Puri
fication, characterization and mass spectroscopic analysis
of thermo-alkalotolerant
b
-1, 4 endoxylanase from Bacillus sp.
and its potential for dye decolorization
Monika Mishra, Indu Shekhar Thakur
School of Environmental Sciences, Jawaharlal Nehru University, JNU Campus, New Delhi 110 067, India
a r t i c l e i n f o
Article history:
Received 12 November 2010
Received in revised form
2 December 2010
Accepted 2 December 2010
Available online 31 December 2010
Keywords:
Alkalotolerant
Bacillus sp.
Decolorization
Dyes
Thermostable
Xylanase
a b s t r a c t
A Bacillus sp., isolated from sludge and sediments of pulp and paper mill, was found to produce xylanase in
a synthetic culture media containing oat spelt xylan (1% w/v) and 10% black liquor as inducers along with
2.5% (w/v) sucrose as additional carbon source. The puri
fied enzyme was highly thermostable with half-life
of 10 min at 90
C and pH 8. The enzyme was stable over a broad range of pH (pH 6
e10) and showed good
thermal stability when incubated at 70
C. Chemicals like EDTA, Hg
2
þ
, Cu
2
þ
and solvents like glycerol and
acetonitrile completely inhibited enzyme activity at high concentration. The molecular weights of the
puri
fied enzyme, determined by matrix-assisted laser desorption/ionization coupled with time-of-flight
mass spectrometry (MALDI-TOF/MS) analysis was analogous to the results obtained from SDS-PAGE, i.e.
55 kDa. Kinetic parameters were determined by using oat spelt xylan as substrate. The K
M
and V
max
values
of the enzyme were 4.4 mg/ml and 287 U/mg respectively. At high xylan concentrations (
>70 mg/ml)
a substrate inhibition phenomenon of the enzyme was observed. In addition, crude xylanase showed
enormous potential for decolorization of various recalcitrant dyes.
Ó 2010 Elsevier Ltd. All rights reserved.
1. Introduction
The growing public concern over the environmental impact
of pollutants from paper and pulp industry is the motivating
force behind the search for novel bleaching techniques. Chlorinated
phenolics, chlorinated dehydroabietic acids and polychlorinated
biphenyls are produced from residual lignin during conventional
pulp bleaching (
). Residual Lignin is very
dark in color due to extensive oxidation and modi
fication. Covalent
interaction of lignin with hemicelluloses and cellulose
fibers makes
it very dif
ficult to be removed from pulp (
).
Most of the chloroaromatic compounds released during the pulp
bleaching process e.g. chlorophenols, chlorobiphenyls and other
chlorolignin derivatives such as 2, 3, 7, 8-tetrachlorodibenzo-p-
dioxin, are toxic and accumulate in the biotic and abiotic compo-
nents of the ecosystem (
Bedard et al. 1987; Larsson et al. 1988;
Xylans, with a linear backbone of L-1, 4-linked xylose residues,
form the major group of hemicelluloses present in the wood.
Xylanases are of great importance to pulp and paper industries since
the hydrolysis of xylan facilitates the release of lignin from pulp,
thereby reducing the use of chlorine as a bleaching agent (
). The Kraft pulping process at higher temperatures and
pH ranges necessitates the search for alkalotolerant thermophilic
xylanases.
and
were the
first to demonstrate that xylanases could be useful in the paper and
pulp industry.
Due to xylan heterogeneity, the enzymatic hydrolysis of xylan
requires different enzymatic activities. Two major enzymes,
b
-1,4-
endo-xylanase (EC 3.2.1.8) and
b
-xylosidase (EC 3.2.1.37) are
responsible for hydrolysis of the main chain of xylan. The former one
attackes the internal main-chain xylosidic linkages and the later one
releases xylosyl residues by endwise attack on xylooligosaccharides
(
). These two enzymes, produced by
biodegradative microorganisms such as Trichoderma, Aspergillus,
Schizophyllum, Bacillus, Clostridium and Streptomyces sp., are the
major components of xylanolytic systems (
et al. 1992; Valenzuela et al. 1997
). However, for complete hydro-
lysis of the molecule, side-chain cleaving enzyme activities are
also necessary. Since lignocellulose is an abundant and renewable
resource, we have already used it for the production of countless
artifacts. Today, we are trying to exploit microbial capabilities in
biodegradation to expand our uses of this biomass resource. The use
* Corresponding author. Tel.: þ91 11 2670 4321.
E-mail addresses:
(M. Mishra),
(I.S. Thakur).
