Characterization and identification of newly isola

Characterization and identification of newly isolated Acinetobacter baumannii strain
serdang 1 for phenol removal
Z. H. M. Yadzir, M. Y. Shukor, M. S. Nazir, and M. A. Abdullah
Citation: AIP Conference Proceedings 1482, 223 (2012); doi: 10.1063/1.4757470
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Characterization and Identification of
Newly Isolated Acinetobacter baumannii Strain Serdang 1
for Phenol Removal
Z.H.M. Yadzir1, M.Y. Shukor2, M.S.Nazir1, M.A. Abdullah1,*
1
Department of Chemical Engineering, Universiti Teknologi PETRONAS,
Bandar Seri Iskandar, 31750, Tronoh, Perak D. R., Malaysia
2
Department of Biochemistry, Faculty of Biotechnology and Biomolecular Sciences,
Universiti Putra Malaysia, Serdang, 43400, Selangor, Malaysia
* Corresponding author. Tel.: +605-3687636; Fax: +605-3656176
E-mail address: [email protected]
Abstract. A new indigenous bacterial strain from Malaysian soil contaminated with petroleum waste had been
successfully isolated, characterized and identified for phenol removal. The gram negative bacteria showed 98% identity
with Acinetobacter baumannii based on BiologTM Identification System and the determination of a partial 16S ribosomal
RNA (rRNA) sequence. The isolate clustered with species belonging to Acinetobacter clade in a 16S rDNA-based
neighbour-joining phylogenetic tree.
Keywords: Acinetobacter baumannii, phenol, phylogenetic tree analysis, 16S ribosomal RNA
PACS: 87.17.Uv
INTRODUCTION
Microorganisms can utilize phenol as carbon and
energy sources, for growth, cell maintenance and cometabolism of other less degradable substances [1,2].
Bacteria plays major role in the degradation of phenol
in the ecosystem. Large numbers of phenol-degrading
bacteria, fungi and yeast have been isolated,
characterized and identified, which include
Acinetobacter calcoaceticus [3], Pseudo-monas putida
[4], Graphium and Fusarium species [5], Candida
oleophila [6] and Trichosporon montevideense [7].
Various Acinetobacter strains are capable of
degrading xenobiotic compounds such as phenol [8],
zearelenone [9], trinitrotoluene [10], 4-hydroxy
benzoate [11] and chlorinated biphenyls [12]. Others
have reported degradation of lignin [13], amino acids
[14], oil [15] and heavy metals removal [16]. Several
strains of Acinetobacter produce extracellular
degradation of polysaccharides [17], wax esters,
polyhydroxyalkalonic acids and cyanophycin [18,19].
A bioluminescent reporter strain, Acinetobacter sp.
DF4, has been constructed showing sensitive
bioluminescence response to phenol concentrations
ranging from 5 to 100 ppm [20].
The objectives of this study were to characterize
and identify newly-isolated, indigeneous bacteria from
Malaysian soil contaminated with petroleum waste for
possible use in the removal of hazardous materials
such as phenol.
MATERIALS AND METHODS
Phenotypical and Biochemical
Characterization
Bacterial Isolates
The bacterial strain was isolated from soil
contaminated with petrol wastes from a car workshop
in Serdang, Selangor, Malaysia. The strain was
initially assigned Isolate Serdang 1. The morphology
was observed by Gram staining and microscopy, and
the shape, elevation and pattern of colonies were
observed and recorded. Bacteria capable of utilizing
phenol as a sole carbon source was isolated by
enrichment in mineral salts medium containing 500
mg/L phenol as carbon source. The mineral medium
constituents were (g/L): 1.0 (NH4)2SO4 (R&M
Chemical, China), 0.25 MgSO4.7H20 (Merck,
Germany), 0.25 KH2PO4 (Merck, Germany), 0.07
CaCl2.2H2O (Merck, Germany), 0.1 yeast extract, 0.5
phenol (Hamburg Chemical, Germany). The isolation
of microbial strains was done by plating technique as
prescribed in APHA 9215 [21].
