Role of manganese peroxidases and lignin peroxidases of Phanerochaete chrysosporium in the decolorization of kraft bleach plant effluent.

The role of lignin peroxidases (LIPs) and manganese peroxidases (MNPs) of Phanerochaete chrysosporium in decolorizing kraft bleach plant effluent (BPE) was investigated. Negligible BPE decolorization was exhibited by a per mutant, which lacks the ability to produce both the LIPs and the MNPs. Also, little decolorization was seen when the wild type was grown in high-nitrogen medium, in which the production of LIPs and MNPs is blocked. A lip mutant of P. chrysosporium, which produces MNPs but not LIPs, showed about 80% of the activity exhibited by the wild type, indicating that the MNPs play an important role in BPE decolorization. When P. chrysosporium was grown in a medium with 100 ppm of Mn(II), high levels of MNPs but no LIPs were produced, and this culture also exhibited high rates of BPE decolorization, lending further support to the idea that MNPs play a key role in BPE decolorization. When P. chrysosporium was grown in a medium with no Mn(II), high levels of LIPs but negligible levels of MNPs were produced and the rate and extent of BPE decolorization by such cultures were quite low, indicating that LIPs play a relatively minor role in BPE decolorization. Furthermore, high rates of BPE decolorization were seen on days 3 and 4 of incubation, when the cultures exhibit high levels of MNP activity but little or no LIP activity. These results indicate that MNPs play a relatively more important role than LIPs in BPE decolorization by P. chrysosporium.     

Role of manganese peroxidases and lignin peroxidases of Phanerochaete chrysosporium in the decolorization of kraft bleach plant effluent.

The role of lignin peroxidases (LIPs) and manganese peroxidases (MNPs) of Phanerochaete chrysosporium in decolorizing kraft bleach plant effluent (BPE) was investigated. Negligible BPE decolorization was exhibited by a per mutant, which lacks the ability to produce both the LIPs and the MNPs. Also, little decolorization was seen when the wild type was grown in high-nitrogen medium, in which the production of LIPs and MNPs is blocked. A lip mutant of P. chrysosporium, which produces MNPs but not LIPs, showed about 80% of the activity exhibited by the wild type, indicating that the MNPs play an important role in BPE decolorization. When P. chrysosporium was grown in a medium with 100 ppm of Mn(II), high levels of MNPs but no LIPs were produced, and this culture also exhibited high rates of BPE decolorization, lending further support to the idea that MNPs play a key role in BPE decolorization. When P. chrysosporium was grown in a medium with no Mn(II), high levels of LIPs but negligible levels of MNPs were produced and the rate and extent of BPE decolorization by such cultures were quite low, indicating that LIPs play a relatively minor role in BPE decolorization. Furthermore, high rates of BPE decolorization were seen on days 3 and 4 of incubation, when the cultures exhibit high levels of MNP activity but little or no LIP activity. These results indicate that MNPs play a relatively more important role than LIPs in BPE decolorization by P. chrysosporium.     

Degradation of benzene, toluene, ethylbenzene, and xylenes (BTEX) by the lignin-degrading basidiomycete Phanerochaete chrysosporium.

Degradation of the BTEX (benzene, toluene, ethylbenzene, and o-, m-, and p-xylenes) group of organopollutants by the white-rot fungus Phanerochaete chrysosporium was studied. Our results show that the organism efficiently degrades all the BTEX components when these compounds are added either individually or as a composite mixture. Degradation was favored under nonligninolytic culture conditions in malt extract medium, in which extracellular lignin peroxidases (LIPs) and manganese-dependent peroxidases (MNPs) are not produced. The noninvolvement of LIPs and MNPs in BTEX degradation was also evident from in vitro studies using concentrated extracellular fluid containing LIPs and MNPs and from a comparison of the extents of BTEX degradation by the wild type and the per mutant, which lacks LIPs and MNPs. A substantially greater extent of degradation of all the BTEX compounds was observed in static than in shaken liquid cultures. Furthermore, the level of degradation was relatively higher at 25 than at 37 degrees C, but pH variations between 4.5 and 7.0 had little effect on the extent of degradation. Studies with uniformly ring-labeled [14C]benzene and [14C]toluene showed substantial mineralization of these compounds to 14CO2.     

