Bioremediation of environmental endocrine disruptor di-n-butyl phthalate ester by Rhodococcus ruber.

In this study DBP-degradation strain CQ0301 was isolated from rubbish landfill soil. According to the biophysical, biochemical characteristics and analysis of 16S rRNA, the strain was identified as Rhodococcus ruber. Three new protein bands could be fractioned after DBP-inducing, which were suspected to participate the process of DBP-degrading. Catechol was suspected to be an intermediate product of DBP and cleaving the benzene ring was catalyzed by catechol 1,2-dioxygenase, because a highly activity of catechol 1,2-dioxygenase could be detected after DBP-inducing. The results of this study also showed the optimal pH value, optimal temperature which influenced the degradation rate in soil: pH 7.0-8.0, 30-35 degrees C. Kinetics of degradation reaction had been performed at different initial concentration and different time. Analyzed with SPSS10.0 software, the DBP degradation can be described as the same exponential model when the initial DBP concentration was lower than 50 mg/kg. The kinetics equation was lnC=-0.1332t + A, with the degradation half-life of DBP in soil (5.20 d). Inoculating CQ0301 could relieve DBP content in plant. We also found that adding nutrient materials into soil was useful for decreasing the DBP content in plant. In summary, we isolated a bacterium capable of degrading DBP and decreasing DBP content in plant. We also explored the mechanism of biodegradation and characterized the environmental factors influencing the degradation process in contaminated soil. Based on this work, we hope that these findings can provide some information for applying of bioremediation of DBP contaminated soil.

[1]  Huff Je,et al.  Phthalate esters carcinogenicity in F344/N rats and B6C3F1 mice. , 1984 .

[2]  L L Needham,et al.  Levels of seven urinary phthalate metabolites in a human reference population. , 2000, Environmental health perspectives.

[3]  M. Fuller,et al.  Microbiological changes during bioremediation of explosives-contaminated soils in laboratory and pilot-scale bioslurry reactors. , 2004, Bioresource technology.

[4]  H. Kay Environmental Health Criteria , 1980 .

[5]  O. Hayaishi,et al.  Studies on oxygenases; pyrocatechase. , 1957, The Journal of biological chemistry.

[6]  S. Young,et al.  Differential Steroidogenic Gene Expression in the Fetal Adrenal Gland Versus the Testis and Rapid and Dynamic Response of the Fetal Testis to Di(n-butyl) Phthalate1 , 2005, Biology of reproduction.

[7]  L. Burns,et al.  Phthalate ester hydrolysis: Linear free energy relationships , 1980 .

[8]  C. Saiz-Jimenez,et al.  Identification of organic pollutants in agricultural soils from Tianjin, China , 1993 .

[9]  H. Kita,et al.  Studies on oxygenases. I. Comparative studies on 3,4-dihydroxyphenylacetate-2,3-oxygenase and pyrocatechase by electron spin resonance spectroscopy. , 1969, Journal of biochemistry.

[10]  Y. Qian,et al.  Microbial degradation of di-n butyl phthalate. , 1995, Chemosphere.

[11]  N. Kalogerakis,et al.  Monitoring the sonochemical degradation of phthalate esters in water using solid-phase microextraction. , 2004, Chemosphere.

[12]  J. Sumpter,et al.  A variety of environmentally persistent chemicals, including some phthalate plasticizers, are weakly estrogenic. , 1995, Environmental health perspectives.

[13]  L. Jun Studies on isolation, identification and degradation characteristics of DBP-degradation strain CQ0302 , 2005 .

[14]  J. Huff,et al.  Phthalate esters carcinogenicity in F344/N rats and B6C3F1 mice. , 1984, Progress in clinical and biological research.

[15]  W. Evans,et al.  The meta cleavage of catechol by Azotobacter species. 4-Oxalocrotonate pathway. , 1971, European journal of biochemistry.

[16]  P. Foster,et al.  Disruption of androgen-regulated male reproductive development by di(n-butyl) phthalate during late gestation in rats is different from flutamide. , 1999, Toxicology and applied pharmacology.

[17]  Jianlong Wang,et al.  KINETICS OF PHTHALIC ACID ESTER DEGRADATION BY ACCLIMATED ACTIVATED SLUDGE , 1997 .

[18]  Yingying Wang,et al.  Aerobic degradation of phthalic acid by Comamonas acidovoran Fy-1 and dimethyl phthalate ester by two reconstituted consortia from sewage sludge at high concentrations , 2003 .

[19]  A. Freer,et al.  Purification and characterization of catechol 1,2-dioxygenase from Rhodococcus rhodochrous NCIMB 13259 and cloning and sequencing of its catA gene. , 1998, The Biochemical journal.

[20]  W. Jianlong,et al.  Microbial degradation of di-n-butyl phthalate , 1995 .

[21]  R. Chapin,et al.  Reproductive toxicity of di-n-butylphthalate in a continuous breeding protocol in Sprague-Dawley rats. , 1997, Environmental health perspectives.