International Conference on Fundamental and Applied Sciences 2012
AIP Conf. Proc. 1482, 223-228 (2012); doi: 10.1063/1.4757470
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Gram staining
A microbial suspension was transferred to a glass
microscope slide, passed through a flame to affix the
cells. The smear was applied with crystal violet dye
(Fluka, Switzerland) as the primary stain, which
stained the cells blue-purple. The slide was washed
with distilled water and the specimen should appear
blue-purple. The slide was then flooded with Gram’s
iodine (Ajax Chemical, Australia), to increase the
affinity of the primary stain to the bacterial cells. The
smear was then discolored by 95% ethyl alcohol
(Hamburg Chemical, Germany), rinsed with distilled
water, before counterstained with safranin (Ajax
Chemical, Australia), which stained those bacteria that
were decolorized in the previous step. The slide was
blotted with bibulous paper and examined under the
light microscope (Olympus) at 100x magnification
with an oil immersion. The morphology of the cell was
also noted.
micropipettor. The ID Microplate was incubated at
room temperature for 16 to 24 hours, and placed in the
reader
for
analysis.
BiologTM Microstation
Identification was carried out using the pre-loaded ID
Database on a computer which identifies bacteria to
the species level.
Molecular Characterization of PhenolDegrading Bacteria
Genomic DNA Extraction
Cells were harvested from 1.5 ml culture by
centrifugation (Eppendorf, North America) at 13,000
rpm for 2 minutes and the supernatant was discarded.
Genomic DNA was extracted by alkaline lysis using
Wizard® Genomic DNA Purification KitTM (Promega,
USA). The DNA pellet obtained was used as a
template in Polymerase Chain Reaction (PCR). The
DNA pellet was stored at 4°C.
Oxidase and Catalase tests
DNA Quantification and Purity
Oxidase test was conducted to test for the presence
of cytochrome C oxidase, a component of electron
transport chain. A separate and well-grown colony
from a culture plate of 24 hour old was spread on to a
reaction zone of an oxidase strip (Medvet, South
Australia) and the colour change was observed for up
to 5 sec. A deep blue/violet color indicates positive
reaction, and a no color change indicates no reaction.
Catalase test was carried out to check the presence
of catalase enzyme as previously prescribed [22].
Culture streak of 24 hour old was applied with three or
four drops of 3% (v/v) hydrogen peroxide to the entire
culture surface to check for the presence or absence of
bubbling or foaming. Bubble formation indicates
presence of catalase.
The concentration and purity of the extracted DNA
was determined by a spectrophotometer (Beckman,
USA) [23].
BiologTM Identification System
BiologTM system uses a 96 well microplate having
different carbon source in each well as described in the
Microlog Users Manual (Biolog Inc., Hayward, CA).
The microplates are specific for Gram positive and
Gram negative isolates. The test inoculum was
prepared from overnight culture of bacterial Isolate
Serdang 1 on nutrient agar plate. The bacterial
colonies were picked using sterile cotton swab and resuspended into inoculation fluid. The bacterial
suspension was adjusted to 61% turbidity using the
BiologTM Turbidimeter (Biolog, Inc) according to the
manufacturer’s recommendation. One hundred and
fifty μl of the suspension was dispensed into all wells
of the BiologTM ID Microplates using the 8-channel
Amplification of Genomic DNA by PCR
PCR was performed by incubating the samples at
three temperatures in a thermal cycler (MJ Research
Inc., USA) corresponding to three steps in an
amplification cycle- denaturation, annealing and
extension. To amplify the 16s rRNA region, PCR was
performed using the 16s universal primer [24].
Following these cycles, a prolonged extension at 72°C
for 10 min was used [23].
Detection of PCR Products
DNA amplified was separated using agarose gel
electrophoresis. The agarose gel at 50-70°C was
poured into the gel tray and the comb was inserted.