Non-involvement of lignin peroxidases and manganese peroxidases in 2,4,5-trichlorophenoxyacetic acid degradation byPhanerochaete chrysosporium

Summary Phanerochaete chrysosporium (ME-446) mineralized 2,4,5-trichlorophenoxyacetic acid (2,4,5-T) in high N medium and in malt extract medium in which lignin peroxidases (LIPs) and manganese peroxidases (MNPs) are not produced; furthermore,per mutant of ME-446, which lacks LIPs and MNPs, mineralized 2,4,5-T as well as the wild type. These results indicate that LIPs and MNPs are not required for 2,4,5-T degradation byP. chrysosporium.     

Homology among multiple extracellular peroxidases from Phanerochaete chrysosporium

The extracellular peroxidases of Phanerochaete chrysosporium were separated into 21 proteins by analytical isoelectric focusing. Fifteen of these enzymes oxidized veratryl alcohol (lignin peroxidases) in the presence of H2O2. Six enzymes were Mn(II)-dependent peroxidases. The Mn(II)-dependent enzymes appeared and reached their maximal activity earlier than the lignin peroxidases in the cultures. Peptide mapping, amino acid analysis, and reaction against specific antibodies showed that all the Mn(II)-dependent peroxidases were probably products of one gene. A great degree of homology was also present among the various lignin peroxidases.     

Lignin peroxidase-negative mutant of the white-rot basidiomycete Phanerochaete chrysosporium

Phanerochaete chrysosporium produces two classes of extracellular heme proteins, designated lignin peroxidases and manganese peroxidases, that play a key role in lignin degradation. In this study we isolated and characterized a lignin peroxidase-negative mutant (lip mutant) that showed 16% of the ligninolytic activity (14C-labeled synthetic lignin----14CO2) exhibited by the wild type. The lip mutant did not produce detectable levels of lignin peroxidase, whereas the wild type, under identical conditions, produced 96 U of lignin peroxidase per liter. Both the wild type and the mutant produced comparable levels of manganese peroxidase and glucose oxidase, a key H2O2-generating secondary metabolic enzyme in P. chrysosporium. Fast protein liquid chromatographic analysis of the concentrated extracellular fluid of the lip mutant confirmed that it produced only heme proteins with manganese peroxidase activity but no detectable lignin peroxidase activity, whereas both lignin peroxidase and manganese peroxidase activities were produced by the wild type. The lip mutant appears to be a regulatory mutant that is defective in the production of all the lignin peroxidases.     

Mineralization of C-Ring-Labeled Synthetic Lignin Correlates with the Production of Lignin Peroxidase, not of Manganese Peroxidase or Laccase

Recently, Mn(II) has been shown to induce manganese peroxidases (MnPs) and repress lignin peroxidases (LiPs) in defined liquid cultures of several white rot organisms. The present work shows that laccase is also regulated by Mn(II). We therefore used Mn(II) to regulate production of LiP, MnP, and laccase activities while determining the effects of Mn(II) on mineralization of ring-labeled synthetic lignin. At a low Mn(II) level, Phanerochaete chrysosporium and Phlebia brevispora produced relatively high titers of LiPs but only low titers of MnPs. At a high Mn(II) level, MnP titers increased 12- to 20-fold, but LiPs were not detected in crude broths. P. brevispora formed much less LiP than P. chrysosporium, but it also produced laccase activity that increased more than sevenfold at the high Mn(II) level. The rates of synthetic lignin mineralization by these organisms were similar and were almost seven times higher at low than at high Mn(II). Increased synthetic lignin mineralization therefore correlated with increased LiP, not with increased MnP or laccase activities.     

Degradation of phenanthrene by Phanerochaete chrysosporium occurs under ligninolytic as well as nonligninolytic conditions.

In order to delineate the roles of lignin and manganese peroxidases in the degradation of polycyclic aromatic hydrocarbons by Phanerochaete chrysosporium, the biodegradation of phenanthrene (chosen as a model for polycyclic aromatic hydrocarbons) was investigated. The disappearance of phenanthrene from the extracellular medium and mycelia was determined by using gas chromatography. The disappearance of phenanthrene from cultures of wild-type strains BKM-F1767 (ATCC 24725) and ME446 (ATCC 34541) under ligninolytic (low-nitrogen) as well as nonligninolytic (high-nitrogen) conditions was observed. The study was extended to two homokaryotic (basidiospore-derived) isolates of strain ME446. Both homokaryotic isolates, ME446-B19 (which produces lignin and manganese peroxidases only in low-nitrogen medium) and ME446-B5 (which totally lacks lignin and manganese peroxidase activities), caused the disappearance of phenanthrene when grown in low- as well as high-nitrogen media. Moreover, lignin and manganese peroxidase activities were not detected in any of the cultures incubated in the presence of phenanthrene. Additionally, the mineralization of phenanthrene was observed even under nonligninolytic conditions. The results collectively indicate that lignin and manganese peroxidases are not essential for the degradation of phenanthrene by P. chrysosporium. The observation that phenanthrene degradation occurs under nonligninolytic conditions suggests that the potential of P. chrysosporium for degradation of certain environmental pollutants is not limited to nutrient starvation conditions.     

