Please wait a minute...
Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front Envir Sci Eng    2013, Vol. 7 Issue (2) : 185-190    https://doi.org/10.1007/s11783-012-0435-6
RESEARCH ARTICLE
Biosorption and biotransformation of crystal violet by Aeromonas hydrophila DN322p
Tao PAN1,2,3,4,5, Suizhou REN2,3,4,5, Jun GUO2,3,4,5, Meiying XU2,3,4,5, Guoping SUN2,3,4,5()
1. School of Bioscience and Bioengineering, South China University of Technology, Guangzhou 510006, China; 2. Guangdong Institute of Microbiology, Guangzhou 510070, China; 3. Guangdong Provincial Key Laboratory of Microbial Culture Collection and Application, Guangdong Institute of Microbiology, Guangzhou 510070, China; 4. Guangdong Open Laboratory of Applied Microbiology, Guangzhou 510070, China; 5. State Key Laboratory of Applied Microbiology (Ministry-Guangdong Province Jointly Breeding Base), South China, Guangzhou 510070, China
 Download: PDF(210 KB)   HTML
 Export: BibTeX | EndNote | Reference Manager | ProCite | RefWorks
Abstract

DN322p, an offspring of Aeromonas hydrophila DN322, has the capacity to adsorb and decolorize triphenylmethane dyes in wastewater simultaneously. As a common triphenylmethane dye, crystal violet (CV) was chosen to test the decolorization characteristics of DN322p. Within 0.5 h, the strain DN322p adsorbed a large amount of CV, producing a deep-colored cell pellet and colorless supernatant. The colors of the cell pellet and supernatant lightened over time. The supernatant and dichloromethane extract of the cell pellet both showed conspicuous CV and leuco CV (LCV) characteristic absorbance peaks at 590 nm and 260 nm, respectively, in the UV-vis spectral analysis. This finding indicated that the DN322p cells can adsorb the two dyes. A 99% (w/w) decolorization rate was achieved within 2.5 h with shaking at 30°C for 50 mg CV·L-1. High Performance Liquid Chromatography (HPLC) analysis of the dichloromethane extract of the supernatant and cell pellet confirmed that CV was mainly converted into its leuco form. Dead cells had a similar adsorption capacity with living cells. About 90% of CV in the dye solution (50 mg·L-1) was removed by autoclaved cells with an optical delnsity at 600 nm (OD600) above 1.0.