Seven microliters of amplified PCR products were premixed with 1 μl of 6X loading dye (MBI Fermentas,
Lithuania) on a piece of parafilm and loaded into the
gel well. Gene Ruler TM 1kb DNA marker (MBI
Fermentas, Lithuania) was used as a standard. The
DNA was electrophoresed at 70 V supplied from a
Power Supply EPS 600 (Pharmacia, Biotech) for 1
hour and 30 min. After electrophoresis, the gel was
removed, stained with 0.5 μg/ml ethidium bromide for
15 min and then destained with distilled water. The
bands on the gel were visualized on an ultraviolet light
trans-illuminator and photographed using the Bio
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Imaging System
(Syngene,UK).
in
Gene
Snap
Program
Purification of desired PCR Product & Plasmid vector
The QIAquick Gel Extraction (QIAGEN,
Germany) was used to extract and purify the DNA
fragment from agarose gel, according to the
manufacturer’s instruction. The DNA fragment band
was excised from the agarose gel with a clean, sharp
scalpel.
TOPO TA Cloning® provides a highly efficient,
one step cloning strategy for direct insertion of Taq
polymerase-amplified PCR products into a plasmid
vector. It was supplied in linear form with single 3’thymidine (T) over hanged at both ends of the TA
Cloning vector and topoisomerase 1 enzyme
covalently bound to the vector.
TOPO Cloning Ligation Reaction
Six microliters of TOPO Cloning reaction mixture
(Fresh PCR product : Salt solution : pCR® 2.1-TOPO
vector = 4 : 1 : 1 μl) was prepared. The solution was
mixed gently and incubated for 5 min at room
temperature to prevent the reduction of transformation
and cloning efficiency.
Fermentas, Lithuania). The restriction digestion
reaction of 10 μl total volume (Sterile deionized water
: Restriction endonuclease Buffer : Restriction
endonuclease (BamHI) : Restriction endonuclease
(XhoI) : Recombinant plasmid = 1 : 2 : 1 : 1 : 5 μl )
was prepared. The solution was mixed gently by
repeated pipeting, followed by incubation at 37°C for
2 hours. The bands on the gel were visualized on an
ultraviolet light trans-illuminator and photographed by
BioImaging System in Gene Snap Program
(Syngene,UK).
Automated DNA Sequencing
The isolated plasmid DNA was subjected to
automated sequencing on both strands using forward
and reverse universal primers. The sequencing was
carried out by First Base Laboratories Sdn Bhd,
Malaysia. ABI PRISM BIGDYETM and Amersham
Pharmacia Biotech DYEnamic ET Terminator
Chemistry were used for the sequencing reactions. The
ABI PRISM® 377-96 DNA Sequencer automatically
analyses DNA molecules labeled with multiple
fluorescent dyes by the BIGDYETM or DYEnamic ET
Terminator sequencing reactions. The samples were
loaded onto vertical 5% Long Ranger DNA
(BioWhittaker Molecular Applications) sequencing
gels.
TOP 10 One Shot Chemical Transformation
DNA Sequence Homology Analysis
Twenty μl chemical competent cells of E.coli TOP
10 One Shot (Invitrogen, USA) were thawed on ice.
Six microliters of TOPO Cloning ligation reaction
mixture was added to a vial containing E.coli TOP 10
One Shot cells and mixed. The mixture was incubated
on ice for 30 min. The cells were heat shocked for 1
min at 42°C without shaking. The tube was then
incubated on ice for 2 min. The plates were incubated
at 37°C for 16 hours. After incubation, blue and white
colonies were observed.
Plasmid Extraction
Plasmid extraction was performed according to the
protocol as described by GeneJETTM Plasmid Miniprep
Kit (MBI Fermentas, Lithuania). The plasmid DNA
was stored at -20°C until use.