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International Biodeterioration & Biodegradation 65 (2011) 301
of microbial enzymes for the industrial hydrolysis of lignocellulose is
advantageous because of the high speci
ficity of enzyme reactions, the
mildness of the reaction conditions, and the absence of substrate
loss due to chemical modi
fications. Hydrolysis products from ligno-
cellulose may be subsequently converted into liquid fuel, single-cell
protein, solvents, and other chemical products by using selected
fermentative microorganisms.
Xylanases have diverse applications including biodegradation
of lignocelluloses in animal feed, foods, and textiles, Kraft pulp
bleaching and biopulping in the pulp and paper industry (
and Schmidt 1982; Viikari et al. 1986; Madlala et al. 2001
). The most
promising application of xylanases is in the prebleaching of pulps,
which could improve pulp
fibrillation and water retention, reduc-
tion of beating times in virgin pulps, restitution of bonding and
increase freeness in recycled
fibers, and removal of xylans from
dissolving pulps (
).
Although xylanases from various microorganisms have been
reported, few of them are alkalotolerant (
Tsujibo et al. 1990; Dey et al. 1992; Kohli et al. 2001; Mamo et al.
2006
). In this study, we describe the culture conditions necessary
for optimal production of alkaline xylanase(s) from Bacillus sp.
reported earlier (
). In addition to partial
puri
fication, characterization and MALDI-TOF spectral analysis of
the extracellular bacterial xylanase have also been carried out.
Furthermore, the application of this xylanase in dye degradation
studies also proved it as a promising bioremediation agent for
treatment of colored wastewaters.
2. Material and methods
2.1. Bacteria and culture condition
The bacterial strain, Bacillus sp., used in this study, was taken
from our previous study (
). Inoculum of
Bacillus sp. was prepared by growing the bacterium overnight in LB
broth. This was inoculated in minimal salt media (MSM) containing
(g/l): Na
2
HPO
4
$2H
2
O, 7.8; KH
2
PO
4
, 6.8; MgSO
4
, 0.2; Fe (CH
3
COO)
3
NH
4
, 0.05; Ca(NO
3
)
2
$4H
2
O, 0.05; NaNO
3
, 0.085; at pH 8
(
) and incubated in a rotary shaker (200 rpm) at 35
C
for 48 h. The growth media was optimized by adding sucrose
(2.5% w/v) as additional carbon sources and oat spelt xylan (1%w/v)
along with black liquor (10%v/v) as xylanase inducer to enhance the
production of xylanase. Xylanase activity was determined after 48 h
of incubation. Cell free culture supernatant was obtained after
centrifugation at 10,000
g for 10 min.
2.2. Enzyme assay
Xylanolytic activity was quantitatively determined using 3, 5-
dinitrosalicyclic acid (DNS) method (
). The assay
was based on the enzymatic hydrolysis of xylan, and the reaction of
the liberated reducing sugar with DNS. Xylose was used as a reference
reducing sugar for preparing a standard curve. One unit of xylanase
activity was de
fined as the quantity of enzyme that released reducing
sugar xylose at the rate of 1
m
M/min at 70
C and pH 8. Protein
estimation of xylanase solution was performed by the Bradford
method using Bovine Serum Albumin as a standard (
2.3. Production and puri
fication of enzyme
The protein puri
fication was carried out at 4
C. The culture
supernatant, after centrifugation (10,000
g for 10 min), was
filtered with 0.2
m
size
filter membrane (millipore). This filtrate
was dialyzed against sucrose to obtain concentrated protein. This
concentrated crude extract was applied to DEAE cellulose ion
exchange column equilibrated with the same buffer used in xylanase
assay. Proteins were eluted with a step gradient of Tris
eCl
(0
e1000 mM) at a flow rate of 0.7 ml/min. Fractions having xylanase
activity were pooled and applied to Sephadex-G100 to determine
molecular weight of the protein by using bovine serum albumin
(66 kDa), ovaalbumin (45 kDa), carbonic anhydrae (31 kDa) and
lysozyme (14 kDa) as molecular marker. Protein samples of 5 ml
were collected at
flow rate of 0.4 ml/min and the absorbance
was measured at 280 nm. Fractions with high protein content were
further checked for xylanase activity. SDS-PAGE was performed
by the method of
with polyacrylamide gel (10%).
The protein bands were stained with Coomassie Brilliant blue R-250
(Sigma) and compared with the molecular weight markers.
