Bioelectrocatalytic properties of lignin peroxidase from Phanerochaete chrysosporium in reactions with phenols, catechols and lignin-model compounds

Bioelectrocatalytic reduction of H(2)O(2) catalysed by lignin peroxidase from Phanerochaete chrysosporium (LiP) was studied with LiP-modified graphite electrodes to elucidate the ability of LiP to electro-enzymatically oxidise phenols, catechols, as well as veratryl alcohol (VA) and some other high-redox-potential lignin model compounds (LMC). Flow-through amperometric experiments performed at +0.1 V vs. Ag|AgCl demonstrated that LiP displayed significant bioelectrocatalytic activity for the reduction of H(2)O(2) both directly (i.e., in direct electron transfer (ET) reaction between LiP and the electrode) and using most of studied compounds acting as redox mediators in the LiP bioelectrocatalytic cycle, with a pH optimum of 3.0. The bioelectrocatalytic reduction of H(2)O(2) mediated by VA and effects of VA on the efficiency of bioelectrocatalytic oxidation of other co-substrates acting as mediators were investigated. The bioelectrocatalytic oxidation of phenol- and catechol derivatives and 2,2'-azino-bis(3-ethyl-benzothiazoline-6-sulphonate) by LiP was independent of the presence of VA, whereas the efficiency of the LiP bioelectrocatalysis with the majority of other LMC acting as mediators increased upon addition of VA. Special cases were phenol and 4-methoxymandelic acid (4-MMA). Both phenol and 4-MMA suppressed the bioelectrocatalytic activity of LiP below the direct ET level, which was, however, restored and increased in the presence of VA mediating the ET between LiP and these two compounds. The obtained results suggest different mechanisms for the bioelectrocatalysis of LiP depending on the chemical nature of the mediators and are of a special interest both for fundamental science and for application of LiP in biotechnological processes as solid-phase bio(electro)catalyst for decomposition/detection of recalcitrant aromatic compounds.     

Escherichia coli expression and in vitro activation of a unique ligninolytic peroxidase that has a catalytic tyrosine residue

Heterologous expression of Trametes cervina lignin peroxidase (LiP), the only basidiomycete peroxidase that has a catalytic tyrosine, was investigated. The mature LiP cDNA was cloned into the pET vector and used to transform Escherichia coli. Recombinant LiP protein accumulated in inclusion bodies as an inactive form. Refolding conditions for its in vitro activation—including incorporation of heme and structural Ca²⁺ ions, and formation of disulfide bridges—were optimized taking as a starting point those reported for other plant and fungal peroxidases. The absorption spectrum of the refolded enzyme was identical to that of wild LiP from T. cervina suggesting that it was properly folded. The enzyme was able to oxidize 1,4-dimethoxybenzene and ferrocytochrome c confirming its high redox potential and ability to oxidize large substrates. However, during oxidation of veratryl alcohol (VA), the physiological LiP substrate, an unexpected initial lag period was observed. Possible modification of the enzyme was investigated by incubating it with H₂O₂ and VA (for 30 min before dialysis). The pretreated enzyme showed normal kinetics traces for VA oxidation, without the initial lag previously observed. Steady-state kinetics of the pretreated LiP were almost the same as the recombinant enzyme before the pretreatment. Moreover, the catalytic constant (k_cat) for VA oxidation was comparable to that of wild LiP from T. cervina, although the Michaelis–Menten constant (K_m) was 8-fold higher. The present heterologous expression system provides a valuable tool to investigate structure–function relationships, and autocatalytic activation of the unique T. cervina LiP.     

2-Chloro-1,4-Dimethoxybenzene as a Novel Catalytic Cofactor for Oxidation of Anisyl Alcohol by Lignin Peroxidase

2-Chloro-1,4-dimethoxybenzene (2Cl-14DMB) is a natural compound produced de novo by several white rot fungi. This chloroaromatic metabolite was identified as a cofactor superior to veratryl alcohol (VA) in the oxidation of anisyl alcohol (AA) by lignin peroxidase (LiP). Our results reveal that good LiP substrates, such as VA and tryptophan, are comparatively poor cofactors in the oxidation of AA. Furthermore, we show that a good cofactor does not necessarily serve a role in protecting LiP against H₂O₂ inactivation. 2Cl-14DMB was not a direct mediator of AA oxidation, since increasing AA concentrations did not inhibit the oxidation of 2Cl-14DMB at all. However, the high molar ratio of anisaldehyde formed to 2Cl-14DMB consumed, up to 13:1, indicates that a mechanism which recycles the cofactor is present.     

