage>340</epage><pages>331-340</pages><issn>0043-1354</issn><eissn>1879-2448</eissn><coden>WATRAG</coden><abstract>The effect of operating conditions during molinate degradation by the defined mixed bacterial culture DC, previously described as able to mineralize molinate, was evaluated in a batch reactor. Parameters such as the rate of molinate degradation, the dissolved organic carbon (DOC) consumption and the accumulation of molinate degradation products were monitored along the culture growth. The effect of conditions such as temperature, pH, aeration rate, salinity, and presence of additional carbon and/or nitrogen sources, was tested independently. Degradation of molinate in river water was also evaluated. Culture DC was able to grow and to mineralize molinate at all the conditions assayed. Temperature was the factor with the strongest influence on bacterial growth and molinate mineralization. The lowest and the highest rate values of growth (0.010 and 0.110
h
−1) and of molinate degradation (0.027 and 0.180
g
molinate
g
−1
cell
dry
wt
h
−1) were obtained at 15 and 35
°C, respectively. In cultures with approximately 187
mg
l
−1 of molinate, 2-oxo-molinate was the major molinate degradation product accumulated in the medium, in concentrations below 0.133
mg
l
−1.
Degradation of molinate was also evaluated in a continuous stirred tank reactor (CSTR). Operating the CSTR at a hydraulic retention time (HRT) of 83
h, fed with medium containing molinate concentrations ranging from 1 to 3
mM, culture DC degraded the herbicide with specific degradation rates similar to those obtained in the batch systems.</abstract><cop>Oxford</cop><pub>Elsevier Ltd</pub><pmid>16380149</pmid><doi>10.1016/j.watres.2005.11.016</doi><tpages>10</tpages></addata></record> |
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subjects | 2-oxo-molinate Applied sciences Azepines - metabolism bacteria Bacteria - growth & development biodegradation Biodegradation of pollutants Biodegradation, Environmental Biological and medical sciences Biological treatment of waters Bioreactors Biotechnology Carbon - metabolism Continental surface waters Earth sciences Earth, ocean, space Engineering and environment geology. Geothermics Environment and pollution Exact sciences and technology Fundamental and applied biological sciences. Psychology Herbicide biodegradation Herbicides - metabolism Hydrogen-Ion Concentration Industrial applications and implications. Economical aspects Kinetics microbial growth mineralization Molinate Natural water pollution Pollution Pollution, environment geology rivers Temperature Thiocarbamates - metabolism water pollution water treatment Water treatment and pollution Xenobiotic |
title | Effect of operating parameters on molinate biodegradation |
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