一株高效邻苯二甲酸二丁酯降解菌的筛选、鉴定及其降解特性研究

李容榛, 李成, 赵暹, 刘春敬, 孟靖凯, 谢建治. 一株高效邻苯二甲酸二丁酯降解菌的筛选、鉴定及其降解特性研究[J]. 环境化学, 2019, (10): 2274-2282. doi: 10.7524/j.issn.0254-6108.2018111502
引用本文: 李容榛, 李成, 赵暹, 刘春敬, 孟靖凯, 谢建治. 一株高效邻苯二甲酸二丁酯降解菌的筛选、鉴定及其降解特性研究[J]. 环境化学, 2019, (10): 2274-2282. doi: 10.7524/j.issn.0254-6108.2018111502
LI Rongzhen, LI Cheng, ZHAO Xian, LIU Chunjing, MENG Jinkai, XIE Jian. Isolation and identification of a highly efficient DBP degrading bacteria and its degradation characteristics[J]. Environmental Chemistry, 2019, (10): 2274-2282. doi: 10.7524/j.issn.0254-6108.2018111502
Citation: LI Rongzhen, LI Cheng, ZHAO Xian, LIU Chunjing, MENG Jinkai, XIE Jian. Isolation and identification of a highly efficient DBP degrading bacteria and its degradation characteristics[J]. Environmental Chemistry, 2019, (10): 2274-2282. doi: 10.7524/j.issn.0254-6108.2018111502

一株高效邻苯二甲酸二丁酯降解菌的筛选、鉴定及其降解特性研究

    通讯作者: 谢建治, E-mail: xjianzhi@126.com
  • 基金项目:

    国家水体污染控制与治理科技重大专项(2015ZX07203-005)和河北省高等学校科学技术研究青年基金(QN2016255)资助.

Isolation and identification of a highly efficient DBP degrading bacteria and its degradation characteristics