Immobilization of lignin peroxidase on nanoporous gold: Enzymatic properties and in situ release of H2O2 by co-immobilized glucose oxidase

Immobilization of enzymes on porous inorganic materials is very important for biocatalysis and biotransformation. In this paper, nanoporous gold (NPG) was used as a support for lignin peroxidase (LiP) immobilization. NPG with a pore size of 40–50 nm was prepared by dealloying Au/Ag alloy (50:50 wt%) for 17 h. By incubation with LiP aqueous solution, LiP was successfully immobilized on NPG. The optimal temperature of the immobilized LiP was ca. 40, 10 °C higher than that of free LiP. After 2 h incubation at 45 °C, 55% of the initial activity of the immobilized LiP was still retained while the free LiP was completely deactivated. In addition, a high and sustainable LiP activity was achieved via in situ release of H₂O₂ by a co-immobilized glucose oxidase. The present co-immobilization system was demonstrated to be very effective for LiP-mediated dye decolourization.     

Fungal biodegradation and enzymatic modification of lignin

Lignin, the most abundant aromatic biopolymer on Earth, is extremely recalcitrant to degradation. By linking to both hemicellulose and cellulose, it creates a barrier to any solutions or enzymes and prevents the penetration of lignocellulolytic enzymes into the interior lignocellulosic structure. Some basidiomycetes white-rot fungi are able to degrade lignin efficiently using a combination of extracellular ligninolytic enzymes, organic acids, mediators and accessory enzymes. This review describes ligninolytic enzyme families produced by these fungi that are involved in wood decay processes, their molecular structures, biochemical properties and the mechanisms of action which render them attractive candidates in biotechnological applications. These enzymes include phenol oxidase (laccase) and heme peroxidases [lignin peroxidase (LiP), manganese peroxidase (MnP) and versatile peroxidase (VP)]. Accessory enzymes such as H₂O₂-generating oxidases and degradation mechanisms of plant cell-wall components in a non-enzymatic manner by production of free hydroxyl radicals (·OH) are also discussed.     

Calculated ionisation potentials determine the oxidation of vanillin precursors by lignin peroxidase

In view of the biocatalytic production of vanillin, this research focused on the lignin peroxidase (LiP) catalysed oxidation of naturally occurring phenolic derivatives: O-methyl ethers, O-acetyl esters, and O-glucosyl ethers. The ionisation potential (IP) of a series of model compounds was calculated and compared to their experimental conversion by LiP, defining a relative IP threshold of approximately 9.0 eV. Based on this threshold value only the O-acetyl esters and glucosides of isoeugenol and coniferyl alcohol would be potential LiP substrates. Both O-acetyl esters were tested and were shown to be converted to O-acetyl vanillin in molar yields of 51.8 and 2.3%, respectively.     

Catalytic activity of lignin peroxidase and partition of veratryl alcohol in AOT/isooctane/toluene/water reverse micelles

The activity of lignin peroxidase (LiP) and the partition of its optimum substrate veratryl alcohol (VA) in sodium bis(2-ethylhexyl)sulfosuccinate (AOT)/isooctane/toluene/water reverse micelles were studied in this paper to understand the microheterogeneous effect of the medium on the catalytic properties of LiP hosted in the reverse micelle. Results showed that LiP from Phanerochaete chrysosporium could express its activity in the reverse micelles, but its activity depended, to a great extent, on the composition of the reverse micelles. Optimum activity occurred at a molar ratio of water to AOT (ω₀) of 11, a pH value of 3.6, and a volume ratio of isooctane to toluene of 7–9. Under optimum conditions, the half-life of LiP was circa 12 h. The dependence of LiP activity on the volume fraction of water in the medium (θ), at a constant ω₀ value of 11, indicated that VA was mainly solubilized in the pseudophase of the reverse micelle. Based on the pseudobiphasic model and the corresponding kinetic method, a linear line can be obtained in a plot of apparent Michaelis constant of VA vs θ, and the partition coefficient of VA between the pseudophase and the organic solvent phase was determined to be 35.8, which was higher than that (22.3) between bulk water and the corresponding mixed organic solvent. H₂O₂ inhibited LiP at concentrations higher than 80 μM; this concentration value seems to be different from that in aqueous solution (about 3 mM). The differences mentioned above should be ascribed to the microheterogeneity and the interface of the AOT reverse micelle.     

