Bioremediation of typical chlorinated hydrocarbons by microbial reductive dechlorination and its key players: A review

2020 ◽  
Vol 202 ◽  
pp. 110925
Author(s):  
Zhixing Xiao ◽  
Wei Jiang ◽  
Dan Chen ◽  
Yan Xu
Chemosphere ◽  
2015 ◽  
Vol 131 ◽  
pp. 110-116 ◽  
Author(s):  
Chunfang Zhang ◽  
Dongdong Zhang ◽  
Zhixing Xiao ◽  
Zhiling Li ◽  
Daisuke Suzuki ◽  
...  

2003 ◽  
Vol 37 (6) ◽  
pp. 1100-1107 ◽  
Author(s):  
Usarat Pakdeesusuk ◽  
W. Jack Jones ◽  
Cindy M. Lee ◽  
Arthur W. Garrison ◽  
Walter L. O'Niell ◽  
...  

Chemosphere ◽  
2021 ◽  
Vol 267 ◽  
pp. 129152
Author(s):  
Rui Shen ◽  
Ling Yu ◽  
Pan Xu ◽  
Zhiwei Liang ◽  
Qihong Lu ◽  
...  

2019 ◽  
Vol 162 ◽  
pp. 236-245 ◽  
Author(s):  
Xiao-Qiu Lin ◽  
Zhi-Ling Li ◽  
Bin Liang ◽  
Hong-Liang Zhai ◽  
Wei-Wei Cai ◽  
...  

2002 ◽  
Vol 2 (2) ◽  
pp. 51-58 ◽  
Author(s):  
A. Tiehm ◽  
M. Gozan ◽  
A. Müller ◽  
H. Schell ◽  
H. Lorbeer ◽  
...  

The aim of this study is to develop a long lasting, sequential anaerobic/aerobic biological activated carbon barrier. In the biobarrier, pollutant adsorption on granular activated carbon (GAC) and biodegradation occur simultaneously. Trichloroethene (TCE), chlorobenzene (CB), and benzene were used as model pollutants. In the first barrier, that was operated under anaerobic conditions with sucrose and ethanol as auxiliary substrates, TCE was completely converted to lower chlorinated metabolites, predominantly cis-dichloroethene (cis-DCE). The reductive dechlorination process was stable for about 300 d, although the concomitant sulphate-reducing and methanogenic processes varied considerably. In the second barrier, that was operated with addition of hydrogen peroxide and nitrate, dechlorination was limited by a lack of oxygen and restricted mainly to CB biodegradation. Additional aerobic batch tests revealed that the metabolites of anaerobic TCE dechlorination, i.e. cis-DCE and vinyl chloride, were oxidatively dechlorinated in the presence of suitable auxiliary substrates such as ethene, CB, benzene, or sucrose and ethanol. During periods of low biological activity, elimination of TCE and CB occurred by adsorption in the GAC barriers. The pre-sorbed pollutants were available for subsequent biodegradation resulting in a bioregeneration of the activated carbon barriers.


2014 ◽  
Vol 164 ◽  
pp. 232-240 ◽  
Author(s):  
Dongdong Zhang ◽  
Chunfang Zhang ◽  
Zhiling Li ◽  
Daisuke Suzuki ◽  
Daisuke D. Komatsu ◽  
...  

2007 ◽  
Vol 41 (7) ◽  
pp. 2554-2559 ◽  
Author(s):  
Federico Aulenta ◽  
Alessandro Catervi ◽  
Mauro Majone ◽  
Stefania Panero ◽  
Priscilla Reale ◽  
...  

2005 ◽  
Vol 52 (1-2) ◽  
pp. 343-349 ◽  
Author(s):  
D.H. Yeh ◽  
S.G. Pavlostathis

Three structurally-related, nonionic, polysorbate surfactants (Tween 60, 61, and 65) were used as the sole carbon source to sustain the microbial, sequential reductive dechlorination of hexachlorobenzene (HCB) in a mixed, methanogenic culture derived from a contaminated estuarine sediment. The surfactants were partially degraded and fermented to methane with no measurable accumulation of volatile fatty acids, indicating that methanogenesis was rapid relative to the rates of hydrolysis and acidogenesis. Addition of the methanogenesis inhibitor 2-bromoethanesulfonic acid resulted in acetate accumulation without impact on the sequential dechlorination of HCB. An anaerobic biodegradability assay was performed and the following data were obtained for the Tween 60, 61, and 65, respectively: 53, 62, and 62% COD destruction; 35, 57, and 48% COD to methane conversion; and 38, 38, and 45% COD to acetate conversion. These data suggest that the hydrophobic moiety (stearate) of the surfactants was preferentially degraded, most likely through β-oxidation, to acetate and ultimately to methane and carbon dioxide. Between 38 and 47% of the initial surfactant COD remained after 46 d incubation, which most likely corresponds to the hydrophilic polyoxyethylene moiety. An anaerobic biodegradation pathway of the Tween surfactants is proposed.


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