Keywords crystal violet      decolorization      biosorption      biotransformation      Aeromonas hydrophila DN322p     
Corresponding Author(s): SUN Guoping,Email:guopingsun@163.com   
Issue Date: 01 April 2013
 Cite this article:   
Tao PAN,Guoping SUN,Suizhou REN, et al. Biosorption and biotransformation of crystal violet by Aeromonas hydrophila DN322p[J]. Front Envir Sci Eng, 2013, 7(2): 185-190.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-012-0435-6
https://academic.hep.com.cn/fese/EN/Y2013/V7/I2/185
Fig.1  Decolorization efficiency of 50 mg CV·L by DN322p over time
Fig.2  Progress of CV decolorization by DN322p: (a) 1 mL sample of decolorization culture solution was centrifuged at 8000?r·min and 0.5 h intervals, and then photographed; (b) the cell pellet was then extracted by 1 mL of dichloromethane, and the color of residual dyes in cell debris was photographed
Fig.3  UV-visible absorbance spectra of the decolorization products of CV: (a) dichloromethane extract of the culture supernatant; (b) dichloromethane extract of the cell pellet
Fig.4  HPLC analyses of the decolorization products of CV: (a) CV detection; (b) LCV detection. A: CV standard; B: CV detection of the culture supernatant; C: CV detection of the cell pellet; D: LCV standard; E: LCV detection of the culture supernatant; and F: LCV detection of the cell pellet. After 2.5 h, CV decolorization was complete. The dichloromethane extracts of the supernatant and cell pellet were detected by HPLC. The characteristic absorbance peaks of CV and LCV were scanned at 590 and 254 nm, respectively. The data were obtained from one experiment, which was repeated thrice
Fig.5  Percentage dye contents of the supernatant and cell pellet relative to the initial CV concentration after CV decolorization by DN322p
Fig.6  Adsorption curve of CV by autoclaved and living cells
1 Gregory P. Dyes and dyes intermediates. In: Kroschwitz JI, ed. Encyclopedia of Chemical Technology. Vol. 8 . New York: John Wiley & Sons, 1993, 544–545
2 Chen C C, Liao H J, Cheng C Y, Yen C Y, Chung Y C. Biodegradation of crystal violet by Pseudomonas putida. Biotechnology Letters , 2007, 29(3): 391–396
doi: 10.1007/s10529-006-9265-6 pmid:17206376
3 Kumar R, Ahmad R. Biosorption of hazardous crystal violet dye from aqueous solution onto treated ginger waste (TGW). Desalination , 2011, 265(1–3): 112–118
doi: 10.1016/j.desal.2010.07.040
4 Fan H J, Huang S T, Chung W H, Jan J L, Lin W Y, Chen C C. Degradation pathways of crystal violet by Fenton and Fenton-like systems: condition optimization and intermediate separation and identification. Journal of Hazardous Materials , 2009, 171(1–3): 1032–1044
doi: 10.1016/j.jhazmat.2009.06.117 pmid:19604632
5 Asad S, Amoozegar M A, Pourbabaee A A, Sarbolouki M N, Dastgheib S M. Decolorization of textile azo dyes by newly isolated halophilic and halotolerant bacteria. Bioresource Technology , 2007, 98(11): 2082–2088
doi: 10.1016/j.biortech.2006.08.020 pmid:17055263
6 Deng D Y, Guo J, Zeng G Q, Sun G P. Decolorization of anthraquinone, triphenylmethane and azo dyes by a new isolated Bacillus cereus strain DC11. International Biodeterioration and Biodegradation , 2008, 62(3): 263–269
doi: 10.1016/j.ibiod.2008.01.017
7 Chen C H, Chang C F, Liu S M. Partial degradation mechanisms of malachite green and methyl violet B by Shewanella decolorationis NTOU1 under anaerobic conditions. Journal of Hazardous Materials , 2010, 177(1–3): 281–289
doi: 10.1016/j.jhazmat.2009.12.030 pmid:20060225
8 Azmi W, Sani R K, Banerjee U C. Biodegradation of triphenylmethane dyes. Enzyme and Microbial Technology , 1998, 3(22): 185–191
doi: 10.1016/S0141-0229(97)00159-2
9 Wu J, Jung B G, Kim K S, Lee Y C, Sung N C. Isolation and characterization of Pseudomonas otitidis WL-13 and its capacity to decolorize triphenylmethane dyes. Journal of Environmental Sciences-China , 2009, 21(7): 960–964
doi: 10.1016/S1001-0742(08)62368-2 pmid:19862963
10 Jang M S, Lee Y M, Kim C H, Lee J H, Kang D W, Kim S J, Lee Y C. Triphenylmethane reductase from Citrobacter sp. strain KCTC 18061P: purification, characterization, gene cloning, and overexpression of a functional protein in Escherichia coli. Applied and Environmental Microbiology , 2005, 71(12): 7955–7960
doi: 10.1128/AEM.71.12.7955-7960.2005 pmid:16332773
11 Ren S Z, Guo J, Zeng G Q, Sun G P. Decolorization of triphenylmethane, azo, and anthraquinone dyes by a newly isolated Aeromonas hydrophila strain. Applied Microbiology and Biotechnology , 2006, 72(6): 1316–1321
doi: 10.1007/s00253-006-0418-2 pmid:16622679
12 Zengler K. Central role of the cell in microbial ecology. Microbiology and Molecular. Biology Reviews , 2009, 73(4): 712–729
doi: 10.1128/MMBR.00027-09 PMID:19946138
13 Fu Y, Viraraghavan T. Fungal decolorization of dye wastewaters: a review. Bioresource Technology , 2001, 79(3): 251–262
doi: 10.1016/S0960-8524(01)00028-1 pmid:11499579
[1] Yiquan Wu, Ying Xu, Ningyi Zhou. A newly defined dioxygenase system from Mycobacterium vanbaalenii PYR-1 endowed with an enhanced activity of dihydroxylation of high-molecular-weight polyaromatic hydrocarbons[J]. Front. Environ. Sci. Eng., 2020, 14(1): 14-.
[2] Feng XUE, Beicheng XIA, Rongrong YING, Shili SHEN, Peng ZHAO. Removal of Zn2+ from aqueous solution by biomass of Agaricus bisporus[J]. Front Envir Sci Eng, 2013, 7(4): 531-538.
[3] Bin YAN, Cuihong DU, Meilan XU, Wenchao LIAO. Decolorization of azo dyes by a salt-tolerant Staphylococcus cohnii strain isolated from textile wastewater[J]. Front Envir Sci Eng, 2012, 6(6): 806-814.
[4] Xiangliang PAN, Jing LIU, Wenjuan SONG, Daoyong ZHANG. Biosorption of Cu(II) to extracellular polymeric substances (EPS) from Synechoeystis sp.: a fluorescence quenching study[J]. Front Envir Sci Eng, 2012, 6(4): 493-497.
[5] Fengyu ZAN, Shouliang HUO, Beidou XI, Xiulan ZHAO. Biosorption of Cd2+ and Cu2+ on immobilized Saccharomyces cerevisiae[J]. Front Envir Sci Eng, 2012, 6(1): 51-58.
[6] Qian YAO, Hua ZHANG, Jun WU, Liming SHAO, Pinjing HE, . Biosorption of Cr(III) from aqueous solution by freeze-dried activated sludge: Equilibrium, kinetic and thermodynamic studies[J]. Front.Environ.Sci.Eng., 2010, 4(3): 286-294.
[7] R. RAJESH KANNAN, M. RAJASIMMAN, N. RAJAMOHAN, B. SIVAPRAKASH, . Brown marine algae turbinaria conoides as biosorbent for Malachite green removal: Equilibrium and kinetic modeling[J]. Front.Environ.Sci.Eng., 2010, 4(1): 116-122.
[8] WANG Xuejiang, XIA Siqing, ZHAO Jianfu. Biosorption of Direct Black 38 by dried anaerobic granular sludge[J]. Front.Environ.Sci.Eng., 2008, 2(2): 198-202.
Viewed
Full text


Abstract

Cited

  Shared   
  Discussed