2.4. Matrix assisted laser desorption ionization time-of-
flight
mass spectrometry (MALDI-TOF/MS)
The excised protein bands were prepared for MALDI-TOF/MS
analysis by the method of
with some modi
fi-
cations. Excised bands from SDS-PAGE, were digested with trypsin
(200 ng) in 50 mM NH
4
HCO
3
at 37
C for overnight followed by
vacuum drying in a Savant SVC100 Speed Vac and desalting using
C
18
Omix microextraction column tips (Varian, Palo Alto, CA). These
resultant peptides were mixed with matrix solution (
w1.5
m
l)
consisting of 10 mg/ml of alpha-cyano-4-hydroxy-cinnamic acid
(CHCA) in 50% acetonitrile and 0.1% tri
fluoroacetic acid. The samples
were mixed well and spotted onto an Anchor Chip target plate
(Bruker Daltonics Ltd, Coventry, UK) keeping the droplet centered
on the anchor spot (400
m
mol/l target selected). This was kept for
drying, and MALDI mass spectra were obtained using a Bi
flex IV
MALDI-TOF MS (Brucker Daltonics) with a nitrogen laser at 337 nm
following routine calibration. The singly charged peptide
fingerprint
was assigned monoisotopic peptide masses using Biotools software
(Brucker Daltonics). These data were then used to search the NCBI
non-identical protein sequence database using MASCOT software
(Matrix Science), and statistically signi
ficant hits were recorded
together with the number of peptides and percentage coverage of
the protein. Finally, each of the peptides was used to BLAST search
to con
firm that the protein identified by MASCOT was the only
relevant match in the non-redundant protein database for a partic-
ular peptide sequence.
2.5. Characterization and kinetic studies of the enzyme
The puri
fied fractions having xylanase activity were used for
enzyme kinetic studies. Michaelis
eMenten kinetic parameters
(Km and Vmax) were determined using oat spelt xylan as substrate
at concentrations varying from 1.25 mg/ml to 30 mg/ml.
Effect of pH on enzyme stability was estimated by pre-incu-
bating enzyme in buffers at different pH ranging between 4.0 and
10.0. Buffer solutions with different pH values as sodium acetate
(4
e5), sodium phosphate (6e7), TriseHCl (8, 9 and 10) were used.
Half-life of enzyme was calculated by incubating the enzyme along
with assay buffer at different temperatures (50
C
e90
C) for
Table 1
Puri
fication of extracellular xylanase produced by Bacillus sp.
Puri
fication
step
Volume
(ml)
Total
Activity
(U)
Total
Protein
(mg)
Speci
fic
Activity
(U mg
1
)
Yield (%) Fold
Puri
fication
Crude Extract
50
2380
65
37
(100)
(1)
Sucrose Dialysis
30
2118
29
73
89
1.97
DEAE
Chromatography
20
1519
10
152
63.8
4.1
Gel Filteration
10
946
4.3
221
39.7
6.0
M. Mishra, I.S. Thakur / International Biodeterioration & Biodegradation 65 (2011) 301
e308
302
different time intervals (5, 10, 20, 30 and 60 min) to check the
thermo stability of the enzyme. The effects of chemicals like
EDTA, CuSO
4
, HgCl
2
(10
e30 mM) and solvents like acetonitrile and
glycerol (10%, 20%, 30%, 40% and 50%), on the activity of xylanase,
were also determined. Each experiment was repeated twice.
2.6. Application of enzyme in dye decolorization study
While studying the applicability of the enzyme, the cultured
filtrate with higher xylanase activity was used as a source of enzyme
to test its ef
ficiency in decolorization of various synthetic dyes.
The dyes (0.1%w/v), studied for decolorization, were aniline blue
(AB), bromo thymol blue (BTB), crystal violet (CV), brilliant blue R
(BBR), brilliant blue G (BBG), and trypan blue (TB). The enzyme was
incubated with dye in suitable buffer (Tris-Cl) at pH 8 for 2-12 hrs.
in triplicates. The composition of the mixture was 2 ml buffer,
0.5 ml dye solution and 0.5 ml crude enzyme solution, having 2 U
of enzyme in
final volume. The reaction was performed in dark
conditions at 70
C by continuous shaking at 200 rpm. Change in the
spectra (spectral scan from 200 to 800 nm) was observed using Cary
Spectrophotometer. The percentage of dye decolorization achieved
was calculated with reference to the control samples that were not
treated with the enzyme, by measuring the decrease in color at
absorption maxima for particular dyes.
Fig. 1. SDS-PAGE of extracellular Bacillus xylanase puri
fied by anion exchange,
Molecular size markers are indicated in kilodaltons (lane 1), DEAE (lane 2) and
sephadex puri
fied xylanase (lane 3).
Fig. 2. MALDI-TOF-MS analysis of extracellular xylanase puri
fied from Bacillus sp. (a) Peptide sequence coverage of the enzyme found by MS analysis against Bacillus subtilis
b
-1, 4
endoxylanase and matched peptides (in bold letters) are shown (b).