Analysis of Positive Clones by Restriction
Endonuclease (RE) Analysis
The presence of the inserted gene in the plasmid
was confirmed by digesting the extracted plasmid with
restriction endonucleases- BamHI and XhoI (MBI
The homology of the PCR amplified DNA
fragment was analyzed and compared with Genbank
database using the BLASTN 2.0.11 programs of the
National Center for Biotechnology Information, which
can be accessed at http://www.ncbi.nlm.nih.gov/
Genbank/.
Phylogenetic Analysis
A multiple alignment of 22 16S rRNA gene
sequences which closely matches Phenol-degrading
strain was retrieved from GeneBank and was aligned
using clustal-W [25] with the PHYLIP (phylogeny
inference package) output option. The aligment was
visually checked for any obvious mis-alignments.
Alignment positions with gaps were excluded from the
calculations. A phylogenetic tree was constructed
using PHYLIP, version 3.573 (J.Q. Felsenstein,
PHYLIP-phylogeny inference package, version 3.573,
Department of Genetics, University of Washington,
(http://evolution.genetics.washington.edu/phylip.html),
with Bacillus strain as the out group in the cladogram.
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Batch experiment
Culture Media
The medium used in all experiments was as
described before [26]. The medium was autoclaved
(Hirayama, USA) at 121°C for 15 minutes. Phenol
solution was filter sterilized using 0.2 μm syringe filter
(Sartorius, Germany) and added to the sterilized
medium at the beginning of the experiment. For the
preparation of phenol solid medium in plates, 20 g/l of
agar was added.
Bacterial Stock and Working Culture
Well-defined colonies of all pure bacterial isolates
were transferred to a phenol medium slant and
preserved at 4°C in refrigerator for future use. For
culture library collection, pure culture was transferred
into Eppendorf tubes containing 20% (v/v) glycerol
and preserved at -20°C for future use. Single colony
was transferred into a universal bottle containing 5 ml
liquid phenol medium at 500 mg/l phenol
concentrations. Cultures were incubated at 30°C for 48
hours at 100 rpm. One percent of bacterial suspension
(absorbency for concentration A600= 1.0) was
inoculated into a 250 ml Erlenmeyer flask (Pyrex)
containing 50 ml liquid phenol medium and incubated
on a rotary shaker (100 rpm) at 30°C. The cultures
were used as inoculum for experiments after leaving
overnight (~15 hours).
Bacterial Growth Determination
Bacterial growth population was determined using
a serial dilution technique to enumerate the colonyforming unit (CFU). The suspensions (100μl) were
spread onto phenol media agar and mixed by rotation.
The plates were incubated for 48 hours at 30°C and the
resulting colonies were counted.
The exponential increase in cell density after
inoculation is measured as a function of time and
analyzed to obtain the specific growth rate (μ), for that
particular substrate concentration as represented by the
equation :
dX / dt = µX
(1)
where X is cell density (CFU/ml), and t is time (day).
Phenol Concentration Determination
Colorimetric method based on 4-aminoantipyrine
(4-AAP) was used to determine phenol concentrations
using phenol solution as a standard [21]. After 15
minutes, the absorbance was read at 510 nm using
spectrophotometer.
The
amount
of
phenol
concentrations was estimated from the standard phenol
curve. This method determines phenol and ortho- and
meta-substituted phenols.
RESULTS AND DISCUSSION
Morphological and Physiological
Characterization
The colonies of bacterial strain Isolate Serdang 1
were observed as creamy colonies, round in shape with
either smooth or irregular edges. The cells were cocci
in shape and formed chains of 3-4 bacterial cells per
chain. The pink-red colour from gram-staining
indicated that it was Gram-negative. The formation of
bubbles in the Catalase test may suggest the evolution
of oxygen and the presence of catalase. However, the
results with oxidase test strip suggest that the Isolate
Serdang1 did not produce cytochrome c oxidase. It
could mean that it lacks cytochrome c oxidase but not
that it lacks an electron transport chain.