Toward a control of lignin and manganese peroxidases hypersecretion by Phanerochaete chrysosporium in agitated vessels: Evidence of the superiority of pneumatic bioreactors on mechanically agitated bioreactors

Phanerochaete chrysosporium and cultivated both mechanically agitated and pneumatic bioreactors. In the pneumatic devices, the yields of lignin and manganese peroxidases as well as extracellular protein, were considerably increased as compared with mechanically agitated bioreactors. Lignin peroxidase and manganese peroxidase activities as high as 4500 U . L(-1) and 1812 U . L(-1) respectively, were produced in an airlift bioreactor. By using enzyme markers, the secretion pathway and the respiration were shown to be dramatically activated in pneumatic bioreactors. The general metabolism of the fungus, when cultivated in the conventional fermentors, is oriented toward the synthesis of biomass at the expense of the synthesis of peroxidases. The use of pneumatic devices for the production of extracellular peroxidases by P. chrysosporium, avoids shear effects due to turbine agitator in the conventional fermentors, and provides a good example for the production of shear-sensitive metabolites. (c) 1993 John Wiley & Sons, Inc.     

Degradation of phenanthrene by Phanerochaete chrysosporium occurs under ligninolytic as well as nonligninolytic conditions.

In order to delineate the roles of lignin and manganese peroxidases in the degradation of polycyclic aromatic hydrocarbons by Phanerochaete chrysosporium, the biodegradation of phenanthrene (chosen as a model for polycyclic aromatic hydrocarbons) was investigated. The disappearance of phenanthrene from the extracellular medium and mycelia was determined by using gas chromatography. The disappearance of phenanthrene from cultures of wild-type strains BKM-F1767 (ATCC 24725) and ME446 (ATCC 34541) under ligninolytic (low-nitrogen) as well as nonligninolytic (high-nitrogen) conditions was observed. The study was extended to two homokaryotic (basidiospore-derived) isolates of strain ME446. Both homokaryotic isolates, ME446-B19 (which produces lignin and manganese peroxidases only in low-nitrogen medium) and ME446-B5 (which totally lacks lignin and manganese peroxidase activities), caused the disappearance of phenanthrene when grown in low- as well as high-nitrogen media. Moreover, lignin and manganese peroxidase activities were not detected in any of the cultures incubated in the presence of phenanthrene. Additionally, the mineralization of phenanthrene was observed even under nonligninolytic conditions. The results collectively indicate that lignin and manganese peroxidases are not essential for the degradation of phenanthrene by P. chrysosporium. The observation that phenanthrene degradation occurs under nonligninolytic conditions suggests that the potential of P. chrysosporium for degradation of certain environmental pollutants is not limited to nutrient starvation conditions.     

Lignin-modifying enzymes from selected white-rot fungi: production and role from in lignin degradation

Abstract: White-rot fungi produce extracellular lignin-modifying enzymes, the best characterized of which are laccase (EC 1.10.3.2), lignin peroxidases (EC 1.11.1.7) and manganese peroxidases (EC 1.11.1.7). Lignin biodegradation studies have been carried out mostly using the white-rot fungus Phanerochaete chrysosporium which produces multiple isoenzymes of lignin peroxidase and manganese peroxidase but does not produce laccase. Many other white-rot fungi produce laccase in addition to lignin and manganese peroxidases and in varying combinations. Based on the enzyme production patterns of an array of white-rot fungi, three categories of fungi are suggested: (i) lignin-manganese peroxidase group (e.g. P. chrysosporium and Phlebia radiata ), (ii) manganese peroxidase-laccase group (e.g. Dichomitus squalens and Rigidoporus lignosus ), and (iii) lignin peroxidase-laccase group (e.g. Phlebia ochraceofulva and Junghuhnia separabilima ). The most efficient lignin degraders, estimated by ¹⁴CO₂ evolution from ¹⁴C-[Ring]-labelled synthetic lignin (DHP), belong to the first group, whereas many of the most selective lignin-degrading fungi belong to the second, although only moderate to good [¹⁴C]DHP mineralization is obtained using fungi from this group. The lignin peroxidase-laccase fungi only poorly degrade [¹⁴C]DHP.     

