Evidence That Ceriporiopsis subvermispora Degrades Nonphenolic Lignin Structures by a One-Electron-Oxidation Mechanism

The white-rot fungus Ceriporiopsis subvermispora is able to degrade nonphenolic lignin structures but appears to lack lignin peroxidase (LiP), which is generally thought to be responsible for these reactions. It is well established that LiP-producing fungi such as Phanerochaete chrysosporium degrade nonphenolic lignin via one-electron oxidation of its aromatic moieties, but little is known about ligninolytic mechanisms in apparent nonproducers of LiP such as C. subvermispora. To address this question, C. subvermispora and P. chrysosporium were grown on cellulose blocks and given two high-molecular-weight, polyethylene glycol-linked model compounds that represent the major nonphenolic arylglycerol-(beta)-aryl ether structure of lignin. The model compounds were designed so that their cleavage via one-electron oxidation would leave diagnostic fragments attached to the polyethylene glycol. One model compound was labeled with (sup13)C at C(inf(alpha)) of its propyl side chain and carried ring alkoxyl substituents that favor C(inf(alpha))-C(inf(beta)) cleavage after one-electron oxidation. The other model compound was labeled with (sup13)C at C(inf(beta)) of its propyl side chain and carried ring alkoxyl substituents that favor C(inf(beta))-O-aryl cleavage after one-electron oxidation. To assess fungal degradation of the models, the high-molecular-weight metabolites derived from them were recovered from the cultures and analyzed by (sup13)C nuclear magnetic resonance spectrometry. The results showed that both C. subvermispora and P. chrysosporium degraded the models by routes indicative of one-electron oxidation. Therefore, the ligninolytic mechanisms of these two fungi are similar. C. subvermispora might use a cryptic LiP to catalyze these C(inf(alpha))-C(inf(beta)) and C(inf(beta))-O-aryl cleavage reactions, but the data are also consistent with the involvement of some other one-electron oxidant.     

Oxidative degradation of phenanthrene by the ligninolytic fungus Phanerochaete chrysosporium.

The ligninolytic fungus Phanerochaete chrysosporium oxidized phenanthrene and phenanthrene-9,10-quinone (PQ) at their C-9 and C-10 positions to give a ring-fission product, 2,2'-diphenic acid (DPA), which was identified in chromatographic and isotope dilution experiments. DPA formation from phenanthrene was somewhat greater in low-nitrogen (ligninolytic) cultures than in high-nitrogen (nonligninolytic) cultures and did not occur in uninoculated cultures. The oxidation of PQ to DPA involved both fungal and abiotic mechanisms, was unaffected by the level of nitrogen added, and was significantly faster than the cleavage of phenanthrene to DPA. Phenanthrene-trans-9,10-dihydrodiol, which was previously shown to be the principal phenanthrene metabolite in nonligninolytic P. chrysosporium cultures, was not formed in the ligninolytic cultures employed here. These results suggest that phenanthrene degradation by ligninolytic P. chrysosporium proceeds in order from phenanthrene----PQ----DPA, involves both ligninolytic and nonligninolytic enzymes, and is not initiated by a classical microsomal cytochrome P-450. The extracellular lignin peroxidases of P. chrysosporium were not able to oxidize phenanthrene in vitro and therefore are also unlikely to catalyze the first step of phenanthrene degradation in vivo. Both phenanthrene and PQ were mineralized to similar extents by the fungus, which supports the intermediacy of PQ in phenanthrene degradation, but both compounds were mineralized significantly less than the structurally related lignin peroxidase substrate pyrene was.     

Lignin and veratryl alcohol are not inducers of the ligninolytic system of Phanerochaete chrysosporium.

Phanerochaete chrysosporium is a white rot fungus which secretes a family of lignin-degrading enzymes under nutrient limitation. In this work, we investigated the roles of veratryl alcohol and lignin in the ligninolytic system of P. chrysosporium BKM-F-1767 cultures grown under nitrogen-limited conditions. Cultures supplemented with 0.4 to 2 mM veratryl alcohol showed increased lignin peroxidase activity. Addition of veratryl alcohol had no effect on Mn-dependent peroxidase activity and inhibited glyoxal oxidase activity. Azure-casein analysis of acidic proteases in the extracellular fluid showed that protease activity decreased during the early stages of secondary metabolism while lignin peroxidase activity was at its peak, suggesting that proteolysis was not involved in the regulation of lignin peroxidase activity during early secondary metabolism. In cultures supplemented with lignin or veratryl alcohol, no induction of mRNA coding for lignin peroxidase H2 or H8 was observed. Veratryl alcohol protected lignin peroxidase isozymes H2 and H8 from inactivation by H2O2. We conclude that veratryl alcohol acts as a stabilizer of lignin peroxidase activity and not as an inducer of lignin peroxidase synthesis.     

