Enhanced Degradation of Quinoline by Immobilized Bacillus Brevis
Enhanced Degradation of Quinoline by Immobilized Bacillus Brevis
Journal of the Korean Chemical Society. 2007. Apr, 51(2): 154-159
Copyright © 2007, The Korean Chemical Society
  • Received : November 09, 2006
  • Published : April 20, 2007
Export by style
Cited by
About the Authors
S, Balasubramaniyan
M., Swaminathan

Biodegradation of Quinoline by free and immobilized Bacillus brevis has been investigated. The rate of quinoline degradation by immobilized Bacillus brevis on coconut shell carbon is faster than the rate by the microorganism immobilized on foam pieces and free cells. A complete removal of 100 ppm of Quinoline in the sample was achieved at a hydraulic retention time of 20 hours with the biocatalyst prepared by immobilizing Bacillus brevis onto coconut shell carbon. The biocatalyst had a reasonable shelf life and desirable recycle capacity.
In recent years there has been increasing concern over the public health threat presented by the introduction of N-heterocyclic compounds into the environment. Little is known about the environmental fate of Quinoline, a heterocyclic compound found in coal tar, mineral oil and bone oil. In the Chemical industry it serves as a solvent and is the starting material for the synthesis of quinoline dyes and pharmaceuticals. Quinoline and some of its derivatives were reported to be toxic, carcinogenic and mutagenic. 1 - 4 The widespread use of quinoline and its derivatives entails that these compounds are distributed in the environment thus polluting soil and water.
Conventional biological processes (activated sludge tricking filters) can destroy a large fraction of biodegradable organic compounds found in wastewater and can remove additional materials by adsorption. But most of the hazardous compounds pass through conventional wastewater treatment facilities unaltered. In addition, they also have adverse impact in the composition and activities of microorganism in activated sludge flocs, thus reducing the overall performance of these facilities. The removal of these compounds is a real challenge for waste treatment engineers and scientists. There have been several reports on the bacterial degradation of quinoline. 5 - 9
Investigation on the taxonomy of the quinoline degrading bacteria showed that in most cases they were members of the genus pseudomonas . Pseudomonas are characterized by their ability to use a wide rage of organic compounds as sole sources of carbon and energy. Mostly these compounds are aromatic and heterocyclic substances.However, the ability to degrade quinoline does not appear to be confined to pseudomonas . A Gram-negative, aerobic moraxella bacterium and a Nocardia species were described showing these degrading properties. 5 , 8 , 10
Immobilization of microbial cells have received increasing interest in recent years. 11 , 16 It offers a promising potential for the improvement of efficiency of bioprocesses. Compared with free cells, immobilized cells have several advantages. The main advantages in the use of immobilized cells are their higher operational stability, their ease of use in a continuous reactor and their ability for scale-up.
Activated carbons are a group of amorphous forms of carbon with a highly developed pore structure. Due to high adsorption capacity, activated carbon finds wider applications in many gas phase and liquid phase adsorption systems. It is used as an industrial catalyst. Activated carbon is also used as a carrier for cells or enzymes in biochemical reactions. 17
Immobilized cells on carbon were widely used for treatment of numerous toxic compounds such as pentachlorophenol. 13 , 18 - 20 benzene derivatives and dichlorobenzoates, 21 2, 4-dichlorphenoxy acetic acid 22 phthalic acid ester 12 and 2,4-dichlorophenol. 23 , 24
In this paper we report the efficiency of free and immobilized bacterium Bacillus brevis on the degradation of Quinoline and the storage capacity and reusability of the immobilized biocatalyst.