Oxidase test aids in differentiation among members
of the genera Pseudomonas, which are oxidase
positive, and Enterobacteriacea, which are oxidase
negative. Gram-negative E.coli is another example of
Enterobacteriacea with an oxidase negative, but having
an electron transport chain that contains other
cytochromes in its cytoplasmic membrane [22].
Oxidase enzymes play a vital role in the electron
transport system during aerobic respiration.
Cytochrome c oxidase, an enzyme found in many
electron transport chains including those of
eukaryotes, catalyzes the oxidation of a reduced
cytochrome by molecular oxygen, resulting in the
formation of hydrogen peroxide or water [27,28].
The physiological characteristics of Isolate Serdang
1 were determined by Biolog TM Identification System,
which can identify isolate to the species level and
show the metabolic capabilities of the isolate. The
system tests the ability of microorganisms to oxidize a
panel of 95 different carbon sources. Isolate Serdang 1
showed similar characteristics to Acinetobacter
baumannii at 99% probability, with similarity index of
0.712 at 24 hours. The identification was accepted as
correct based on similarity index of the genus and
species name as listed in the system database and if the
assigned identity matched the genus and species of the
reference ATCC strain [29].
Molecular Characterization
The intensity of absorbance of the DNA solution at
wavelength 260 nm and 280 nm was used as a
measure of DNA purity [23]. DNA absorbs UV light
at 260 nm and protein absorbs UV light at 280 nm.
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Pure sample of DNA has the 260/280 ratio at 1.7 to 2.0
and is relatively free from protein contamination. In
this study, the 260/280 ratio at 1.7 was recorded,
suggesting that pure DNA was obtained.
The recombinant plasmids were isolated and
digested with BamHI and XhoI which produced two
bands, the vector (~3.9 kbp) and the insert (~1.5 kbp).
Based on gel electrophoresis analysis as shown in
Figure 1, ~1.5 kbp band was seen, corresponding to
the 16s rRNA region of the complete genomic DNA.
Lane 1 Lane 2 Lane 3
~3.9 kbp
~1.5 kbp
strictly aerobic and tend to be paired cocci, rather than
monoflagellate rods. They can use various carbon
sources for growth and can be cultured on relatively
simple media [30]. Based on cell shape, absence of
flagella, G+C content of DNA and nutritional
properties, these organisms are initially classified in
the genus Moraxella but now known more as
Acinetobacter [31]. The Acinetobacter baumannii–
Acinetobacter calcoaceticus complex is the species
most commonly isolated from clinical specimens and
found as part of the normal skin, throat and rectal flora
as well as in food and body lice. It colonises patients
in Intensive Care Units and contaminates inanimate
hospital surfaces and devices as well as wounds,
including war injuries. Acinetobacter has also emerged
as a cause of nosocomial outbreaks and is
characterised by increasing antimicrobial multiresistance [30].
Kinetics of Microbial Cell Growth and
Phenol Removal
FIGURE 1. Restriction Endonuclease (RE) analysis of the
extracted plasmid of positive transformant colony. Lane 1:
DNA ladder marker; Lane 2: White colony: Vector (~3.9
kbp) with released PCR products (~1.5 kbp) Lane 3: Blue
colony: Vector (~3.9 kbp) without released PCR products.
This analysis confirmed that the clone carrying the
gene as an insert, has been obtained. The plasmid
vector contained a gene (ampR) coding for resistance
to the antibiotic ampicillin. The host bacterium will
not be able to grow on the test medium, containing
ampicillin, unless the vector had transferred the
ampicillin-resistance gene.
The PCR product was sequenced using M13
forward and reverse universal primers on both strands
and the complete sequence revealed that this gene
consists of 1501 nucleotides (data not shown). Based
on a BLASTN search of GenBank, the complete
sequences of these bacteria share 98% similarity with
Acinetobacter baumannii. This is also confirmed by a
neighbour-joining phylogenetic tree based on the
alignment of 16S rRNA gene sequence of Isolate
Serdang 1 with 16S rRNA sequence of the 22
described Acinetobacter type strains available in
GenBank databases and rooted by using Bacillus.