M. Mishra, I.S. Thakur / International Biodeterioration & Biodegradation 65 (2011) 301
e308
303
3. Results and discussion
3.1. Isolation and production of xylanase of Bacillus sp.
Based of the morphological features and DNA sequence of 16S
rDNA, strain was identi
fied as Bacillus sp. and its sequence has been
deposited at Genbank Bethesda, Maryland USA, having accession
number EU741057 (
Xylanase production was enhanced by optimising growth
factors and process parameters of the culture media. Maximum
xylanase production was obtained with MSM containing oat
spelt xylan 1% (w/v), sucrose 2.5% (w/v) and inoculum size 5% (w/v)
along with 10% (v/v) black liquor at pH 8.0. The extracellular
enzyme activity was measurable after 20
e24 h of the onset of
growth in the culture media, having maximum activity at 48 h.
The use of xylanases in pulp and paper industry has increased
appreciably with its discovery by
. The objective
of this study was to isolate, purify and characterize extracellular
xylanase from Bacillus sp. The previously described xylanase
producing bacteria include Bacillus sp. XTR-10, Bacillus amylolique-
faciens, Micrococcus sp., Streptomyces roseiscleroticus NRRL-B-11019,
Cellulomonas uda, Staphylococcus (
and Jeffries 1991; Saxena et al. 1991; Breccia et al. 1998; Gupta
et al. 2000; Saleem et al. 2009
The application of various organisms including fungi and bacteria
for degradation and decolorization of pulp and paper mill ef
fluent
has been studied for more than three decades. The possible mecha-
nism behind degradation of polymers in pulp and paper mill ef
fluent
is the production of enzymes (
). Some reports
have been cited in which ef
fluents such as black liquor from paper
and pulp mill and molasses spent wash from alcohol distillery are
known to induce xylanase production, when used at a concentration
of 1% (v/v) while decolorizing the ef
fluent (
To our knowledge, this study is the
first report where pulp and
paper mill ef
fluent at a concentration of 10% (v/v), was used to induce
xylanase production by Bacillus sp. in the culture supernatant.
3.2. Puri
fication and MALDI-TOF-MS analysis
of xylanase of Bacillus sp.
Using batch culture of the Bacillus sp. in MSM, we were able to
obtain good xylanase activity, around 47 U/ml. Crude xylanase
solution, obtained after 48 hrs, was puri
fied by sucrose dialysis
followed by DEAE anion exchange chromatography and sephadex-
G100 gel
filtration chromatography. This protocol afforded 6 fold
puri
fication of xylanase from the culture filtrate with a yield of
39.7% and speci
fic activity of 221 U/mg (
). Molecular weight
of protein as determined by gel
filtration chromatography was
55 kDa. The puri
fied xylanase produced single band on an SDS-
PAGE gel at a molecular mass of approximately 56 kDa (
). Most
of the studies had reported the molecular weight of the xylanases
in the range 11
e104 kDa (
The puri
fied band of bacterial xylanase was further studied for
MALDI-TOF/MS analysis to determine the molecular weight of the
puri
fied enzyme. These spectra were obtained using a Perseptive
Biosystems DE-PRO MALDI mass spectrometer equipped with
a TOF analyzer operated in positive ion mode. In MALDI-TOF/MS, only
a
finite number of molecules are actually analyzed by the detector.
The peptide sequence obtained by MALDI-TOF analysis was matched
against NCBI database and FASTA protein sequence database (Mascot
search). Our data indicated that enzyme obtained from Bacillus sp. is
xylanase. MALDI spectra are shown in
a. The sequence coverage
of the peptide against the Bacillus subtilis
b
- 1, 4 endoxylanase
reached 20% (
b). Previously some workers have identi
fied
b
- 1,
4 endoxylanase enzyme in B. subtilis and its use in hemicelluloses
degradation (
Kato and Nevins 1984; Yuana et al. 2005
). In this case,
five peptides were found to correspond exactly to internal sequence
of
b
- 1, 4 endoxylanase belonging to B. subtilis (
). The nominal
mass of the homologous protein of B. subtilis was 54,561 daltons.
The molecular weights of the protein, determined by gel
filtration
chromatography, SDS-PAGE and MALDI-TOF/MS were almost similar.
3.3. Characterization of xylanase of Bacillus sp.
The kinetic constants of the puri
fied xylanase were determined
using oat spelt xylan as substrate under optimal assay conditions
through Michaelis
eMenten equation and the apparent K
M
and V
max
values of the enzyme were 4.4 mg/ml and 287 U/mg respectively
(
).
Xylanases are considered to be non-speci
fic for their substrate,
being able to oxidize a wide range of aromatic compounds. In
the present work, oat spelt xylan was used as substrate for
kinetic studies and the enzyme showed typical Michaelis
eMenten
kinetics. The K
M
value for the xylanase is low which shows that
the xylanase has good af
finity with substrate oat spelt xylan. It was
observed that oat spelt xylan at high concentration produces an
inhibitory effect on xylanase activity.