- Microorganism
The microorganism used in this study was a pure strain, isolated from the soil suspension of carbonization plant effluent channel. One gram of the soil suspension was inoculated into sterile tubes with 9 ml of the medium containing nutrient broth and cetrimide agar. After two days of incubation, the contents were examined for turbidity and the turbid portion was streaked out on plates containing potassium thiocyanate as a sole source. Colonies that grow on the plates were selected for identification The bacterium was analysed by biochemical, morphological and physiological tests in Institute of Microbial Technology, Chandigarh. The bacterium is motile, mesophilic and salt tolerant (up to 9%). It grows up to a temperature of 37 ℃ and pH 9. There is a growth of the bacterium under aerobic and partial anaerobic conditions. The results of biochemical tests match with Bacillus brevis as per the Bergey’s manual of systematic Bacteriology (Vol.1, 1989). Hence the organism was identified as Bacillus brevis and labeled as MTCC 3136.
- Preparation of culture
The organism was grown in nutrient broth medium for 48 hrs at 35 ℃ under stationary condition. The culture was then harvested by centrifugation at 10,000 rpm for 20 minutes, washed twice with sterilized water and resuspended in sterile buffered water. The centrifuged biomass was used for the degradation.
- Immobilization of organism
Foam pieces and coconut shell carbon were used as matrices for immobilization. The bacterial suspension used for immobilization contains 48 hrsgrown cells incubated at 35 ℃ in the nutrient broth. The immobilization was carried out by passing this suspension 5 times up and down through the column highly packed with either by sterilized foam pieces of uniform size (5×5 mm) or by coconut shell carbon spherical particles. The washings of the column after immobilization showed negative results in the biological analysis for the presence of cells. This reveals that cells are inside the pores of the matrices. This observation was also confirmed by the same efficiency of immobilized cells on to coconut shell carbon with the repeated use.
- Batch and Column Study
In biodegradation, the experiments were performed either in batch reactor or continuous flow reactor ( . 1 ) using free or immobilized cells respectively. Erlenmeyer flasks plugged with foam stopper were used as batch reactor. For the continuous flow reactor acrylic tube of 1m length and 10 cm diameter was used. The samples were withdrawn periodically and analysed for growth of the bacterium and quinoline degradation using Hitachi U-2001 spectrophotometer. The concentration of quinoline was determined by measuring the absorbance of the centrifugate at 313 nm. The growth of the cells in batch reactor was determined by measuring the absorbance of the sample at 540 nm.
PPT Slide
Lager Image
Schematic flow diagram of continuous column reactor.
- Quinoline degradation by Bacillus brevis free cells
The inoculums of Bacillus brevis was added to the solutions with solutions of different concentrations of quinoline. The samples were taken at regular intervals of time and the cell growth and quinoline concentration were determined. The growth of the bacterium at different initial concentrations of quinoline is shown in . 2 . The degradation of quinoline for various initial concentrations of quinoline is shown in . 3 . The growth of the bacterium decreases and the lag period increases with increase in the concentration of quinoline. The time required for complete degradation increases with the increase in initial concentration. The bacterium is capable of completely degrading the quinoline up to a concentration of 200 ppm in 50 hrs. A comparison of . 2 and 3 reveals that the growth of the bacterium matches with the degradation. This indicates that the bacterium grows only by taking quinoline as carbon, nitrogen and energy sources.
PPT Slide
Lager Image
Growth of Bacillus brevis with different concentrations of quinoline. 1. 100 ppm, 2. 200 ppm, 3. 300 ppm 4, 400 ppm, 5. 500 ppm.
PPT Slide
Lager Image
Quinoline degradation by Bacillus brevis (free cells). 1. 100 ppm, 2. 200 ppm, 3. 300 ppm 4, 400 ppm, 5. 500 ppm.
The influence of pH on quinoline degradation had been carried out and the results are shown in . 4 . The degradation of quinoline increases with increase in pH from 6-9 and then decreases. The degradation is found to be efficient at pH 9 and it is taken as optimum pH.
PPT Slide
Lager Image
Effect of pH on quinoline degradation by Bacillus brevis (free cells). 1. pH 6, 2. pH 7, 3. pH 8, 4. pH 9, 5. pH 10.