Based on earlier results, the Isolate Serdang 1 has
been re-designated Acinetobacter baumannii Serdang1
and the complete sequence has been submitted to
GeneBank database under the accession number
EF525671. Acinetobacter spp. are ubiquitous and can
be found in water, soil and living organisms. These are
Gram-negative bacteria, oxidase-negative, non-motile,
The batch kinetic profile shows the variation of
phenol and cell density versus time as depicted in
Figure 2. A decrease in phenol concentration was
concomitant with an increase in cell growth suggesting
that phenol is being assimilated for energy and growth.
There were two phases observed: - the first phase (0-5
days) when cells began to divide and entered a
logarithmic phase with lower phenol removal rate at
48 mg L-1 day-1; and the second phase when cells were
in stationary phase (5-7 days) and the phenolremoval
rate was 130 mg L-1 day-1.
The maximum cell density on day 5 was 8.9 log
CFU/ml corresponding to 66 x 10-7 CFU/ml and the
cell specific growth rate was 0.560 day-1. In this
preliminary study, the time needed for complete
phenol removal at 500 mg/L initial concentration was
7 days, while others have reported 5 days with
Acinetobacter sp. strain W-17 [32]. This shows the
need for identification of important design parameters
for further optimization of phenol removal.
FIGURE 2. Cell growth profile of Acinetobacter baumannii
Serdang 1 at basic conditions; 30°C, pH 7, 100 rpm on
orbital shaker in basic medium with 500 mg/L phenol.
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CONCLUSION
A new indigenous phenol-degrading bacteria strain
from Malaysian soil had been successfully isolated,
characterized and identified. Based on a BLASTN
search of GenBank, the complete sequences of
bacteria shared 98% similarity with Acinetobacter
baumannii. This is confirmed by BiologTM Identification System, sequence alignment and phylogenetic
tree analysis. The Isolate Serdang 1 has been
redesignated Acinetobacter baumannii Serdang1 and
the complete sequence submitted to GeneBank
database under the accession number EF525671.
ACKNOWLEDGMENTS
The authors would like to thank Universiti
Teknologi PETRONAS for the scholarship to Zailatul
Hani Mohamad Yadzir and the research facilities, and
Universiti Putra Malaysia for the research facilities to
carry out microbial and molecular work.
REFERENCES
1. P.M. van Schie, L.Y. Young, Bioremed. 4, 1-18, (2000)
2. G. Cornelissen, D.T.H.M. Sijm, Chemosp. 33, 817-830,
(1993)
3. Y. Zhan, Y. Yan, W. Zhang, M. Chen, W. Lu, S. Ping,
M. Lin, Research in Microbiology,163, 36-43 (2011)
4. P. C. Ignacio, B. Judith, D. Katrin, dos S. Vitor, W.
Christoph, Appl. Microb. Biotechnol., 93, 2279-90
(2012)
5. K. M.Basha, A. Rajendran, and V. T.Velu, Asian J. Exp.
Biol. Sci, 1, 219-234 (2010)
6. C. Amaral, M.S. Lucas, A. Sampaio, Int. J. Biodet
Biodegrad., 68, 45-50 (2012 )
7. H.Liu, Q.J.Yu, G.Wang, F.Ye, Y.Cong, Proc. Biochem.,
46, 1678-1681 (2011)
8. A. Siti, S. Nor, A. Noorliza, K. Gan, M. Shukor,
S.Mohd, World J Microbiol. Biotechnol., 28, 347-352
(2012)
9. Y.Yuanshan, Q. Liping, W. Hui, T. Yuqian, Y. Yigang,
L. Xiaofeng, L. Dongmei, Biodegradation, 22, 613-622
(2011)
10. I. Solyanikova, B. Baskunov, M. Baboshin, A. Saralov,
L. Golovleva, Applied Biochemistry and Microbiology,
48, 21-27 (2012)
