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DC Field | Value | Language |
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dc.contributor.author | Boonnorat J. | |
dc.contributor.author | Techkarnjanaruk S. | |
dc.contributor.author | Honda R. | |
dc.contributor.author | Prachanurak P. | |
dc.date.accessioned | 2021-04-05T03:23:26Z | - |
dc.date.available | 2021-04-05T03:23:26Z | - |
dc.date.issued | 2016 | |
dc.identifier.issn | 9608524 | |
dc.identifier.other | 2-s2.0-84979774564 | |
dc.identifier.uri | https://ir.swu.ac.th/jspui/handle/123456789/13350 | - |
dc.identifier.uri | https://www.scopus.com/inward/record.uri?eid=2-s2.0-84979774564&doi=10.1016%2fj.biortech.2016.07.094&partnerID=40&md5=7518d7228abf73bbf73c1bdd1cc68fb5 | |
dc.description.abstract | This research investigated the biodegradation of the micro-pollutants in leachate by the membrane bioreactor (MBR) system under six treatment conditions, comprising two C/N ratios (6, 10) and three hydraulic retention time (HRT) durations (6, 12, 24 h). The experimental results indicated that the C/N 6 environment was more advantageous to the bacterial growth. The bacterial communities residing in the sludge were those of heterotrophic bacteria (HB), heterotrophic nitrifying bacteria (HNB) and ammonia oxidizing bacteria (AOB). It was found that HB and HNB produced phenol hydroxylase (PH), esterase (EST), phthalate dioxygenase (PDO) and laccase (LAC) and also enhanced the biodegradation rate constants (k) in the system. At the same time, AOB promoted the production of HB and HNB. The findings also revealed that the 12 h HRT was the optimal condition with regard to the highest growth of the bacteria responsible for the biodegradation of phenols and phthalates. Meanwhile, the longer HRT duration (i.e. 24 h) was required to effectively bio-degrade carbamazepine (CBZ), N,N-diethyl-m-toluamide (DEET) and diclofenac (DCF). © 2016 Elsevier Ltd | |
dc.subject | Bacteria | |
dc.subject | Bioconversion | |
dc.subject | Bioreactors | |
dc.subject | Carbon | |
dc.subject | Enzyme activity | |
dc.subject | Enzymes | |
dc.subject | Esters | |
dc.subject | Leachate treatment | |
dc.subject | Nitrification | |
dc.subject | Phenols | |
dc.subject | Pollution | |
dc.subject | Potassium compounds | |
dc.subject | Rate constants | |
dc.subject | C/N ratio | |
dc.subject | Hydraulic retention time | |
dc.subject | Leachates | |
dc.subject | Membrane bio reactor (MBR) | |
dc.subject | Micropollutants | |
dc.subject | Biodegradation | |
dc.subject | 2,6 di tert butylphenol | |
dc.subject | 4,4' isopropylidenediphenol | |
dc.subject | carbamazepine | |
dc.subject | carbon | |
dc.subject | diclofenac | |
dc.subject | diethyltoluamide | |
dc.subject | dioxygenase | |
dc.subject | endocrine disruptor | |
dc.subject | esterase | |
dc.subject | laccase | |
dc.subject | nitrogen | |
dc.subject | oxygenase | |
dc.subject | pesticide | |
dc.subject | phenol derivative | |
dc.subject | phenol hydroxylase | |
dc.subject | phthalate dioxygenase | |
dc.subject | phthalic acid | |
dc.subject | unclassified drug | |
dc.subject | artificial membrane | |
dc.subject | carbon | |
dc.subject | nitrogen | |
dc.subject | sewage | |
dc.subject | water pollutant | |
dc.subject | bacterium | |
dc.subject | biodegradation | |
dc.subject | bioreactor | |
dc.subject | carbon isotope | |
dc.subject | enzyme activity | |
dc.subject | experimental study | |
dc.subject | growth rate | |
dc.subject | isotopic ratio | |
dc.subject | leachate | |
dc.subject | microbial activity | |
dc.subject | nitrogen isotope | |
dc.subject | pollutant | |
dc.subject | waste treatment | |
dc.subject | water retention | |
dc.subject | ammonia oxidizing bacterium | |
dc.subject | Article | |
dc.subject | biodegradation | |
dc.subject | hydraulic retention time | |
dc.subject | leaching | |
dc.subject | membrane reactor | |
dc.subject | microbial community | |
dc.subject | nitrifying bacterium | |
dc.subject | nonhuman | |
dc.subject | pollutant | |
dc.subject | priority journal | |
dc.subject | sludge | |
dc.subject | time | |
dc.subject | artificial membrane | |
dc.subject | bacterium | |
dc.subject | bioreactor | |
dc.subject | bioremediation | |
dc.subject | denaturing gradient gel electrophoresis | |
dc.subject | heterotrophy | |
dc.subject | isolation and purification | |
dc.subject | kinetics | |
dc.subject | metabolism | |
dc.subject | microbiology | |
dc.subject | nitrification | |
dc.subject | polyacrylamide gel electrophoresis | |
dc.subject | polymerase chain reaction | |
dc.subject | real time polymerase chain reaction | |
dc.subject | sewage | |
dc.subject | time factor | |
dc.subject | water pollutant | |
dc.subject | Bacteria (microorganisms) | |
dc.subject | Nitrosomonadales | |
dc.subject | Bacteria | |
dc.subject | Biodegradation, Environmental | |
dc.subject | Bioreactors | |
dc.subject | Carbon | |
dc.subject | Denaturing Gradient Gel Electrophoresis | |
dc.subject | Electrophoresis, Polyacrylamide Gel | |
dc.subject | Heterotrophic Processes | |
dc.subject | Kinetics | |
dc.subject | Membranes, Artificial | |
dc.subject | Nitrification | |
dc.subject | Nitrogen | |
dc.subject | Polymerase Chain Reaction | |
dc.subject | Real-Time Polymerase Chain Reaction | |
dc.subject | Sewage | |
dc.subject | Time Factors | |
dc.subject | Water Pollutants, Chemical | |
dc.title | Effects of hydraulic retention time and carbon to nitrogen ratio on micro-pollutant biodegradation in membrane bioreactor for leachate treatment | |
dc.type | Article | |
dc.rights.holder | Scopus | |
dc.identifier.bibliograpycitation | Bioresource Technology. Vol 219, (2016), p.53-63 | |
dc.identifier.doi | 10.1016/j.biortech.2016.07.094 | |
Appears in Collections: | Scopus 1983-2021 |
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