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.     

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.     

Stimulation of ligninolytic enzyme production in Phanerochaete chrysosporium by polyoxyalkanes

AIMS: Poly(ethylene glycol) (PEG) and some substances similar to PEG in chemical structure were tested as stimulators of ligninolytic enzyme production in shaken culture of Phanerochaete chrysosporium. METHODS AND RESULTS: The substances that caused high enzymatic activity were linear polymers [poly(ethylene glycol), poly(propylene glycol), poly(butylene glycol) and poly(vinyl alcohol)] and cyclic polymers (crown ether). They can have terminal groups other than -OH [PEG (di)methyl ether, PEG sulphate, PEG derivative with the amino group and xanthate]. The maximum lignin peroxidase activities were compared with the surface pressure caused by the stimulator. Addition of polymers composed of charged monomer units did not increase the enzymatic activity and the fungi did not grow at all on addition of polymers having a fixed positive charge. CONCLUSIONS: Lignin peroxidase activity was increased after the addition of polymers with uncharged monomer units. It was higher and its maximum was reached in a shorter time on addition of polymers with higher molecular weights. SIGNIFICANCE AND IMPACT OF STUDY: Beside Tweens there are several polymers that stimulate ligninolytic enzyme production in shaken culture of P. chrysosporium. Their characteristics are: similarity to PEG in chemical structure, having uncharged monomer units and high molecular weight.     

Biodegradation of pentachlorophenol by white rot fungi under ligninolytic and nonligninolytic conditions

The roles of lignin peroxidase, manganese peroxidase, and laccase were investigated in the biodegradation of pentachlorophenol (PCP) by several white rot fungi. The disappearance of pentachlorophenol from cultures of wild type strains,P. chrysosporium, Trametes sp. andPleurotus sp., was observed. The activities of manganese peroxidase and laccase were detected inTiametes sp. andPleurotus sp. cultures. However, the activities of ligninolytic enzymes were not detected inP. chrysosporium cultures. Therefore, our results showed that PCP was degraded under ligninolytic as well as nonligninolytic conditions. Indicating that lignin peroxidase, manganese peroxidase, and laccase are not essential in the biodegradation of PCP by white rot fungi.     

Biodegradation of azo and heterocyclic dyes by Phanerochaete chrysosporium.

Biodegradation of Orange II, Tropaeolin O, Congo Red, and Azure B in cultures of the white rot fungus, Phanerochaete chrysosporium, was demonstrated by decolarization of the culture medium, the extent of which was determined by monitoring the decrease in absorbance at or near the wavelength maximum for each dye. Metabolite formation was also monitored. Decolorization of these dyes was most extensive in ligninolytic cultures, but substantial decolorization also occurred in nonligninolytic cultures. Incubation with crude lignin peroxidase resulted in decolorization of Azure B, Orange II, and Tropaeolin O but not Congo Red, indicating that lignin peroxidase is not required in the initial step of Congo Red degradation.     

Biodegradation of azo and heterocyclic dyes by Phanerochaete chrysosporium

Biodegradation of Orange II, Tropaeolin O, Congo Red, and Azure B in cultures of the white rot fungus, Phanerochaete chrysosporium, was demonstrated by decolarization of the culture medium, the extent of which was determined by monitoring the decrease in absorbance at or near the wavelength maximum for each dye. Metabolite formation was also monitored. Decolorization of these dyes was most extensive in ligninolytic cultures, but substantial decolorization also occurred in nonligninolytic cultures. Incubation with crude lignin peroxidase resulted in decolorization of Azure B, Orange II, and Tropaeolin O but not Congo Red, indicating that lignin peroxidase is not required in the initial step of Congo Red degradation.     