    Corresponding author: XIE Jian, xjianzhi@126.com
  • Fund Project: Supported by the National Water Pollution Control and Management Technology Major Project of China(2015ZX07203-005) and the Science and Technology Research Fund for Young Scholars of Hebei Higher Institutions(QN2016255).
  • 摘要: 从活性污泥中分离出1株以邻苯二甲酸二丁酯(DBP)为碳源和能源生长的高效降解菌DP-2,经形态观察、生化鉴定及16S rDNA序列分析,鉴定该菌株为不动杆菌(Acinetobacter sp.).采用单因素试验研究了不同试验条件(接种量、DBP浓度、NaCl浓度和碳源)对菌株DBP降解特性的影响,结果表明:接种量大于10%时,菌株DP-2在3 d内对初始浓度为10 mg·L-1的DBP降解率可达到90%以上;DBP初始浓度为5—50 mg·L-1时,菌株在6 d内对DBP降解率均能达到90%以上,但高浓度DBP会影响菌株DP-2生长,DBP浓度为1000 mg·L-1时,DBP降解率仅为26.88%;菌株降解DBP的最佳NaCl浓度范围为0—20 g·L-1;此外,醋酸钠、蔗糖、葡萄糖添加对于菌株降解DBP均有一定的促进作用,其中葡萄糖效果最为明显.在此基础上,采用响应曲面法优化了菌株降解DBP的培养条件并进行了试验验证,在盐度为5 g·L-1,接种量为17.14%,底物浓度为9.81 mg·L-1,菌株对DBP的降解率为85.86%.
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  • [1] ROSLEV P, VORKAMP K, AARUP J, et al. Degradation of phthalate esters in an activated sludge wastewater treatment plant[J]. Water Research, 2007, 41(5):969-976.
    [2] HEUDORF U, MERSCHSUNDERMANN V, ANGERER J. Phthalates:Toxicology and exposure[J].International Journal of Hygiene & Environmental Health, 2007, 210(5):623-634.
    [3] SARATH JOSH M K, PRADEEP S, VIJAYALEKSHMI AMMA K S, et al. Phthalates efficiently bind to human peroxisome proliferator activated receptor and retinoid X receptor α, β, γ subtypes:an in silico approach[J]. Journal of Applied Toxicology, 2014, 34(7):754-765.
    [4] JOSH M K S, PRADEEP S, ADARSH V K, et al. In silico evidences for the binding of phthalates onto human estrogen receptor α, β subtypes and human estrogen-related receptor γ[J]. Molecular Simulation, 2014, 40(5):408-417.
    [5] FENG N X, YU J, MO C H, et al. Biodegradation of di-n-butyl phthalate (DBP) by a novel endophytic Bacillus megaterium strain YJB3[J]. Science of the Total Environment, 2018,616-617:117-127.
    [6] PRADEEP S, BENJAMIN S. Mycelial fungi completely remediate di(2-ethylhexyl)phthalate, the hazardous plasticizer in PVC blood storage bag[J]. Journal of Hazardous Materials, 2012, 235-236:69-77.
    [7] PRADEEP S, FASEELA P, JOSH M K S, et al. Fungal biodegradation of phthalate plasticizer in situ[J]. Biodegradation, 2013, 24(2):257-267.
    [8] JOSH M K S, PRADEEP S, BALACHANDRAN S, et al. Temperature- and solvent-dependent migrations of di(2-ethylhexyl)phthalate, the hazardous plasticizer from commercial PVC blood storage bag[J]. Journal of Polymer Research, 2012, 19(7):9915-9916.
    [9] GAN D W, WEN Z D. Phthalate esters in the environment:A critical review of their occurrence, biodegradation, and removal during wastewater treatment processes[J]. Science of the Total Environment, 2016, 541:986-1001.
    [10] CHEN J A, LIU H, QIU Z, et al. Analysis of di-n-butyl phthalate and other organic pollutants in Chongqing women undergoing parturition[J]. Environmental Pollution, 2008, 156(3):849-853.
    [11] PATIL N K, KUNDAPUR RSHOUCHE Y S, KAREGOUDAR T B. Degradation of plasticizer di-n-butylphthalate by Delftia sp. TBKNP-05[J]. Current Microbiology, 2006, 52(3):225-230.
    [12] 刘庆, 杨红军, 史衍玺,等. 环境中邻苯二甲酸酯类(PAEs)污染物研究进展[J]. 中国生态农业学报, 2012, 20(8):968-975.

    LIU Q, YANG H J, SHI Y Z, et al. Research progress of phthalate esters (PAEs) in the environment[J]. Chinese Journal of Eco-Agriculture, 2012, 20(8):968-975(in Chinese).

    [13] YUAN S Y, HUANG I, CHANG B V. Biodegradation of dibutyl phthalate and di-(2-ethylhexyl) phthalate and microbial community changes in mangrove sediment[J]. Journal of Hazardous Materials, 2010, 184(1):826-831.
    [14] 杨婧, 郭楚玲, 刘沙沙,等. 邻苯二甲酸酯降解菌的筛选、降解特性及土壤修复研究[J]. 农业环境科学学报, 2018, 37(5):933-940.

    YANG J, GUO C L, LIU S S, et al. Screening, degradation characteristics and soil remediation of phthalate-degrading bacteria[J]. Journal of Agro-Environment Science, 2018, 37(5):933-940(in Chinese).

    [15] TANG W J, ZHANG L S, FANG Y, et al. Biodegradation of phthalate esters by newly isolated Rhizobium sp. LMB-1 and its biochemical pathway of di-n-butyl phthalate[J]. Journal of Applied Microbiology, 2016, 121(1):177-186.
    [16] 高静静,陈丽玮,王宜青,等.一株邻苯二甲酸二(2-乙基己基)酯(DEHP)高效降解菌的筛选及其降解特性[J].环境化学,2016,35(11):2362-2369.

