African Journal of Biotechnology
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African Journal of Biotechnology Vol. 2 (11), pp. 444-447, November 2003
Production and regulation of lignin degrading enzymes from Lentinus squarrosulus (mont.) Singer and Psathyrella atroumbonata Pegler
WUYEP. P. A 1 KHAN, A. U1, AND NOK, A. J.2
1Department of Biological Sciences, Ahmadu Bello University, Zaria, Nigeria. 2Department of Biochemistry, Ahmadu Bello University, Zaria, Nigeria.
*Corresponding author. E-mail: pwuyep@yahoo.com.
Accepted 18 October 2003
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The influence of metal ions on the production and regulation of ligninase and mycelia extension of two type Basidiomycetes (Lentinus squarrosulus and Psathyrella atroumbonata) cultivated on lignocellulose waste was investigated. Mn2+ and Ca2+ ions stimulated growth of both fungi and mycelia extension significantly. Ligninase production increased two to twelve fold under the influence of Mn2+ and Ca2+ ions at concentrations of 20 to 80 mM. Mg2+ and K+ ions did not stimulate growth and extension of fungal mycelia, rather fungal cultures became deactivated after six days. The importance of mycelia extension and enhanced enzyme production has biotechnological applications in wood and pulp, textile and tanning, as well as in oil industries.
Key words: Basidiomycetes, Lentinus squarrosulus, Psathyrella atroumbonata, ligninase, cofactors.
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The unique ability of white-rot basidiomycetes to degrade lignin has become a matter of high interest with the aim of developing environmentally sound biotechnological alternatives to reduce the cost of energy and chemicals, or lowering the environmental impact in pulp paper manufacturing.
Different culture conditions have been employed such as addition of tween detergents (Alexander et al., 1985), use of liquid (with or without agitation) and solid-state fermentations (Kirk et al., 1978; Leisola et. al., 1983). Other conditions involved the use of metal ions, particularly manganese Mn (II), cadmium, mercury, copper and organic acids as precursors (Gold, 1991; Baldrian et al., 2000) to enhance enzyme production and rapid degradability of substrates.
Lentinus squarrosulus and Psathyrella atroumbonata are cultivated edible mushrooms, which can be exploited for their lignin-degrading properties (Fasidi and Kadiri, 1993; Kadiri, 1998). Fungal technology is vital for industrial products such as pharmaceuticals, flavours, organic acids and enzymes, and fungi are also used in bioremediation technology (Wolter et al., 1997).
The aim of this research is to investigate the influence of metal ions as cofactors of enzyme production and mycelia extension in L. squarrosulus and P. atroumbonata through kinetic study and visual estimation of mycelia progress in solid-state fermentation condition.
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Fungal Cultivation
Cultures of L. squarrosulus and P. atroumbonata spores germinated previously (Wuyep, 2001) were maintained on malt extract agar incorporated with 0.0002% NaH2PO4, 0.001% FeSO4.7H2O, 2.0% thiamine hydrochloride, and 2% H3BO3.
Colonization of lignocellulosic waste
Shredded wood (particle size <2 mm) was mixed with distilled water (1:3 w/v) and allowed to soak over night in a refrigerator. 108 hollow glass tubes (length 280 mm, inner diameter 16 mm) were filled with 12 g of wet woodchips, spread horizontally to half of the glass tubes and sealed with cellulose stoppers. The tubes were autoclaved at 121oC for 30 min. The wood chips in the hollow glass tubes were inoculated with an agar plug of L. squarrosulus and P. atroumbonata mycelia. The cultures were incubated at 32oC and growth was monitored for 30 days. To determine the effect of metal ions of growth on fungi, 10 ml solution of 20, 40, 60 and 80 mM of Mn2+, Ca2+, Mg2+ and K+ (in their chloride forms) were added into the wood chip for 48 h to stabilize the medium before inoculation. Each experiment was done in triplicates. A visual estimate of the mycelial length as it colonized the wood chips from the inoculum point, toward the end of the glass tube was recorded every 48 h.