Degradation of anthracene by selected white rot fungi

Abstract Approximately 60% of the originally supplied anthracene (AC) was degraded in ligninolytic stationary cultures of selected white rot fungi within 21 days. All the white rot fungi tested oxidized AC to anthraquinone (AQ). Unlike Phanerochaete chrysosporium and strain Px, with Pleurotus ostreatus, Coriolopsis polyzona and Trametes versicolor , AQ did not accumulate in the cultures, indicating that AQ was degraded further and its degradation did not appear to be a rate-limiting step. However, P. ostreatus and C. polyzona failed to degrade AQ in the absence of AC. P. ostreatus, T. versicolor and strain Px did not produce lignin peroxidase (ligninase) (LIP) under the test conditions but oxidized AC to AQ suggesting that white rot fungi produce enzyme(s) other than LIP capable of oxidizing compounds with high ionization potential like AC. Moreover, in the case of Ph. chrysosporium and C. polyzona , AC degradation started earlier than the production of LIP. Veratryl alcohol (VA) seemed to be playing a role in AC oxidation catalyzed by LIP in Ph. chrysosporium .     

Biodegradation of crystal violet by the white rot fungus Phanerochaete chrysosporium

Biodegradation of crystal violet (N,N,N',N',N',N'-hexamethylpararosaniline) in ligninolytic (nitrogen-limited) cultures of the white rot fungus Phanerochaete chrysosporium was demonstrated by the disappearance of crystal violet and by the identification of three metabolites (N,N,N',N',N'-pentamethylpararosaniline, N,N,N',N'-tetramethylpararosaniline, and N,N',N'-trimethylpararosaniline) formed by sequential N-demethylation of the parent compound. Metabolite formation also occurred when crystal violet was incubated with the extracellular fluid obtained from ligninolytic cultures of this fungus, provided that an H2O2-generating system was supplied. This, as well as the fact that a purified ligninase catalyzed N-demethylation of crystal violet, demonstrated that biodegradation of crystal violet by this fungus is dependent, at least in part, upon its lignin-degrading system. In addition to crystal violet, six other triphenylmethane dyes (pararosaniline, cresol red, bromphenol blue, ethyl violet, malachite green, and brilliant green) were shown to be degraded by the lignin-degrading system of this fungus. An unexpected result was the finding that substantial degradation of crystal violet also occurred in nonligninolytic (nitrogen-sufficient) cultures of P. chrysosporium, suggesting that in addition to the lignin-degrading system, another mechanism exists in this fungus which is also able to degrade crystal violet.     

Biodegradation of crystal violet by the white rot fungus Phanerochaete chrysosporium.

Biodegradation of crystal violet (N,N,N',N',N',N'-hexamethylpararosaniline) in ligninolytic (nitrogen-limited) cultures of the white rot fungus Phanerochaete chrysosporium was demonstrated by the disappearance of crystal violet and by the identification of three metabolites (N,N,N',N',N'-pentamethylpararosaniline, N,N,N',N'-tetramethylpararosaniline, and N,N',N'-trimethylpararosaniline) formed by sequential N-demethylation of the parent compound. Metabolite formation also occurred when crystal violet was incubated with the extracellular fluid obtained from ligninolytic cultures of this fungus, provided that an H2O2-generating system was supplied. This, as well as the fact that a purified ligninase catalyzed N-demethylation of crystal violet, demonstrated that biodegradation of crystal violet by this fungus is dependent, at least in part, upon its lignin-degrading system. In addition to crystal violet, six other triphenylmethane dyes (pararosaniline, cresol red, bromphenol blue, ethyl violet, malachite green, and brilliant green) were shown to be degraded by the lignin-degrading system of this fungus. An unexpected result was the finding that substantial degradation of crystal violet also occurred in nonligninolytic (nitrogen-sufficient) cultures of P. chrysosporium, suggesting that in addition to the lignin-degrading system, another mechanism exists in this fungus which is also able to degrade crystal violet.     