- Quinoline degradation by bacillus brevis immobilized on foam pieces and activated carbon
Quinoline degradation by Bacillus brevis immobilized on foam pieces and coconut shell carbon were carried out in a continuous flow reactor. . 5 and 6 show the quinoline degradation by immobilized cells with different initial concentrations of quinoline. A complete degradation for 300 ppm in foam pieces and for 400 ppm in coconut shell carbon was observed in 65 hrs. The immobilized cells on coconut shell carbon are more efficient than those on foam pieces. . 7 shows quinoline concentration – time – degradation diagram of Bacillus brevis immobilized on coconut shell carbon. The diagram is more advantageous as it gives the time required for the start of degradation ( ts ), time required for 100% degradation ( tf ) and time for 50% of quinoline degradation ( t ½ ) at various quinoline concentrations. To the left of the ts curve the quinoline degradation does not occur and to the right of the tf curve quinoline in the medium is negligibly small. With the increase of quinoline concentration the increase in t ½ and tf are more when compared to the increase in ts . This reveals that change in time for the start of degradation is not much but the time for 50% and 100% degradation increases sharply with the increase in quinoline concentration.
PPT Slide
Lager Image
Quinoline degradation by Bacillus brevis immobilized on foam pieces. 1. 100 ppm, 2. 200 ppm, 3. 300 ppm 4, 400 ppm, 5. 500 ppm.
PPT Slide
Lager Image
Quinoline degradation by Bacillus brevis immobilized on coconut Shell carbon. 1. 100 ppm, 2. 200 ppm, 3. 300 ppm 4, 400 ppm, 5. 500 ppm.
PPT Slide
Lager Image
Quinoline concentration – time of degradation diagram for Bacillus brevis immobilized on coconut shell carbon. ts- time for the start of degradation, t½-Time for 50% degradation, tf - time for complete degradation.
- Storage stability and repeated usability of the cells immobilized on carbon
Since the efficiency of degradation is higher with the cells immobilized on coconut shell carbon, we had carried out an experiment to find its storage stability and repeated usability for three months. The concentrations 100,200 and 300 ppm of Quinoline were used for the degradation by cells immomobilized on coconut shell carbon. A complete degradation of 100 ppm of Quinoline is observed in 20 hours of hydraulic retention time and the percentage of removal decreases with increase in Quinoline concentration ( . 8 ). The biocatalyst after its use was washed with double distilled sterile water and kept in the column for a month. The experiment was repeated with this biocatalyst using the same concentrations of Quinoline two times and the results are displayed in . 8 . The figure shows that the efficiency of this biocatalyst remained same every month for three months.
PPT Slide
Lager Image
Storage stability and repeated usability of the carbon immobilized cells on Quinoline degradation (20 Hours).
Comparison of the efficiencies of free and immobilized cells
PPT Slide
Lager Image
Comparison of the efficiencies of free and immobilized cells
The immobilized cells are advantageous in wastewater treatment due to easy transportation and storage. During storage and transportation the immobilized organism is likely to be affected due to environmental alteration and thus the efficiency deteriorates. If immobilization of cells were only on the surface of the carrier materials, the cells might be sloughed off by attrition during continuous treatment leading to a decrease in efficiency of the immobilized cells in degradation process. The experiment did show that the cells had maintained its efficiency in the removal of Quinoline. Hence the immobilized organism must be in the pores of the activated carbon. This fact is considered to be important while advocating the immobilized system for biodegradation or bioconversion of organics in wastewater.
The time required for 50% quinoline degradation by the free and immobilized cells are given in 1 . The immobilized cells are found to be efficient than free cells. The cells immobilized on coconut shell carbon are more efficient than those on foam pieces.