    GAO J J, CHEN L W, WANG Y Q, et al. Screening and degradation characteristics of a highly efficient degrading bacteria of Di(2-ethylhexyl) phthalate (DEHP)[J].Environmental Chemistry,2016,35(11):2362-2369(in Chinese).

    [17] LI J, GU J D, PAN L. Transformation of dimethyl phthalate, dimethyl isophthalate and dimethyl terephthalate by Rhodococcus rubber, Sa and modeling the processes using the modified Gompertz model[J]. International Biodeterioration & Biodegradation, 2005, 55(3):223-232.
    [18] 陈学斌. DEHP降解菌的分离及其与玉米联合修复受污染土壤[D]. 广州:暨南大学, 2017. CHEN X B. Separation of DEHP-degrading bacteria and its combined restoration with corn for contaminated soil[D]. Guangzhou:Jinan University, 2017(in Chinese).
    [19] 东秀珠, 蔡妙英. 常见细菌系统鉴定手册[M]. 北京:科学出版社, 2001. CAI M Y, DONG X Z. Common Bacterial System Identification Manual[J]. Beijing:Science Press, 2001(in Chinese).
    [20] 柴阳阳. DBP对蔬菜叶际、根际微生物和内生菌群落结构的影响[D].青岛:青岛科技大学,2018. CHAI Y Y. The effect of DBP on the intercropping, rhizosphere and endophytic community structure of vegetables[D]. Qingdao:Qingdao University of Science and Technology, 2018(in Chinese).
    [21] LIANG R,WU X,WANG X,et al. Aerobic biodegradation of diethyl phthalate by Acinetobacter sp. JDC-16 isolated from river sludge[J]. Journal of Central South University of Technology,2010,17(5):959-966.
    [22] 刘时旸. 邻苯二甲酸二正戊酯高效降解菌的筛选、降解特性及其降解途径研究[D].南京:南京农业大学,2015. LIU S C. Screening, degradation characteristics and degradation pathway of di-hexyl phthalate efficient degrading bacteria[D]. Nanjing:Nanjing Agricultural University, 2015(in Chinese).
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  • 收稿日期:  2018-11-15

一株高效邻苯二甲酸二丁酯降解菌的筛选、鉴定及其降解特性研究

    通讯作者: 谢建治, E-mail: xjianzhi@126.com
  • 河北农业大学资源与环境科学学院, 河北省农田生态环境重点实验室, 保定, 071001
基金项目:

国家水体污染控制与治理科技重大专项(2015ZX07203-005)和河北省高等学校科学技术研究青年基金(QN2016255)资助.

摘要: 从活性污泥中分离出1株以邻苯二甲酸二丁酯(DBP)为碳源和能源生长的高效降解菌DP-2,经形态观察、生化鉴定及16S rDNA序列分析,鉴定该菌株为不动杆菌(Acinetobacter sp.).采用单因素试验研究了不同试验条件(接种量、DBP浓度、NaCl浓度和碳源)对菌株DBP降解特性的影响,结果表明:接种量大于10%时,菌株DP-2在3 d内对初始浓度为10 mg·L-1的DBP降解率可达到90%以上;DBP初始浓度为5—50 mg·L-1时,菌株在6 d内对DBP降解率均能达到90%以上,但高浓度DBP会影响菌株DP-2生长,DBP浓度为1000 mg·L-1时,DBP降解率仅为26.88%;菌株降解DBP的最佳NaCl浓度范围为0—20 g·L-1;此外,醋酸钠、蔗糖、葡萄糖添加对于菌株降解DBP均有一定的促进作用,其中葡萄糖效果最为明显.在此基础上,采用响应曲面法优化了菌株降解DBP的培养条件并进行了试验验证,在盐度为5 g·L-1,接种量为17.14%,底物浓度为9.81 mg·L-1,菌株对DBP的降解率为85.86%.

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