Removal of Aroclor 1254 by the white rot fungus Coriolus versicolor in the presence of different concentrations of Mn(IV)oxide

Lignin peroxidase (LiP) plays an active role in the biodegradation of lignin and phenolic structures resembling lignin. The role of other enzymes in the biodegradation of recalcitrant compounds, e.g. manganese(II)-peroxidase, is uncertain. Solid manganese(IV)oxide addition improved the production of manganese(II)-dependant peroxidase (MnP) and H₂O₂ and increased the rate of biodegradation of Aroclor 1254 in a nitrogen-limited medium by the white rot fungus Coriolus versicolor. MnP activity was detected 48 h after the addition of MnO₂ to the cultures and was absent in cultures that did not receive MnO₂. The rate of Aroclor 1254 removal by C. versicolor was influenced by the concentration of MnO₂. 34.5 mM concentrations only increased the H₂O₂ production. Removal of Aroclor 1254 in the absence of MnO₂ still took place which implied the presence of (LiP) or nonspecific absorption. The cultures containing 57.5 mM MnO₂ removed ca. 84% of the initial 750 mg l⁻¹ Aroclor in 6 days of incubation. Cultures with no MnO₂ and 34.5 mM removed 79 and 76%, respectively. Cultures with MnP or LiP as the dominant enzyme species removed penta- and hexachlorobiphenyls at a slower rate than tri- and tetrachlorobiphenyl.     

Peroxidation of linoleic acid during the oxidation of phenols by fungal laccase

A system comprising laccase and a suitable phenol such as 4-hydroxybenzoic acid (HBA) or synthetic lignin (DHP) exhaustively peroxidized linoleic acid in acetate buffer. The presence of phenols in lignin was essential since an exhaustively methylated preparation of the same lignin did not support peroxidation. The peroxidation rate was greatly enhanced by Mn²⁺, which was oxidized to Mn³⁺ by laccase/HBA, whereas H₂O₂ inhibited strongly due to rapid reduction of Mn³⁺ by H₂O₂ with concomitant formation of O₂. When acetate was replaced by Mn³⁺–chelating oxalate or malonate, there was no change in peroxidation rates in the absence of Mn²⁺, whereas strong inhibition was observed in the presence of Mn²⁺. In case of malonate part of the inhibition was due to H₂O₂ formation as a result of Mn³⁺ reduction by malonate. These findings suggest that laccase may contribute to fungal lipid peroxidation in vivo thus expanding its role in the biodegradation of lignin and other recalcitrant aromatic compounds.     

Degradation of glyphosate and other pesticides by ligninolytic enzymes

The ability of pure manganese peroxidase (MnP), laccase, lignin peroxidase (LiP) and horseradish peroxidase (HRP) to degrade the widely used herbicide glyphosate and other pesticides was studied in separate in vitro assays with addition of different mediators. Complete degradation of glyphosate was obtained with MnP, MnSO₄ and Tween 80, with or without H₂O₂. In the presence of MnSO₄, with or without H₂O₂, MnP also transformed the herbicide, but to a lower rate. Laccase degraded glyphosate in the presence of (a) 2,2′-azino-bis(3-ethylbenzthiazoline-6-sulphonic acid) (ABTS), (b) MnSO₄ and Tween 80 and (c) ABTS, MnSO₄ and Tween 80. The metabolite AMPA was detected in all cases where degradation of glyphosate occurred and was not degraded. The LiP was tested alone or with MnSO₄, Tween 80, veratryl alcohol or H₂O₂ and in the HRP assay the enzyme was added alone or with H₂O₂ in the reaction mixture. However, these enzymes did not degrade glyphosate. Further experiments using MnP together with MnSO₄ and Tween 80 showed that the enzyme was also able to degrade glyphosate in its commercial formulation Roundup^® Bio. The same enzyme mixture was tested for degradation of 22 other pesticides and degradation products present in a mixture and all the compounds were transformed, with degradation percentages ranging between 20 and 100%. Our results highlight the potential of ligninolytic enzymes to degrade pesticides. Moreover, they suggest that the formation of AMPA, the main metabolite of glyphosate degradation found in soils, can be a result of the activity of lignin-degrading enzymes.     

