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应用红外方法探讨耐镉菌株高积累Cd^(2+)的机理 被引量:18

Research on high accumulating Cd^(2+) mechanism of a toletant-Cd^(2+) strain by Infrared spectroscopy analysis
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摘要 从安徽某冶炼厂污染土壤中分离出一株能耐高浓度镉的菌株(J5),经初步鉴定为假单胞菌属(Pseudomonassp.).该菌株在液体培养基中耐受40mmol.L-1CdSO4,在固体培养基上耐受75mmol.L-1CdSO4.培养基中Cd2+、Zn2+、Pb2+、Cu2+浓度分别为100mg.L-1和Mn2+浓度为275mg.L-1时,菌株生长正常.在重金属Cu2+、Pb2+、Zn2+、Mn2+存在时,采用红外光谱与原子吸收光谱分析菌株对Cd2+的积累,结果表明,在低浓度Cd2+溶液中菌株细胞对Cd2+的积累,主要靠细胞壁上—NH2与Cd2+配位结合;在高浓度Cd2+溶液中,细胞壁上—NH2、—OH、—COOH、—PO43-、—M—O(O—M—O)基团吸附Cd2+的能力显著.Mn2+可以增加细胞壁上有效官能团活性,提高Cd2+积累率;但当有Zn2+、Pb2+、Cu2+重金属离子共存时,即使有Mn2+存在,菌体对Cd2+吸附积累能力未见提高. A tolerant-cadmium strain J5, isolated from the polluted soil around the smeltery in Anhui province, was identified as Pseudomonas sp. strain. It can tolerate 40 mmol·L^- 1 cadmium sulphate in liquid medium and 75 mmol· L^- 1 Cd^2+ in solid medium. The strain grew normal in the presence of 100 mg·L^- 1 of Cd^2+、Zn^2+、Pb^2+、Cu^2+ and 275 mg·L^-1 of Mn^2+ , respectively. The accumulation to Cd^2+ in the strain was observed by infrared spectroscopy and atomic absorption spectroscopy, in the presence of Cd^2+、Pb^2+、Zn^2+、Mn^2+ . The results indicated that in low Cd^2+ concentration, -NH2 group on the cell wall mostly match with Cd^2+ . When in high Cd^2+ concentration, -NH2, -OH, -COOH, -PO4^3- and -M-O(O-M-O)groups strongly adsorbed Cd^2+ . Mn^2+ increased the activity of the groups mentioned above, and facilitated the accumulation of Cd^2+ on the cell wall. In contrast, Zn^2+、Ph^2+、Cu^2+. ions coexisting decreased such adsorption and accumulation, even if in the Bresence of Mn^2 + .
出处 《环境科学学报》 CAS CSCD 北大核心 2005年第11期1502-1506,共5页 Acta Scientiae Circumstantiae
关键词 耐镉细菌 重金属离子 吸附 红外光谱 tolerant-cadmium bacterium, heavy metal ions, adsorption, Infrared spectroscopy
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参考文献12

  • 1Filali B K, Taoufik J, Zeroual Y, et al. 2000. Waste Water Bacterial Isolates Resistant to Heavy Metals and Antibiotics [ J ]. Current microbiology, 41:151-156.
  • 2Kamnev A A, Risti? M, Antonyuk L P, et al. 1997. Fourier transform infrared spectroscopic study of intact cells of the nitrogen-fixing bacterium Azospirillum brasilense [ J]. J Mol structure, 408/409: 201-205.
  • 3Kamnev A A, Antonyuk L P, Matora L Y, et al. 1999. Spectroscopic characterization of cell membranes and their constituents of the plantassociated soil bacterium. Azospirillum brasilense [ J ]. J Mol structure,480/481: 387-393.
  • 4Llanos J, Capasso C, Parisi E, et al. 2000. Susceptibility to heavy metals and cadmium accumulation in aerobic and anaerobic themophilic microorganisms isolated from deep-sea Hydrothermal Vents [J]. Current Microbiology, 41: 201-205.
  • 5McEldowney S. 2000. The impact of surface attachment on cadmium accumulation by Pseudomonas fluorescens H2 [ J ]. FEMS Microbiology Ecology, 33:121-128.
  • 6Pethkar A V, Kulkarni S K, Paknikar K M. 2001. Comparative studies on metal biosorption by two strains of Cladosporium cladosporioides [ J ].Bioresource Technology, 80:211-215.
  • 7Ridvan S, Nalan Y, Adil D. 2003. Biosorption of cadmium, lead, mercury and arsenic ions by the fungus Penicillium purpurogenum[J]. Separation Science and Technology, 38(9) :2039-2053.
  • 8Simkiss K, Taylor M G. 1989. Metal fluxes across the membranes of aquatic organisms [J]. Rev Aquat Sci, 1:173-176.
  • 9Yilmaz E I. 2003. Metal tolerance and biosorption capacity of Bacillus circulans strain EB1[J]. Research in Microbiology 154:409-415.
  • 10刘爱民,黄为一.应用红外方法探讨耐镉菌株高积累Cd^(2+)的机理[J].环境科学学报,2005,25(11):1502-1506. 被引量:18

二级参考文献12

  • 1刘爱民,黄为一.应用红外方法探讨耐镉菌株高积累Cd^(2+)的机理[J].环境科学学报,2005,25(11):1502-1506. 被引量:18
  • 2Filali B K, Taoufik J, Zeroual Y, et al. 2000. Waste Water Bacterial Isolates Resistant to Heavy Metals and Antibiotics [ J ]. Current microbiology, 41:151-156.
  • 3Kamnev A A, Risti? M, Antonyuk L P, et al. 1997. Fourier transform infrared spectroscopic study of intact cells of the nitrogen-fixing bacterium Azospirillum brasilense [ J]. J Mol structure, 408/409: 201-205.
  • 4Kamnev A A, Antonyuk L P, Matora L Y, et al. 1999. Spectroscopic characterization of cell membranes and their constituents of the plantassociated soil bacterium. Azospirillum brasilense [ J ]. J Mol structure,480/481: 387-393.
  • 5Llanos J, Capasso C, Parisi E, et al. 2000. Susceptibility to heavy metals and cadmium accumulation in aerobic and anaerobic themophilic microorganisms isolated from deep-sea Hydrothermal Vents [J]. Current Microbiology, 41: 201-205.
  • 6McEldowney S. 2000. The impact of surface attachment on cadmium accumulation by Pseudomonas fluorescens H2 [ J ]. FEMS Microbiology Ecology, 33:121-128.
  • 7Pethkar A V, Kulkarni S K, Paknikar K M. 2001. Comparative studies on metal biosorption by two strains of Cladosporium cladosporioides [ J ].Bioresource Technology, 80:211-215.
  • 8Ridvan S, Nalan Y, Adil D. 2003. Biosorption of cadmium, lead, mercury and arsenic ions by the fungus Penicillium purpurogenum[J]. Separation Science and Technology, 38(9) :2039-2053.
  • 9Simkiss K, Taylor M G. 1989. Metal fluxes across the membranes of aquatic organisms [J]. Rev Aquat Sci, 1:173-176.
  • 10Yilmaz E I. 2003. Metal tolerance and biosorption capacity of Bacillus circulans strain EB1[J]. Research in Microbiology 154:409-415.

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