Ubiquity of lignin-degrading peroxidases among various wood-degrading fungi.

Phanerochaete chrysosporium is rapidly becoming a model system for the study of lignin biodegradation. Numerous studies on the physiology, biochemistry, chemistry, and genetics of this system have been performed. However, P. chrysosporium is not the only fungus to have a lignin-degrading enzyme system. Many other ligninolytic species of fungi, as well as other distantly related organisms which are known to produce lignin peroxidases, are described in this paper. In this study, we demonstrated the presence of the peroxidative enzymes in nine species not previously investigated. The fungi studied produced significant manganese peroxidase activity when they were grown on an oak sawdust substrate supplemented with wheat bran, millet, and sucrose. Many of the fungi also exhibited laccase and/or glyoxal oxidase activity. Inhibitors present in the medium prevented measurement of lignin peroxidase activity. However, Western blots (immunoblots) revealed that several of the fungi produced lignin peroxidase proteins. We concluded from this work that lignin-degrading peroxidases are present in nearly all ligninolytic fungi, but may be expressed differentially in different species. Substantial variability exists in the levels and types of ligninolytic enzymes produced by different white not fungi.     

A search for ligninolytic peroxidases in the fungus pleurotus eryngii involving alpha-keto-gamma-thiomethylbutyric acid and lignin model dimers

Because there is some controversy concerning the ligninolytic enzymes produced by Pleurotus species, ethylene release from alpha-keto-gamma-thiomethylbutyric acid (KTBA), as described previously for Phanerochaete chrysosporium lignin peroxidase (LiP), was used to assess the oxidative power of Pleurotus eryngii cultures and extracellular proteins. Lignin model dimers were used to confirm the ligninolytic capabilities of enzymes isolated from liquid and solid-state fermentation (SSF) cultures. Three proteins that oxidized KTBA in the presence of veratryl alcohol and H2O2 were identified (two proteins were found in liquid cultures, and one protein was found in SSF cultures). These proteins are versatile peroxidases that act on Mn2+, as well as on simple phenols and veratryl alcohol. The two peroxidases obtained from the liquid culture were able to degrade a nonphenolic beta-O-4 dimer, yielding veratraldehyde, as well as a phenolic dimer which is not efficiently oxidized by P. chrysosporium peroxidases. The former reaction is characteristic of LiP. The third KTBA-oxidizing peroxidase oxidized only the phenolic dimer (in the presence of Mn2+). Finally, a fourth Mn2+-oxidizing peroxidase was identified in the SSF cultures on the basis of its ability to oxidize KTBA in the presence of Mn2+. This enzyme is related to the Mn-dependent peroxidase of P. chrysosporium because it did not exhibit activity with veratryl alcohol and Mn-independent activity with dimers. These results show that P. eryngii produces three types of peroxidases that have the ability to oxidize lignin but lacks a typical LiP. Similar enzymes (in terms of N-terminal sequence and catalytic properties) are produced by other Pleurotus species. Some structural aspects of P. eryngii peroxidases related to the catalytic properties are discussed.     

Lignin peroxidase H2 from Phanerochaete chrysosporium: purification, characterization and stability to temperature and pH