The roles of veratryl alcohol and nonionic surfactant in the oxidation of phenolic compounds by lignin peroxidase

Veratryl alcohol (VA) at higher concentration stimulated the lignin peroxidase (LiP)-catalyzed oxidation of phenolic compounds remarkably. This novel phenomenon was due to its competition with the phenols for the active site of the enzyme and to the high reactivity of the formed cation radical of VA (VA+*) which resulted in an additional oxidation of the phenols. The influence of the nonionic surfactant Tween 80 on the VA-enhanced LiP-catalyzed oxidation of phenols depended on its concentration. At lower concentration it had a small synergetic effect but at higher concentration it decreased the initial rate. Studies of the capillary electrophoretic behavior of LiP in the presence of Tween 80 showed that this effect was caused by the surfactant aggregation on LiP which, at higher surfactant concentrations, might impede the access of VA to its binding site on LiP and, consequently, the VA+* formation.     

Purification and biochemical characterization of two extracellular peroxidases from Phanerochaete chrysosporium responsible for lignin biodegradation

Two extracellular peroxidases from Phanerochaete chrysosporium, namely a lignin peroxidase (LiP) and manganese peroxidase (MnP), were purified simultaneously by applying successively, ultrafiltration, ion-exchange and gel filtration chromatography. LiP and MnP have a molecular mass of 36 and 45 kDa, respectively. The optimal pHs for LiP and MnP activities were 3.0 and 4.5, respectively. Both peroxidases showed maximal activity at 30 °C and moderate thermostability. MnP activity was strongly inhibited by Fe²⁺, Zn²⁺, Mg²⁺ and Hg²⁺, and enhanced by Mn²⁺, Ca²⁺ and Cu²⁺. LiP activity was enhanced by Ca²⁺, Na⁺ and Co²⁺ and it was inhibited in the presence of K⁺, Hg⁺, Fe²⁺, Mg²⁺ and high concentrations of Cu²⁺ and Zn²⁺. The K_m and V_max for LiP toward veratryl alcohol as a substrate were 0.10 mM and 15.2 U mg⁻¹, respectively and for MnP toward Mn²⁺, they were respectively 0.03 mM and 25.5 U mg⁻¹. The two peroxidases were also able to break down rice lignin in a small-scale solid state treatment system. Data suggest these two peroxidases may be considered as potential candidates for the development of enzyme-based technologies for lignin degradation.     

Purification and characterization of peroxidases from the dye-decolorizing fungus Bjerkandera adusta

A peroxidase oxidizing Mn²⁺ (MnP) is described for the first time in Bjerkandera adusta, a fungus efficiently degrading xenobiotic compounds. The MnP appeared as two isoenzymes, which were purified to homogeneity together with two lignin peroxidases (LiP). Their N-terminal sequences were identical, but the MnP isoenzymes showed more basic isoelectric points and differences in amino acid composition and catalytic properties. The B. adusta LiP is similar to LiP from Phanerochaete chrysosporium. However, the interest of the MnP described here is related to its ability to catalyze Mn²⁺-mediated as well as Mn²⁺-independent reactions on aromatic compounds, which may be of use for applications in biotechnology and environmental technology.     

Pretreatment of empty palm fruit bunch for production of chemicals via catalytic pyrolysis

The effect of chemical pretreatments using NaOH, H₂O₂, and Ca(OH)₂ on Empty Palm Fruit Bunches (EPFB) to degrade EPFB lignin before pyrolyis was investigated. Spectrophotometer analysis proved consecutive addition of NaOH and H₂O₂ decomposed almost 100% of EPFB lignin compared to 44% for the Ca(OH)₂, H₂O₂ system while NaOH and Ca(OH)₂ used exclusively could not alter lignin much. Next, the pretreated EPFB was catalytically pyrolyzed. Experimental results indicated the phenolic yields over Al-MCM-41 and HZSM-5 catalysts were 90 wt% and 80 wt%, respectively compared to 67 wt% yield for the untreated sample under the same set of conditions. Meanwhile, the experiments with HY zeolite yielded 70 wt% phenols.     