Extraction of crude enzymes
At the end of the experiment, colonized portions of the wood chips were carefully collected into 300 ml Erlenmeyer flasks. 150 ml of 25 mM sodium acetate buffer (pH 5.5) was added and the mixture was homogenized. The contents were later transferred into cheesecloth and then a vice grip which produce a force of 880 Nm2 capable of extruding most of the fluid out of the wood substrate was applied. The exudate was filtered, concentrated with ammonium sulphate to 60% saturation, and dialyzed overnight with 14 kD dialysis tubing against 25 mM sodium acetate (pH 5.5). The dialysate was used to measure ligninase activity using veratryl alcohol as described by Tien and Kirk (1984).
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Average mycelia extension at different levels of metal ions, which was monitored for 30 days for Mn2+ and Ca2+, and six days for Mg2+ and K+ (because the culture became deactivated at the lag phase of growth) (Tables 1 and 2). The mycelia of L. squarrosulus and P. atroumbonata extended longer in the presence of Mn2+ and Ca2+ (20 to 80 mM). However, wood chips degradation in the presence of both fungi reached 35 - 50% with the highest values recorded at higher metal ion concentration 60 - 80mM for Mn2+, and 40 - 60mM for Ca2+. Wood chip degradation was significantly low, about 2 - 5%, in the presence of Mg2+ and K+.
Table 1. Effect of metal ion on mycelia extension (mm) of P. atroumbonata at 32oC at metal ions (mM) concentrations.
Values are means for three replicates.
Table 2. Effect of metal ion on mycelia extension (mm) of L. squarrosulus at 32oC at metal ions (mM) concentrations.
Values are means for three replicates.
Ca2+ caused an increase of up to 20-fold in ligninase activity in the culture of L. squarrosulus at 60 mM (Table 4). At 80 mM Ca2+, there was a drop in ligninase activity. For P. atroumbonata, Ca2+ ion effect on ligninase activity followed a similar pattern with an increase 14-fold at 40mM, followed by a drop at 80 mM.
Table 3. Effect of Mn 2+ ion on the activity (kinetic constants) of ligninase from L. squarrosulus and P. atroumbonata with veratryl alcohol as substrate.
a
= L. squarrosulus
b = P.
atroumbonata
Table 4. Effect of Ca2+ ion on the activity (kinetic constants) of ligninase from L. squarrosulus and P. atroumbonata with veratryl alcohol as substrate.
a
= L. squarrosulus
b = P.
atroumbonata
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The inability of magnesium and potassium ions to support growth of both fungi may be attributed to nutrient composition of the culture which may determine the availability of these metal ions, and the lack of Mg2+-ATPase and K+-ATPase activity at alkaline pH. Magnesium and potassium ions uptake in fungi is slower at neutral pH (Comerford et al., 1985).
The rapid mycelia progress as observed in cultures supplemented with manganese and calcium can be attributed to the uptake of the metal ions and subsequent metabolism. Manganese plays an essential role in lignin biodegradation (Frederic and Gold, 1991). It acts as physiological effectors in cultures of white-rot basidomycetes (Hatakka et al., 1996). The ability of both fungi to grow on low and high concentrations of calcium corroborates the findings of Cooke and Whipps (1993) about improving extracellular enzymes of fungi. However, calcium is yet to be reported to play any role in the catalytic activity of ligninases except that it serves as protein structure stabilizers (Martinez, 2002).
In this work, we demonstrated that enhanced mycelia biomass production is promoted by manganese and calcium ions at high (<40mM) concentrations. This is advantageous to biodegradation and bioremediation technologies as mycelia of white-rot basidiomycetes can be introduced into such system when grown on lignocellulose material or immobilized on other matrix.
ACKNOWLEDGMENT
This study was partially supported by the University Board of Research Grant, Ahmadu Bello University, Zaria, Nigeria. |
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Adler E (1977). Lignin Chemistry Past, Present and Future. Wood Sci. Technol. 11:169 - 218.
