EXTRACTION
OF XYLAN DEGRADING ENZYME FROM SOIL ISOLATES FOR ITS APPLICATION AS
BIOBLEACHING AGENT IN PAPER PULP PROCESSING
Mohan
Gaanappriya and L. Vijaykumar*
Department
of Biotechnology, Bannariamman Institute of Technology, Sathyamangalam –
638401, Tamil Nadu, India
*
Author for correspondence – microlvk@yahoo.co.in
ABSTRACT
The use of
hemicellulolytic enzymes has recently attracted considerable interest as a
substitute for chlorine chemicals in pulp bleaching in view of the
environmental concerns. Fungal biotechnology opens a potpourri of strains for
identification and secondary metabolite extractions. The present work aims in
extraction of xylanase from novel microorganism(s) for its commercial
application as biobleaching agent in paper and pulp industries. Eight
xylanolytic fungi were isolated for the enzyme production. The culture
conditions for enzyme production were optimized. The optimal enzyme activity
was assayed for the xylanse enzyme. The results of the work were discussed with
related references.
Key Words: Xylanase,
Fungal Biotechnology, Enzyme production, biobleaching
INTRODUCTION
The
past few decades witnessed a drastic change and advances in the lifestyle of
human kind due to the conjoint formulations of science and the human demands.
However, the rapid translation of laboratory findings into real time usage had
posed a threat to the environmental safety and has brought considerable issues
of concern to restore the pace of natural environment. Environmental concerns
have drawn the interests of the biotechnologists to look out for an alternative
way to chemical methods of processing. Advances
in biotechnology and process control, for example,
offer opportunities for
responding to environmental needs, and
energy considerations will play
a role in the
development of such control technologies
as bleach effluent
recycling by concentration
and burning. This outcome has reflected in the field of chemical
technology, where manufacture of a variety of products on large scale has
resulted in serious effluent and hazardous waste disposal problems. Now, the
need for safer and ‘environmental friendly’ technologies has become imminent.
This has now started up the scientists to learn and identify the solutions from
the nature. Finally, the newer field of microbial biotechnology has emerged to
give remedies to the threatening issues. Microbes are capable of performing
multifarious reactions that are biochemically driven, under ambient
environmental conditions with the least or no hazardous effects. Thus, enzymes
are becoming the cornerstones for the biotechnological research, becoming an
alternative strategy to reduce or replace the hazardous polluting chemicals.
(Srinivasan and Meenakshi, 2006)
Xylanases
(1,4-P-D-xylan xylanohydrolase; EC 3.2.1.8) are hemicellulases that hydrolyze
xylan, which is a major constituent of the hemicellulose complex.(Browning,
1963). Viikari et al. (1986), for the first time, demonstrated the usefulness
of xylanase in reducing the consumption of bleach chemicals. Today, the
beneficial effects of xylanase have also been commercially demonstrated in the
pulp and paper industry (Kulkarni et al., 1999, Techapun et al., 2003) The
interest in xylan degrading enzyme and its application in pulp and paper
industries has advanced significantly over the past few years. A survey of
several microorganisms that produce xylanases that could be purified readily
indicated that Fungal strains are potent producers of the enzyme. (Gaanappriya
et al.,2011) The current research article explains the concept of biobleaching
with the use of xyanolytic enzymes as an active bio agent, extracted from the
fungal soil isolates, to replace the conventional bleaching of wood pulp by
chlorine compounds.
The objectives of the
present study were isolation, identification and characterization of xylanase
producing fungi, optimization of cultural conditions for xylanase enzyme
production. A variety of microorganisms were reported to produce endoxylanases,
which can degrade ß -1, 4-xylan in a random fashion, yielding a series of
linear and branched oligosaccharide fragments. The fugal strains were isolated
from soil collected from effluent treatment area of paper mills. Eight strains
were selected and optimized for the production of xylanase enzyme.