Oxidation of monomethoxylated aromatic compounds by lignin peroxidase: role of veratryl alcohol in lignin biodegradation

Lignin peroxidase (LiP), an extracellular heme enzyme from the lignin-degrading fungus Phanerochaete chrysosporium, catalyzes the H2O2-dependent oxidation of a variety of nonphenolic lignin model compounds. The oxidation of monomethoxylated lignin model compounds, such as anisyl alcohol (AA), and the role of veratryl alcohol (VA) in LiP reactions were studied. AA oxidation reached a maximum at relatively low H2O2 concentrations, beyond which the extent of the reactions decreased. The presence of VA did not affect AA oxidation at low molar ratios of H2O2 to enzyme; however, at ratios above 100, the presence of VA abolished the decrease in AA oxidation. Addition of stoichiometric amounts of AA to LiP compound II (LiPII) resulted in its reduction to the native enzyme at rates that were significantly faster than the spontaneous rate of reduction, indicating that AA and other monomethoxylated aromatics are directly oxidized by LiP, albeit slowly. Under steady-state conditions in the presence of excess H2O2 and VA, a visible spectrum for LiPII was obtained. In contrast, under steady-state conditions in the presence of AA a visible spectrum was obtained for LiPIII*, a noncovalent complex of LiPIII and H2O2. AA competitively inhibited the oxidation of VA by LiP; the Ki for AA inhibition was 32 microM. Addition of VA to LiPIII* resulted in its conversion to the native enzyme. In contrast, AA did not convert LiPIII* to the native enzyme; instead, LiPIII* was bleached in the presence of AA. Thus, AA does not protect LiP from inactivation by H2O2.(ABSTRACT TRUNCATED AT 250 WORDS)     

Enzymatic demethylation of lignin for potential biobased polymer applications

Lignin is a highly methylated, recalcitrant biopolymer available aplenty in nature, and is highly heteropolymer in nature, but yet it has been an under-utilized biopolymer. Modifying it chemically, biologically or enzymatically could render it a good candidate for phenol formaldehyde resin or into fine chemicals, fuels, and plastics applications. Lignin demethylation is facilitated by the enzymes called the O-demethylases, which are able to strip-off of the –OCH₃ group in lignin, that give rise to the more widely accessible phenolic hydroxyls groups. Biological demethylation of lignins can be accomplished by means of the microorganisms, such as the white-rot, soft-rot and brown-rot fungi, besides some species of bacteria. Although the enzymes responsible for the lignin demethylation process have not been identified and purified adequately, it is perhaps possible that the O-demethylases, which have the ability to remove the O-methyl groups at the C-3 and (or) C-4 positions of the benzyl ring of low molecular weight lignin-like model compounds (LMCs) and lignin makes them the suitable candidate. These LMCs resemble the aromatic moieties inherent in the molecular structure of lignins, such as the vanillate, syringate, and veratrate. Thus, these enzymes are known as vanillate-O-demethylases, syringate O-demethylases, veratrate O-demethylases and Tetrahydrofolate (THF)-dependent O-demethylase (LigM), respectively. Whereas, some ligninolytic enzymes are known to cause damage to the structure of lignins (e.g., laccases, manganese-dependent peroxidase and lignin peroxidases). The O-demethylase enzymes are believed to be capable of removing the O-methyl groups from the lignins without affecting the complex backbone structure of the lignins. The mechanism of action of O-demethylases on lignin degradation is still largely unexplored, and their ability to remove the O-methyl groups from lignins has not been elucidated sufficiently. In this review, the recent advances made on the molecular approaches in the lignin demethylation (O-demethylases and ligninolytic enzymes), degradation and the probable strategies to tone up the lignin quality have been discussed in detail. The demethylation process of lignins by means of enzymes is envisaged to open up new vistas for its application as a biopolymer in various bioprocess and biorefinery process.     