Alexander J, Croan S, Kirk TK (1985). Production of Ligninases and Dehydration of Legume in Agitated Submerged Cultures of Phanerochaete chrysosporium. Appl. Environ. Microbiol. 50:1274 - 1278.
Baldrian P, Der Weische CW, Gabriel J, Nerud F, Zadrazil F (2000). Influence of Cadmium and Mercury on Activities of Ligninolytic Enzymes and Degration of Polycyclic Aromatic Hydrocarbons by Pleurotus ostreatus in Soil. Appl. Environ. Microbiol. 66:2471 - 2478. [Pubmed]
Comerford JG, Spancer-Phillips PTH, Janningo DH (1985). Membrane-Bound ATPase Activity, Properties of which are altered by growth condition, isolated from the marine yeast Debaryomyces harsenii. Trans. Br. Mycol. Soc. 89:539 - 550.
Cooke RC, Whipps JM (1993). Resource Acquisition and Utilization in: Ecophyciology of Fungi. Blackwell Scientific Publications. University Press Cambridge, Great Britain. Pp. 46-50.
Fasidi IO, Kadiri M (1993). Use of Agricultural Wastes for the Cultivation of Lentinus subnudus (Polyporales: Polyporaceae) in Nigeria. Rev. Biol. Trop. 41:411 - 415.
Frederic P, Gold MH (1991). Manganese Regulation of Manganese Peroxidase Expression and Lignin Degradation by White-rot Fungus: Dichomitus squalens. Appl. Environ. Microbiol. 57:2240-2245.
Glen JK, Akileswaran L, Gold MH (1986). Mn(11) Oxidation is the principal function of the extracellular Mn-peroxidase from Phanerochaete chrysosporium. Arch. Biochem. Biophys. 251:688-696. [Pubmed]
Hammel KE, Kalyanaraman B, Kirk T (1986). Substrate Free Radicals are intermediates in Ligninase Catalysis. Proc. Natl. Acad. Sci. USA. 83:3708-3712. [Pubmed]
Kawai S, Umezawa T, Higuchi T (1988). Degradation Mechanisms of Phenolic beta-lignin substructure model compounds by Laccase of Coriolus versicolor. Arch. Biochem. Biophy. 262:99-110. [Pubmed]
Kirk TK, Schultz WD, Cinnob LF, Zeikus JG (1978). Influence of Culture Parameters on Lignin Metabolism by Phanerochaete chrysosporium. Arch. Microbiol. 17:227-285.
Leisola M, Ulmer D, Fiechter A (1983). Problem of Oxygen Transfer During Degradation of Lignin by Phanerochaete chrysosporium. Eur. J. Appl. Microbiol. Biotechnol. 17:113-116.
Martinez AT (2002). Molecular Biology and Structure - Function of Lignin Degradation Heme-peroxidases. Enzyme Microb. Technol. 30: 425-444.
Moilanen AM, Lundel T, Vares T, Hatakka A (1996). Manganese and Melonate and individual Regulators for the Production of Lignin and Manganese Peroxidase isozymes and in the Degradation of Lignin by Phlebia radiata. Appl. Microbiol. Biotechnol. 45:722 - 799.
Tien M, Kirk TK (1988). Lignin Peroxidase of Phanerochaete chrysosporium. Methods Enzymol. 1618:238 - 248.
Wolter M, Zadrazil F, Martens R, Bahadir M, (1997). Degradation of Eight Highly Condensed Polycyclic Aromatic Hydrocarbons by Pleurotus sp. Florida in solid wheat straw substrate. Appl. Microbiol. Biotechnol. 48:398 - 404.
Wuyep PA (2001). Studies on the Ligninolytic Activity of Lentinus squarrosulus (Mont.) Singer and Psathyrella atroumbonata Pegler in the Presence of some Co-factors. M.Sc. Thesis, Ahmadu Bello University, Zaria, Nigeria.
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