MATERIALS AND METHODS
Chemicals and Reagents
M9 Minimal medium was freshly prepared. Potato Dextrose Agar (PDA),
Xylan – from Birch wood, D – xylose , Carboxy Methy cellulose sodium salt, 2-
hydroxy-3,5-dinitrobenzoic acid (DNS), were obtained from Merk. The other
reagents were of analytical grade while the buffers used were freshly prepared
and of analytical grade. Sterilized double distilled water was used through out
the experiment.
M9 Minimal medium preparation
The M9 Salts medium was prepared :
800mL H2O was aliquoted and the following components were added. 64g
Na2HPO4-7H2O, 15g KH2PO4, 2.5g
NaCl and 5.0g NH4Cl. This solution was made up to 1000 mL and
sterilized. The M9 Minimal medium, 200 mL of M9 salts solution, 2 mL of 1M MgSO4 (sterile),
100ul of 1M CaCl2 (sterile), 20 mL of 20% xylan were added and
the final volume was made upto 1000 mL with sterilized, double distilled water.
Increasing the concentration of the xylan in the medium was done to get more
active strains.
Strain Isolation and identification
To 500 mL each of M9 Minimal medium
containing 20 % xylan and 10% xylan respectively, 1 g of soil sample was
inoculated and incubated for three days at 37°C. These samples were then plated
on M9 Minimal agar medium amended with xylan. Enumeration of microbes was done.
Eight strains (X1 – X8) producing xylanase were isolated based on the zone of
clearance formed in xylan – agar plates. The cultures were maintained in PDA
slants.
Enzyme Production
Spores were obtained by culturing the organisms at 28°C in sporulating
medium contained (g/L): Trisodium
citrate 5, KH2PO4
5, NH4NO3 2, (NH4)2SO4
4g, MgSO4 0.2, peptone 1,
yeast extract 2, glucose 2 at pH of 5.5. The sporulating medium was
taken as the inoculating medium. A loopful of cultures were transferred into the enzyme production medium(g/100mL): Glucose 3.0, Bactopeptone 1.0, Urea 0.3, (NH4)2SO4 1.4, MgSO4.7H2O 0.3, CaC12.6H2O 0.3 and Xylan 2.0 for enzyme production. These flasks were incubated at 28°C for 5 days in
static condition
Culture Harvest
Liquid state cultures were harvested by centrifugation at 10,000 × g for 20 min. at 4°C and the resulting
supernatant was called as crude enzyme preparation. The crude enzyme was first saturated up to
30% with solid (NH4)2SO4 and then centrifuged at 5,000 ×
g for 15 min. The supernatant obtained was further saturated up to 70% with
solid (NH4)2SO4
and again centrifuged. The pellets obtained were dissolved in minimum volume of
0.1 M phosphate buffer, pH 6.0.
Partial Purification of Xylanases:
The enzyme was isolated, partially purified and characterized at room
temperature (28 ± 2˚C). The extra cellular xylanase was partially purified from
the culture filtrate when grown on oat spelt xylan. Solid ammonium sulphate was
dissolved to attain initially 35% saturation at 0˚C centrifuged at 12,000 rpm
for 30 min at 4˚C.(Jaganathan et al.,1956)
Total Protien Estimation
Total soluble protein was measured according to Lowry et al., (1951).
Protein concentration was determined using bovine serum albumin (BSA) as a
standard. The protein content of the chromatographic eluant was measured by
monitoring the optical density at 280 nm.
Xylanase Assay
Xylanase activity was measured according to Bailey et al. [1992]. Xylanase activity was assayed using 1% (w/v)
of xylan as a substrate. Reaction
mixture contained I mL of appropriately diluted enzyme and 1% xylan in citrate phosphate buffer. The mixture was incubated at 50
°C for 30 min. The reaction was
terminated by adding 3 mL of dinitrosalysilic acid (DNS) reagent.(Miller,1951). After heating for 5 min in a boiling water
bath and cooling, the absorbance was noted at 550 nm.
Determination of optimal pH, temperature on enzyme
activity
The enzymatic reactions were carried out for 5 min in 3 different
buffers (50 mM): citric acid-Na2HPO4 (pH 5 to 6),
phosphate buffer (pH 6 to 8), Glycine-NaOH buffer (pH 8 to 9.5). The actual pH
in the assay mixture was determined at the reaction temperature. The effect of
temperature on the reaction rate was determined by performing the standard
reaction for 5 min at a temperature range of 55 to 80°C.