The microbe Bacillus brevis grows by consuming quinoline as C, N and energy sources. The growth of the organism and quinoline degradation efficiencies are more at pH 9. The immobilized cells are efficient than free cells. Cells immobilized on activated coconut shell carbon are found to be more efficient than cells immobilized on foam pieces. The storage stability and repeated usability of the biocatalyst developed by immobilizing the bacterium on to coconut shell carbon will be very useful for the degradation of Quinoline in wastewater.
Minako N. , Takio Y. , Yuko S. , Takashi S. 1977 Mutant. Res. 42 335 -    DOI : 10.1016/S0027-5107(77)80037-7
Sideropoulos A. S. , Secht S. M. 1996 Mutant . Res. 11 59 -
Jianlong W. , Liping H. , Hanchang S. , Yi Q. 2001 Chemosphere 44 1041 -    DOI : 10.1016/S0045-6535(00)00469-0
Sugaya K. , Nakayama O. , Hinata N. , Kamekura K. , Ito A. , Yamagiwa K. , Ohkawa A. 2001 Chem.Technol and Biotechnol. 76 603 -    DOI : 10.1002/jctb.423
Grant D. J. W. , Al-Najjar T. R. 1976 Microbes. 15 177 -
Dzumedzei N. V. , Shevchnko A. G. , Turovskii A. A. , Staroviotov I. I. 1982 Microbiology 52 157 -
Bennet J. L. , Updegraff D. M. , Pereira W. E. , Rostad C. 1985 Microbios Lett. 29 147 -
Shukla O. P. 1986 Appl, Environ. Microbial. 51 1332 -
Jianlong W. , Xiangchun Q. , Liping H. , Yi Q. , Hegemann W. 2001 Chemosphere. 44 1041 -    DOI : 10.1016/S0045-6535(00)00469-0
Han L. , Wang J. , Shi H. , Qian Y. 2000 J. Environ. Sci. 12 22 -
Wang J. D. , Hou W. , Qian Y. 1995 Biotechnol. Techniques. 9 203 -    DOI : 10.1007/BF00157079
Wang J. , Liu P. , Qian Y. 1997 Environ. Int. 23 775 -    DOI : 10.1016/S0160-4120(96)00081-5
Wang J. , Quan Y. 1999 Chemosphere. 38 3109 -    DOI : 10.1016/S0045-6535(98)00516-5
Cassidy M. B. , Lee H. , Trevors J. T. 1996 J. Ind. Microbial. 16 79 -    DOI : 10.1007/BF01570068
Gosmann B. , Rehm H. J. 1986 Appl. Microbiol. Biotechnol. 23 163 -    DOI : 10.1007/BF00261907
Trevors J. T. , Elsas J. D. , Lee H. , Wolters A. C. 1993 Appl. Microbial. Biotechnol. 39 637 -    DOI : 10.1007/BF00205067
Ehrhardt H. M. , Rehm H. J. 1985 Appl. Microbiol. Biotechnol. 21 32 -
Balfanz J. , Rehm H. J. 1991 Appl. Microbiol. Biotechnol. 35 662 -    DOI : 10.1007/BF00169634
OReilly K. T. , Crawford R. L. 1989 Appl. Environ. Microbiol. 55 213 -
Hu Z. C. , Korus R. A. , Levison W. E. , Crawford R. L. 1994 Environ. Sci. Technol. 28 491 -    DOI : 10.1021/es00052a023
Sahasrabudhe S. R. , Modi A. J. , Modi V. V. 1988 Biotechnol. Bioeng. 31 889 -    DOI : 10.1002/bit.260310818
Shreve G. S. , Vogel T. M. 1993 Biotechnol. Bioeng. 41 370 -    DOI : 10.1002/bit.260410312
Quan X. , Shi H. , Wang J. , Qian Y. 2003 Chemosphere. 50 1069 -    DOI : 10.1016/S0045-6535(02)00625-2
Quan X. , Shi H. , Liu H. , Lv P. , Qian Y. 2004 Wat. Res. 38 245 -    DOI : 10.1016/j.watres.2003.09.003