11. M. Roberto, P. Enrica, G. Maria, F. Paolo, B. Cristina, G.
Carlo, L. Nicholas, Arch. Microbiol., 188, 55-68 (2007)
12. C.Tu,Y.Teng,Y.Luo,X.Li,X.Sun,Z.Li,W.Liu,P.Christie, J
Hazard Mat.,186, 1438-1444(2011)
13. T. D.H. Bugg, M. Ahmad, E. M. Hardiman, R.Singh,
Curr. Op. Biotechnol., 22, 394-400 (2011)
14. Y.K.Park, J. Y. Choi, D.Shin, K.S. Ko, Int. J.
Antimicrob. Agents, 37, 525-530 (2011).
15. S. Cappello, S. Santisi, R. Calogero, M. Hassanshahian,
M. Yakimov, Water, Air & Soil Poll., 1-8 (2011)
10.1007/s11270-012-1103-y.
16. S.K.Yahya, Z.A. Zakaria, J.Samin, A.S.S.Raj,
W.A.Ahmad, Coll. and Surf B: Biointerfaces, 94, 362368 (2012)
17. A.Sakatoku, M. Wakabayashi, Y. Tanaka, D. Tanaka, S.
Nakamura, Microbiol. Open,1, 2-12 (2012)
18. N.Sood, B.Lal, Chemosphere,70,1445-1451 (2008)
19. J.Dalal, P.M.Sarma, M.Lavania, A.K.Mandal, B.Lal,
Pedobiologia, 54,1,25-30(2010)
20. D. Abd El-Haleem, S. Ripp, C. Scott, G. Sayler, J. Ind.
Microbiol. Biotechnol. 29, 233-237(2002)
21. APHA Standard methods for the examination of water
and wastewater American Public Health Association
17th Edition ,Washington, DC, 1989.
22. J. Cappuccino, N. Sherman, Microbiology: A Laboratory
Manual, Benjamin Cummings, 7th Edition, San
Francisco, CA 94111, 2004.
23. J. Sambrook, E.F. Frittsch, T. Mniatis, Molecular
Cloning: A Laboratory Manual, Cold Spring Harbor
Laboratory, Cold Spring Harbor Laboratory Press 1st
edition, New York, 1989.
24. C.Y. Turenne, L. Tschetter, J. Wolfe, A. Kabani, J.
Clinical Microbiol., 6, 23-26, (2002)
25. D. Higgins, J. Thompson, T. Gibson, J.D. Thompson,
D.G. Higgins, T.J. Gibson, W. Clustal, Nucl. Acid Res.,
22, 4673-4680 (1994)
26. S. Ali, R. Fernandez-Lafuente, D.A. Cowan, Enzym.
Microb. Technol. 23, 462-468, (1998)
27. G.S. Wilson, A.A. Miles, Topley and Wilson’s Principles
of bacteriology and immunity, Baltimore: Williams and
Wilkins, Vol.I, 5th edn., 493, 1964.
28. K.J. Steel, The oxidase reaction as a taxonomic tool,
Gen. Microbiol. 25, 297 (1961)
29. J.M. Klingler, R.P. Stowe, D.C. Obenhuber, T.O.
Groves, S.K. Mishra, D.L. Pierson, Appl. Environ.
Microbiol, 58, 2089-2092 (1992)
30. E. Juni, Genus III. Acinetobacter, Brisou and Prévot
1954, 727AL, Bergey's Manual of Systematic
Bacteriology.(1984) Williams & Wilkins, Baltimore.
31. P. Baumann, M. Doudoroff, R.Y. Stanier,J. Bacteriol.
95, 1520–1541, 1968.
32. L. Dijkshoorn, A. Nemec, H. Seifert.Nature Reviews
Microbiology. 5, 939–951(2007)
33. U.Beshay, D. Abd-El-Haleem, H. Moawad,S.Zaki,
Biotechnol. Lett. 24, 1295-1297 (2002)
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