Hyperactivation and thermostabilization of <Emphasis Type="Italic">Phanerochaete chrysosporium</Emphasis> lignin peroxidase by immobilization in xerogels

This is a continuation of our previous paper on production of lignin peroxidase (LiP) by Phanerochaete chrysosporium in solid substrate fermentation (SSF) medium of corncobs. The enzyme was purified by ammonium sulphate precipitation and ion-exchange fast protein liquid chromatography. Maximum yield of LiP was 13.7 U/gds (units per gram dry substrate) after 5 days of SSF with 70% moisture and 20% (v/w) inoculum. The approximate molecular mass of purified LiP, estimated by sodium dodecyl sulphate-polyacrylamide gel electrophoresis, was 38 kDa. The pH and temperature optima for the LiP were 4 and 40°C, respectively. Immobilization of LiP in hydrophobic xerogels caused hyperactivation of LiP and enhanced its thermostability properties. The K _M and V _max values for immobilized LiP were 10.56 mg/ml and 16.67 μmol/min (120.49 U/mg of protein) as compared to 13 mg/ml and 11.76 μmol/min (85 U/mg of protein), respectively, for free LiP using veratryl alcohol as substrate.     

Production of lignocellulose-degrading enzymes employing <Emphasis Type="Italic">Fusarium solani</Emphasis> F-552

In this work, capability of Fusarium solani F-552 of producing lignocellulose-degrading enzymes in submerged fermentation was investigated. The enzyme cocktail includes hydrolases (cellulases, xylanases, and proteinases) as well as ligninolytic enzymes: manganese-dependent peroxidase (MnP), lignin peroxidase (LiP), and laccase (Lac). To our knowledge, this is the first report on production of MnP, LiP, and Lac together by one F. solani strain. The enzyme productions were significantly influenced by application of either lignocellulosic material or chemical inducers into the fermentation medium. Among them, corn bran significantly enhanced especially productions of cellulases and xylanases (248 and 170 U/mL, respectively) as compared to control culture (11.7 and 29.2 U/mL, respectively). High MnP activity (9.43 U/mL, control 0.45 U/mL) was observed when (+)-catechin was applied into the medium, the yield of LiP was maximal (33.06 U/mL, control 2.69 U/mL) in gallic acid, and Lac was efficiently induced by, 2,2′-azino-bis-[3-ethyltiazoline-6-sulfonate] (6.74 U/mL, not detected in control). Finally, in order to maximize the ligninolytic enzymes yields, a novel strategy of introduction of mild oxidative stress conditions caused by hydrogen peroxide into the fermentation broth was tested. Hydrogen peroxide significantly increased activities of MnP, LiP, and Lac which may indicate that these enzymes could be partially involved in stress response against H₂O₂. The concentration of H₂O₂ and the time of the stress application were optimized; hence, when 10 mmol/L H₂O₂ was applied at the second and sixth day of cultivation, the MnP, LiP, and Lac yields reached 21.67, 77.42, and 12.04 U/mL, respectively.     

Degradation of the herbicide bentazon as related to enzyme production by Phanerochaete chrysosporium in two solid substrate fermentation systems

Enzyme production and degradation of the herbicide bentazon by Phanerochaete chrysosporium growing on straw (solid substrate fermentation, SSF) and the effect of nitrogen and the hydraulic retention time (HRT) were studied using a small bioreactor and batch cultures. The best degradation of bentazon was obtained in the low nitrogen treatments, indicating participation of the ligninolytic system of the fungus. The treatments that degraded bentazon also had manganese peroxidase (MnP) activity, which seemed to be necessary for degradation. Pure MnP (with Mn(II) and H₂O₂) did not oxidize bentazon. However, in the presence of MnP, Mn(II) and Tween 80, bentazon was slowly oxidized in a H₂O₂-independent reaction. Bentazon was a substrate of pure lignin peroxidase (LiP) and was oxidized significantly faster (22,000–29,000 times) as compared to the MnP-Tween 80 system. Although LiP was a better enzyme for bentazon oxidation in vitro, its role in the SSF systems remains unclear since it was detected only in treatments with high nitrogen and high HRT where no degradation of bentazon occurred. Inhibition of LiP activity may be due to phenols and extractives present in the straw.     

Mycoremediation (bioremediation with fungi) – growing mushrooms to clean the earth

Abstract

Some of the prospects of using fungi, principally white-rot fungi, for cleaning contaminated land are surveyed. That white-rot fungi are so effective in degrading a wide range of organic molecules is due to their release of extra-cellular lignin-modifying enzymes, with a low substrate-specificity, so they can act upon various molecules that are broadly similar to lignin. The enzymes present in the system employed for degrading lignin include lignin-peroxidase (LiP), manganese peroxidase (MnP), various H₂O₂ producing enzymes and laccase. The degradation can be augmented by adding carbon sources such as sawdust, straw and corn cob at polluted sites.