RESULTS
AND DISCUSSION
Isolation
and identification of strains:
The soil sample
was inoculated in M9 Minimal medium enriched with xylan (10% and 20%). The
samples were then plated on M9 Minimal agar medium amended with xylan for the
isolation of xylanolytic fungal strains(Fig 1). From the microbial diversity,
eight strains were screened for the production of xylanase enzyme by checking
for the zone of clearance in xylan agar medium. Totally 8 strains were
isolated. These strains were named as X1 – X8.(Fig.2). The strains were
identified based on their morphological characters as follows. However these
identifications do not intend to identify the organisms at the species level.
Purification
of Xylanase
The culture filtrate
was precipitated by fractional (35–80%) ammonium sulphate saturation. Proteins
precipitated within this range had maximum xylanase activity and was used for
purification. (Table 2)
Effect of pH on enzyme activity
Fig.3 shows the pH effect on enzyme activity. It is clear from the
figure that enzymes from Aspergillus strains were most active in the
neutral pH range, between pH 6 to 7.0. For Trichoderma species, the
enzymes were found to be active in ph between 6 to 7, and for Fusarium ,
pH was 6.5 and for the Penicilium species, the optimal pH
was identified in the range of 5 -5.5. At pH above 7.5, the enzyme tends to precipitate in our assay
conditions. Most xylanases known today are active at acidic (John et,al.,
1979) or neutral pHs (Berenger et.al,1985). Hence the pH of the medium was adjusted
to in accord for the growth of the fungal strains respectively in
Vogel’s medium and also in all subsequent experiments. The optimal pH for
fungal enzymes varies from species to species, though in most cases the optimum
pH ranges from 3.0 to 8.0 (Subramaniyan, S and
Prema, P, 2002). A similar observation was reported by Alves-Prado et
al., (2010) for the production of celluloytic enzymes from Neosartorya spinosa.
Effect of Temperature on enzyme activity
Like most chemical reactions, the rate of an enzyme-catalyzed reaction
alters as the temperature is altered. many enzymes are adversely affected by
high temperatures too. Fig. 4 depicts the temperature effect on xylanse
production. A maximum production of xylanase was achieved in the range of
50-55°C for Aspergillus spp. and Fusarium sp, 55 – 65 °C for Penicillium
spp. and below 55°C for Aspergillus species The optimum temperature for celluloses production by T. harzianum
is in accordance with earlier research is 28°C. But in our study a optimum
temperature of 55°C was achieved, which could be reason that the isolated
strain was from a environmental sample. This is in contradictory with those of
earlier worker conducted on C. thermophile (Ganju et al.,1989), and Myceliopthera
thermophila (Zamost et al.,1991) whose reported the optimum temperature for
xylanases produced from these species was 70ºC.
Effect of Time on enzyme activity
The Time factor study showed that a time period of 72 h - 120 h for an
optimum xylanase production by Aspergillus spp, 144 h for Fusarium
sp, 96 – 120 h for Penicillium spp and120 h for Trichoderma spp.
(Fig. 5). The obtained finding was in accordance with earlier reports. The
xylanase from Aspergillus niger recorded the optimal production between 120 –
168h. (Anthony et al., 2005) Similarly A. fumigatus showed maximum production at 120 h of cultivation.(
Ancharida Svarachorn, 1999).
CONCLUSION
Xylanase secretion
often associates with low or high amount of cellulases. Haltrich et al.(1996)
also reported that xylanases were always associated with cellulose. To use
xylanase for pulp treatment, it is preferable to use cellulose-free xylanases,
since the cellulase may adversely affect the quality of the paper pulp. (Ninawe
et al., 2008). Upon eight strains, the strains X4, X5 and X6 were stable at a
higher temperature and neutral pH, enabling the usage of these enzymes for
biobleaching applications. The rest could be used for other applications in
textile industries and food processing industries wherein the process
conditions are at a relatively lower temperature.
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