The extracellular xylanase activity was found maximum at pH 8
and it became inactive (20% activity) at pH 4 and 48% active at pH
Table 2
Observed and expected monoisotopic [M
þ H]
þ
masses of selected ions from the tryptic digest of Bacillus sp.
b
-1, 4 endoxylanase.
Expected molecular mass
Observed ion (M/z)
Range
Deviation
Sequence
1262.446
1263.454
434
e446
0.252
TFKANVASALGGK
1300.553
1301.560
121
e133
0.104
WAGASWAPSAAVK
2115.983
2116.990
303
e322
0.005
NPGAFFGGGGNNHHAVFNFR
2457.093
2458.100
451
e474
0.168
LDSANGKLVGTLNVPSTGGTQSWR
3376.752
3377.760
229
e260
0.247
LGPDMTSVAGSASTIDAPFMFEDSGMHKYNGK
r
2
=0.998
Xylan conc.(mg/ml)
0
10
20
30
)
g
m/
ni
m/
M
µ(
yti
vi
tc
a
ci
fi
ce
p
S
0
50
100
150
200
250
300
Vmax(a)=287
Km(b)=4.1
Fig. 3. K
M
and V
max
values of the extracellular xylanase of alkalotolerant Bacillus sp.
isolated from pulp and paper mill ef
fluent and sludge. Data are mean of three inde-
pendent sets of reaction. In
figure K
M
and V
max
values are shown.
M. Mishra, I.S. Thakur / International Biodeterioration & Biodegradation 65 (2011) 301
e308
304
10.0 (
). The optimum temperature for xylanase activity was
70
C (
a), however the xylanase was active over broad range
of temperature (50
C
e90
C). The half lives of the enzyme are
49 min, 46 min, 53 min, 24 min and 10 min at 50
C, 60
C, 70
C,
80
C and 90
C respectively (
This enzyme exhibited high activity and good stability under
alkaline conditions, making it a potent candidate for Kraft pulp
treatment. The use of alkaline active xylanases allows direct enzy-
matic treatment of the alkaline pulp and avoids the cost incurring
and time consuming steps in pH re-adjustment. In particular, alka-
line xylanases which are operationally stable at higher temperature
are more bene
ficial due to savings in cooling cost and time. In
this regard, the present xylanase is expected to be active under
conditions close to those of most mills, i.e. high pH and temperature.
So far, only few xylanases with optimum temperature for activity
exceeding 70
C at or above pH 8 have been reported (
Gessesse and Mamo 1998; Kohli et al. 2001
). Due to better solubility
of xylan under alkaline conditions, alkaline active xylanases may also
find other potential applications in addition to pulp bleaching.
For example, in waste management programs, xylanases can be used
to hydrolyze xylan in industrial and municipal waste. The optimum
pH for xylan hydrolysis is about 5.0 for most of the fungal xylanases,
which are normally stable at pH 2
e9 (
). Application of bacteria in pulp
and paper industries is advantageous over fungi since the later
require acidic growth media.
pH
3
4
5
6
7
8
9
10
11
yti
vi
tc
A
e
vi
t
al
e
R
0
20
40
60
80
100
120
Fig. 4. Effect of pH on xylanase activity at constant temperature 70
C. The X axis
indicates duration in min and Y axis indicates percentage residual activity (Error bars
are standard deviations).
Temperature(ºC)
20
30
40
50
60
70
80
90
100
yti
vi
tc
A
e
vi
t
al
e
R
0
20
40
60
80
100
120
Time(min)
0
10
20
30
40
50
60
70
yti
vi
tc
A
l
a
u
di
se
R
0
20
40
60
80
100
120
50°C
60°C
70°C
80°C
90°C
a
b
Fig. 5. Effect of temperature at constant pH 8, on xylanase activity (a) and calculation
of half life (b), the X axis indicates duration in min and Y axis indicates residual activity.
(90 U/ml of enzyme activity was taken as 100% activity). Error bars are standard
deviations.
conc(mM)
0
5
10
15
20
25
30
35
n
oi
ti
bi
h
nI
%
0
20
40
60
80
100
EDTA
CuSO
4
HgCl
2
% Concentration
0
10
20
30
40
50
60
n
oi
ti
bi
h
nI
%
30
40
50
60
70
80
90
100
110
Glycerol
Acetonitrile
a
b
Fig. 6. Percentage inhibition of xylanase activity by different concentration of HgCl
2
,
CuSO
4
, EDTA (a) and organic solvents (b). (Error bars are standard deviations).