The wood-destroying fungus Phanerochaete chrysosporium secretes extracellular enzymes known as lignin peroxidases that are involved in the biodegradation of lignin and a number of environmental pollutants. Several lignin peroxidases are produced in liquid cultures of this fungus. However, only lignin peroxidase isozyme H8 has been extensively characterized. In agitated nutrient nitrogen-limited culture, P. chrysosporium produces two lignin peroxidases in about equal proportions. The molecular weights of these two major proteins (H2 and H8) as determined by sodium dodecyl sulfate-polyacrylamide gel electrophoresis were 38,500 (H2) and 42,000 (H8). The isoelectric points of these enzymes were 4.3 for H2 and 3.65 for H8. All subsequent experiments in this study were performed with H2 as it contributed the most (42%) to total activity and had the highest specific activity (57.3 U/mg). The Km values of lignin peroxidase H2 for H2O2 and veratryl alcohol were calculated to be 47 microM and 167 microM at pH 3.5, respectively. The pH optima for veratryl alcohol oxidase activity were pH 2.5 at 25 degrees C, pH 3.0 at 35 degrees C, and pH 3.5 at 45 degrees C. In the same manner the temperature optimum shifted from 25 degrees C at pH 2.5 to 45 degrees C at pH 3.5 and approximately 45-60 degrees C at pH 4.5. During storage the resting enzyme was relatively stable for 48 h up to 50 degrees C. Above this temperature the enzyme lost all activity within 6 h at 60 degrees C. At 70 degrees C all activity was lost within 10 min. The resting enzyme retained approximately 80% of its initial activity when stored at 40 degrees C for 21 h at a pH range of 4.0-6.5. Above pH 7.5 and below 4.0, the enzyme lost all activity in less than 5 h. During turnover the enzyme remained active at pH 5.5 for over 2 h whereas the enzyme activity was lost after 45 min at pH 2.5. The oxidation of veratryl alcohol was inhibited by EDTA, azide, cyanide, and by the catalase inhibitor 3-amino-1,2,4-triazole, but not by chloride. In the absence of another reducing substrate incubation of lignin peroxidase H2 with excess H2O2 resulted in partial and irreversible inactivation of the enzyme. The spectral characteristics of lignin peroxidase H2 are similar to those of other peroxidases. The suitability of lignin peroxidases for industrial applications is discussed.     

Potential Applications of the Oxidoreductive Enzymes in the Decolorization and Detoxification of Textile and Other Synthetic Dyes from Polluted Water: A Review

ABSTRACT

Recently, the enzymatic approach has attracted much interest in the decolorization/degradation of textile and other industrially important dyes from wastewater as an alternative strategy to conventional chemical, physical and biological treatments, which pose serious limitations. Enzymatic treatment is very useful due to the action of enzymes on pollutants even when they are present in very dilute solutions and recalcitrant to the action of various microbes participating in the degradation of dyes. The potential of the enzymes (peroxidases, manganese peroxidases, lignin peroxidases, laccases, microperoxidase-11, polyphenol oxidases, and azoreductases) has been exploited in the decolorization and degradation of dyes. Some of the recalcitrant dyes were not degraded/decolorized in the presence of such enzymes. The addition of certain redox mediators enhanced the range of substrates and efficiency of degradation of the recalcitrant compounds. Several redox mediators have been reported in the literature, but very few of them are frequently used (e.g., 1-hydroxybenzotriazole, veratryl alcohol, violuric acid, 2-methoxy-phenothiazone). Soluble enzymes cannot be exploited at the large scale due to limitations such as stability and reusability. Therefore, the use of immobilized enzymes has significant advantages over soluble enzymes. In the near future, technology based on the enzymatic treatment of dyes present in the industrial effluents/wastewater will play a vital role. Treatment of wastewater on a large scale will also be possible by using reactors containing immobilized enzymes.     

The involvement of hydroxyl radical derived from hydrogen peroxide in lignin degradation by the white rot fungus Phanerochaete chrysosporium

The possible involvement of hydrogen peroxide (H2O2)-derived hydroxyl radical (.OH) in lignin degradation ([14C]lignin leads to 14CO2) by Phanerochaete chrysosporium was investigated. When P. chrysosporium was grown in low nitrogen medium (2.4 mM N), an increase in the specific activity for H2O2 production in cell extracts was observed to coincide with the appearance of ligninolytic activity and both activities appeared after the culture entered stationary phase. The production of .OH in ligninolytic cultures of P. chrysosporium was demonstrated by alpha-keto-gamma-methiolbutyric acid-dependent formation of ethylene. Hydrogen peroxide-dependent .OH formation was also shown in cell extracts of ligninolytic cultures. The radical species was demonstrated to be .OH by the .OH-dependent hydroxylation of p-hydroxybenzoic acid to form protocatechuic acid and by using 5,5-dimethyl-1-pyrroline-N-oxide and detecting the production of the nitroxide radical of 5,5-dimethyl-1-pyrroline-N-oxide by EPR. These reactions were inhibited by .OH-scavenging agents and were stimulated when azide was added to inhibit endogenous catalase. Lignin degradation by P. chrysosporium was markedly suppressed in the presence of the .OH-scavenging agents mannitol, benzoate, and the nonspecific radical scavenging agent butylated hydroxytoluene. The above results indicate that .OH derived from H2O2 is involved in lignin biodegradation by P. chrysosporium.