Phenol biodegradation by Acinetobacter radioresistens APH1 and its application in soil bioremediation

2019 ◽  
Vol 104 (1) ◽  
pp. 427-437 ◽  
Author(s):  
Yifan Liu ◽  
Weiwei Wang ◽  
Syed Bilal Shah ◽  
Giulio Zanaroli ◽  
Ping Xu ◽  
...  
2003 ◽  
Author(s):  
Charles Thomas Parker ◽  
Dorothea Taylor ◽  
George M Garrity

2009 ◽  
Vol 17 (3) ◽  
pp. 611-617 ◽  
Author(s):  
Éva Fenyvesi ◽  
Laura Leitgib ◽  
Katalin Gruiz ◽  
Gábor Balogh ◽  
Attila Murányi
Keyword(s):  

2012 ◽  
Vol 550-553 ◽  
pp. 2296-2300 ◽  
Author(s):  
Xiao Jun Meng ◽  
Yu Xiu Zhang ◽  
Rong Jia ◽  
Xia Li ◽  
Tuan Yao Chai ◽  
...  

A aerobic bacterium strain P2 isolated from coking wastewater, was able to utilize phenol, o-cresol and pyridine as its sole carbon and energy source. The morphological properties and the phylogenetic analysis based on 16S rDNA sequences showed strain P2 belonged to the genus Diaphorobacter sp.. The optimum biodegradation of phenol was 37°C, pH 7.0-9.0 and 0.25% NaCl , respectively. The growth arrearage period was prolonged with the phenol concentration. The growth of Diaphorobacter P2 and phenol-degradation were inhibited completely by 50 μmol/L metal ions, such as Cu2 +, Ni2+, Cd2+ or Cr6+. Orthogonal experiment indicated the order of metal toxicity to biodegradation of P2 was Zn2+>Mn2+>Pb2+ under various heavy-metal compounds. The phenol biodegradation in coking wastewater supplemented with 2/3 beef extract peptone medium was degraded fully in 3 days, indicating that nutrient solution was beneficial for P2 growth and phenol degradation in wastewater. Those results suggest that the Diaphorobacter P2 has potential for treatment of coking wastewater.


2006 ◽  
Vol 39 (2) ◽  
pp. 553-558 ◽  
Author(s):  
Cherif Ben-Youssef ◽  
Julio Waissman ◽  
Gabriela Vázquez

2008 ◽  
Vol 58 (5) ◽  
pp. 1101-1106
Author(s):  
Pichiah Saravanan ◽  
K. Pakshirajan ◽  
P. K. Saha

An indigenous mixed culture of microorganisms, isolated from a sewage treatment plant, was investigated for its potential to simultaneously degrade phenol and m-cresol during its growth in batch shake flasks. 22 full factorial designs with the two substrates as the factors, at two different levels and two different initial concentration ranges, were employed to carry out the biodegradation experiments. For complete utilisation of phenol and m-cresol, the culture took a minimum duration of 21 hrs at their low concentration of 100 mg/L each, and a maximum duration of 187 hrs at high concentration of 600 mg/L each in the multisubstrate system. The biodegradation results also showed that the presence of phenol in low concentration range (100–300 mg/L did not inhibit m-cresol biodegradation; on the other hand, presence of m-cresol inhibited phenol biodegradation by the culture. Moreover, irrespective of the concentrations used, phenol was degraded preferentially and earlier than m-cresol. During the culture growth, a lag phase was observed above a combined concentration of 500 mg/L i.e., 200 mg/L m-cresol and 300 mg/L of phenol and above). Statistical analysis of the specific growth rate of the culture in the multisubstrate system was also performed in the form of ANOVA and Student ‘t’ test, which gave good interpretation in terms of main and interaction effects of the substrates.


2006 ◽  
Vol 29 (3) ◽  
pp. 227-234 ◽  
Author(s):  
Jiang Yan ◽  
Wen Jianping ◽  
Bai Jing ◽  
Wang Daoquan ◽  
Hu Zongding

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