M. Mishra, I.S. Thakur / International Biodeterioration & Biodegradation 65 (2011) 301
e308
305
The dependence of xylanase on pH usually renders a bell-shaped
pro
file. Although xylanase was active over a wide range of temper-
atures, optimum temperature range for xylanase was 50
C
e80
C.
Very less activity (15%) was detected at 30
C and approximately 79%
of activity was retained at 90
C. The optimal temperature range in
fungal xylanases also lies between 30
C
e60
C (
). The xylanase from Bacillus sp. was more thermostable
with half-life of 10 min at 90
C.
HgCl
2
and EDTA at 30 mM concentration could inhibit upto 89%
and 69% of the enzyme activity respectively (
a). In case of
organic solvents, there was complete inhibition by glycerol and
acetonitrile at 50% v/v concentration (
b).
Chemicals like CuSO
4
, EDTA were less effective in inhibiting the
enzyme activity even at a very high concentration (30 mM). Similar
findings were observed for the xylanase from the fungus Aspergillus
cf. niger BCC14405 (
). Acetonitrile had higher
inhibitory effect on xylanase activity as compared to glycerol and
both had strong inhibitory effects with almost complete loss of
enzyme activity at higher concentrations (50%).
3.4. Decolorization of dyes by the enzyme
We selected various synthetic dyes bearing different functional
groups to evaluate decolorization performance of the extracellular
enzyme. The xylanase enzyme showed high decolorization poten-
tial with various dyes at the interval of 2 h, 6 h and 12 h (
Fig. 7. Changes in spectral scan of different dyes after treatment with extracellular xylanase. In this
figure U is untreated; T1 after 2 h; T2 after 12 h and T3 after 24 h.
Table 3
Decolorization of different dyes with extracellular xylanase from Bacillus sp.
Dye
Absorbance maxima (
l
)
% Decolorization
Aniline blue
580
65
1.2
Brilliant blue G (BBG)
582
21
1.8
Brilliant blue R (BBR)
552
75
2.3
Crystal violet
580
48
4.1
Trypan blue
599
77
3.3
Bromo Thymol blue (BTB)
434
70
2.6
M. Mishra, I.S. Thakur / International Biodeterioration & Biodegradation 65 (2011) 301
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306
There was almost complete decolorization of Trypan blue and BBR,
showing more than 77% and 75% decolorization respectively. In
contrast, the original color of the BTB dye changed with the addi-
tion of enzyme which showed increased absorption maxima in
visible range (
Xylanase activity at high temperature may
find potential applica-
tion in treatment of heated industrial ef
fluents. Use of Xylanase
enzyme in decolorization of colored ef
fluent has been studied
previously (
). In present work, we found easy
decolorization of synthetic dyes by crude extracellular xylanase and
the enzyme showed higher degree of decolorization of trypan
blue and BBR. Decolorization of synthetic dyes was achieved with in
2
e12 h by incubating the extracellular enzyme with the dye and
a major reduction in color was seen in initial 2 h in most of the
cases. Dye decolorization attributed to adsorption of the dye on
microorganism surface or biodegradation by enzyme activity. In our
case, decolorization is due to enzyme activity. Microorganisms, fungi
and bacteria are capable of utilizing a variety of complex compounds
including dyes as sole carbon source but only meager data are avail-
able on bacterial breakdown of azo and other dyes. The degradation of
coloring materials is primarily mediated by peroxidases, oxidases and
hydrolases (
Chang and Lin 2000; Verma and Madamwar 2003
). In this
study xylanase is used for the decolorization of different dyes in order
to
find out an environment friendly and cost competitive alternative
for removal of color and dyes in the environment.
4. Conclusion
A new extracellular bacterial xylanase has been puri
fied and
characterized. Results presented in this work indicated that pulp and
paper mill ef
fluent acted as xylanase inducer when added to the
growing culture of Bacillus sp. in MSM along with carbon sources.
A high activity of xylanase was obtained after 48 h of inoculation.
The enzyme possesses broad range of pH and a
flat optimum
temperature curve, thus bearing good thermo stability properties.
Acknowledgement
This paper is supported by the research grants of Department
of Biotechnology and Council of Scienti
fic and Industrial research
(CSIR), Government of India. Author (MM) thanks CSIR for
providing Junior Research Fellowship. We thank Century Pulp and
Paper mill, Lalkuan, Uttarakhand, India for providing ef
fluent and
sludge/sediments during the course of investigation.
References
Ali, M., Sreekrishnan, T.R., 2001. Aquatic toxicity from pulp and paper mill ef
fluents:
a review. Advanced Environmental Research 5, 175
e196.
Bedard, D.L., Haberl, M.L., May, R.J., Brennan, M.J., 1987. Evidence for novel mech-
anisms of polychlorinated biphenyl metabolism in Alcaligenes eutrophus H 850.
Applied Environment Microbiology 53, 1103
e1112.
Beg, Q.K., Kapoor, M., Mahajan, L., Hoondal, G.S., 2001. Microbial xylanases and their
industrial applications: a review. Applied Microbiology and Biotechnology 56,
326
e338.
Bradford, M.M., 1976. A rapid sensitive method for quantitation of microgram
quantities of proteins utilizing the principle of protein-dye binding. Analytical
Biochemistry 72, 248
e254.
Breccia, J.D., Si
fieriz, F., Baigori, M.D., Castro, G.R., Kaul, R.H., 1998. Purification and
characterization of a thermostable xylanase from Bacillus amyloliquefaciens.
Enzyme and Microbial Technology 22, 42
e49.
Chang, J., Lin, Y., 2000. Fed-batch bioreactor strategies for microbial decolorization of
azo dyes using a Pseudomonas lutiola strain. Biotechnology Progress 16, 979
e985.
Chaudhri, S., Thakur, I.S., Goel, R., Johri, B.N., 1988. Puri
fication and characterization
of two thermostable xylanases from Melanocarpus albomyces. Biochemistry
International 17, 563
e575.
Dey, D., Hinge, J., Shendye, A., Rao, M., 1992. Puri
fication and properties of extra-
cellular endoxylanases from alkaliphilic thermophilic Bacillus sp. Canadian
Journal of Microbiology 38, 436
e442.
Gessesse, A., Mamo, G., 1998. Puri
fication and characterization of an alkaline
xylanase from alkaliphilic Micrococcus sp. AR-135. Journal of Industrial Micro-
biology and Biotechnology 20, 210
e214.
Gessesse, A., 1998. Puri
fication and properties of two thermostable alkaline
xylanases from an alkaliphilic Bacillus sp. Applied and Environmental Micro-
biology 64, 3533
e3535.
Grabski, A.C., Jeffries, T.W., 1991. Production, puri
fication and characterization of
L-(1-4)-endoxylanase of Streptomyces roseiscleroticus. Applied and Environ-
mental Microbiology 57, 987
e992.
Gupta, S., Bhushan, B., Hoondal, G.S., 2000. Isolation, puri
fication and character-
ization of xylanase from Staphylococcus sp. SG-13 and its application in
biobleaching of kraft pulp. Journal of Applied Microbiology 88, 325
e334.
Jurasek, L., Paice, M., 1986. Pulp, paper and biotechnology. Chemical Technology 16,
360
e365.
Kato, Y., Nevins, D.J., 1984. Enzymic dissociation of zea shoot cell wall poly-
saccharides
’ III. Purification and partial characterization of an endo-(1-4)-
b
-d-
xylanase from a Bacillus subtilis enzyme preparation. Plant physiology 75,
753
e758.
Kohli, U., Nigam, P., Singh, D., Chaudhary, K., 2001. Thermostable, alkalophilic and
cellulase free xylanase production by Thermoactinomyces thalophilus subgroup
C. Enzyme and Microbial Technology 28, 606
e610.
Krisana, A., Rutchadaporn, S., Jarupan, G., Lily, E., Sutipa, T., Kanyawim, K., 2005.
Endo-1,4-
b
-xylanase B from Aspergillus cf. niger BCC14405 Isolated in Thailand:
puri
fication, characterization and gene isolation. Journal of Biochemistry and
Molecular Biology 38, 17
e23.
Kumar, V., Hassan, M.I., Tomar, A.K., Kashav, T., Nautiyal, J., Singh, S., Singh, T.P.,
Yadav, S., 2009. Proteomic analysis of heparin-binding proteins from human
seminal plasma: a step towards identi
fication of molecular markers of male
fertility. Journal of Bioscience 34, 899
e908.
Laemmli, U.K., 1970. Cleavage of structural proteins during the assembly of the head
of bacteriophage T
4
. Nature 227, 680
e685.
Larsson, A., Anderson, T., Forlin, L., Hardig, J., 1988. Physiological disturbances in
fish
exposed to bleached kraft mill ef
fluents. Water Science and Technology 20,
67
e76.
Madlala, A.M., Bissoon, S., Singh, S., Christov, L., 2001. Xylanase induced reduction of
chlorine dioxide consumption during elemental chlorine-free bleaching of
different pulp types. Biotechnology Letters 23, 345
e351.
Mamo, G., Hatti-Kaul, R., Mattiasson, B., 2006. A thermostable alkaline active endo-
b
-1-4-xylanase from Bacillus halodurans S7: puri
fication and characterization.
Enzyme and Microbial Technology 39, 1492
e1498.
Mishra, M., Thakur, I.S., 2010. Isolation and characterization of alkalotolerant bacteria
and optimization of process parameters for decolorization and detoxi
fication
of pulp and paper mill ef
fluent by Taguchi approach. Biodegradation 21,
967
e978.
Mohn, W.W., Stewart, G.R., 1997. Bacterial metabolism of chlorinated dehy-
droabietic acids occurring in pulp and paper mill ef
fluents. Applied Environ-
mental Microbiology 63, 3014
e3020.
Ohkoshi, A., Kudo, T., Mase, T., Horikoshi, K., 1985. Puri
fication of three types of
xylanases from an alkalophilic Aeromonus sp. Agricultural and Biological Chem-
istry 49, 3037
e3038.
Raghukumar, C., D
’Souza-Ticlo, D., Verma, A.K., 2008. Treatment of colored effluents
with lignin-degrading enzymes: an emerging role of marine-derived fungi.
Critical Reviews in Microbiology 34, 189
e206.
Rapp, P., Wagner, F., 1986. Production and properties of xylan-degrading
enzymes from Cellulomonas uda. Applied Environmental Microbiology 51,
746
e752.
Saleem, M., Tabassum, M.R., Yasmin, R., Imran, M., 2009. Potential of xylanase from
thermophilic Bacillus sp. XTR-10 in biobleaching of wood kraft pulp. Interna-
tional Biodeterioration and Biodegradation 63, 1119
e1124.
Saxena, S., Bahadur, J., Varma, A., 1991. Production and localization of carbox-
ymethylcellulase xylanase and
L
-glucosidase from Cellulomonas and Micro-
coccus spp. Applied Microbiology and Biotechnology 34, 668
e670.
Schwien, U., Schmidt, E., 1982. Improved degradation of monochloro phenols by
a constructed strain. Applied Environmental Microbiology 44, 33
e39.
Shoham, Y., Schwartz, Z., Khasin, A., Gat, O., Zosim, Z., Rosenberg, E., 1992.
Deligni
fication of wood pulp by a thermostable xylanase from Bacillus stear-
othermophilus strain T-6. Biodegradation 3, 207
e218.
Silveira, F.Q.P., Sousa, M.V., Ricart, C.A.O., Milagres, A.M.F., Medeiros, C.L.,
Filho, E.X.F., 1999. A new xylanase from a Trichoderma harzianum strain. Journal
of Industrial Microbiology and Biotechnology 23, 682
e685.
Subramaniyan, S., Prema, P., 2002. Biotechnology of microbial xylanases: enzy-
mology, molecular biology and application. Critical Reviews in Biotechnology
22, 33
e46.
Thakur, I.S., 2004. Screening and identi
fication of microbial strains for removal of
colour and adsorbable organic halogens in pulp and paper mill ef
fluent. Process
Biochemistry 39, 1693
e1699.
Thompson, G., Swain, J., Kay, M., Forster, C.F., 2001. The treatment of pulp and paper
mill ef
fluent: a review. Bioresource Technology 77, 275e286.
Tsujibo, H., Sakamoto, T., Nishino, N., Hasegawa, T., Inamori, Y., 1990. Puri
fication
and properties of three types of xylanases produced by an alkalophilic
actinomycete. Journal of Applied Bacteriology 69, 398
e405.
Valenzuela, J., Bumann, U., Cespedes, R., Padilla, L., Gonzalez, B., 1997. Degradation
of chlorophenols by Alcaligenes eutrophus JMP134 (pJ4) in bleached Kraft mill
ef
fluent. Applied Environmental Microbiology 63, 227e232.
M. Mishra, I.S. Thakur / International Biodeterioration & Biodegradation 65 (2011) 301
e308
307
Verma, P., Madamwar, D., 2003. Decolorization of synthetic dyes by newly isolated strain
of Serratia marcescens. World Journal of Microbiology and Biotechnology 19, 615
e618.
Viikari, L., Panua, M., Kantelinen, A., Sundquist, J., Linko, M., 1986. Bleaching with
enzymes. In Proceedings of the Third International Conference on Biotech-
nology in the Pulp and Paper Industry, Stockholm, pp. 67
e69.
Yang, J.L., Lou, G., Eriksson, K.E.L., 1992. The impact of xylanase on bleaching of kraft
pulps. TAPPI Journal 75, 95
e101.
Yuana, X., Wanga, J., Yao, H., Venanta, N., 2005. Separation and identi
fication of
endoxylanases from Bacillus subtilis and their actions on wheat bran insoluble
dietary
fibre. Process Biochemistry 40, 2339e2343.
M. Mishra, I.S. Thakur / International Biodeterioration & Biodegradation 65 (2011) 301
e308
308