Lignin peroxidase is involved in the biobleaching of manganese-less oxygen-delignified hardwood kraft pulp by white-rot fungi in the solid-fermentation system

Biobleaching of manganese-less oxygen-delignified hardwood kraft pulp (E-OKP) by the white-rot fungi Phanerochaete sordida YK-624 and P. chrysosporium was examined in the solid-state fermentation system. P. sordida YK-624 possessed a higher brightening activity than P. chrysosporium, increasing pulp brightness by 13.4 points after seven days of treatment. In these fermentation systems, lignin peroxidase (LiP) activity was detected as the principle ligninolytic enzyme, and manganese peroxidase and laccase activities were scarcely detected over the course of treatment of E-OKP by either fungus. Moreover, a linear relationship between brightness increase and cumulative LiP activity was observed under all tested culture conditions with P. sordida YK-624 and P. chrysosporium. These results indicated that LiP is involved in the brightening of E-OKP by both white-rot fungi.     

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.     

Nutritional Regulation of Lignin Degradation by Phanerochaete chrysosporium

Previous studies have shown that a lignin-degrading system appears in cultures of the white rot fungus Phanerochaete chrysosporium in response to nitrogen starvation, apparently as part of secondary metabolism. We examined the influence of limiting carbohydrate, sulfur, or phosphorus and the effect of varying the concentrations of four trace metals, Ca, and Mg. Limitation of carbohydrate or sulfur but not limitation of phosphorus triggered ligninolytic activity. When only carbohydrate was limiting, supplementary carbohydrate caused a transient repression of activity. In carbohydrate-limited cultures, ligninolytic activity appeared when the supplied carbohydrate was depleted, and this activity was associated with a decrease in mycelial dry weight. The amount of lignin degraded depended on the amount of carbohydrate provided, which determined the amount of mycelium produced during primary growth. Carbohydrate-limited cultures synthesized only small amounts of the secondary metabolite veratryl alcohol compared with nitrogen-limited cultures. l-Glutamate sharply repressed ligninolytic activity in carbohydrate-starved cultures, but NH(4) did not. Ligninolytic activity was also triggered in cultures supplied with 37 muM sulfur as the only limiting nutrient. The balance of trace metals, Mg, and Ca was important for lignin degradation.     

Growth and ligninolytic system production dynamics of the Phanerochaete chrysosporium fungus A modelling and optimization approach

The well-documented ability to degrade lignin and a variety of complex chemicals showed by the white-rot fungus Phanerochaete chrysosporium has made it the subject of many studies in areas of environmental concern, including pulp bioleaching and bioremediation technologies. However, until now, most of the work in this field has been focused on the ligninolytic sub-system but, due to the great complexity of the involved processes, less progress has been made in understanding the biochemical regulatory structure that could explain growth dynamics, the substrate utilization and the ligninolytic system production itself. In this work we want to tackle this problem from the perspectives and approaches of systems biology, which have been shown to be effective in the case of complex systems. We will use a top-down approach to the construction of this model aiming to identify the cellular sub-systems that play a major role in the whole process. We have investigated growth dynamics, substrate consumption and lignin peroxidase production of the P. chrysosporium wild type under a set of definite culture conditions. Based on data gathered from different authors and in our own experimental determinations, we built a model using a GMA power-law representation, which was used as platform to make predictive simulations. Thereby, we could assess the consistency of some current assumptions about the regulatory structure of the overall process. The model parameters were estimated from a time series experimental measurements by means of an algorithm previously adapted and optimized for power-law models. The model was subsequently checked for quality by comparing its predictions with the experimental behavior observed in new, different experimental settings and through perturbation analysis aimed to test the robustness of the model. Hence, the model showed to be able to predict the dynamics of two critical variables such as biomass and lignin peroxidase activity when in conditions of nutrient deprivation and after pulses of veratryl alcohol. Moreover, it successfully predicts the evolution of the variables during both, the active growth phase and after the deprivation shock. The close agreement between the predicted and observed behavior and the advanced understanding of its kinetic structure and regulatory features provides the necessary background for the design of a biotechnological set-up designed for the continuous production of the ligninolityc system and its optimization.     

Recent advances in studies of the mechanisms of microbial degradation of lignins

Major advances in our understanding of the biochemical and enzymological mechanisms of lignin biodegradation have been made in the past three years. Research has principally involved two ligninolytic microorganisms, the white rot fungus Phanerochaete chrysosporium and the actinomycete Streptomyces viridosporus. Research has been centred on attempts to identify the microbial catalysts that mediate lignin decay in these two microbes. Emphasis has been on studies concerned with isolating specific lignin catabolic enzymes and/or reduced forms of oxygen involved in attacking the lignin polymer. The possibility that lignin degradation might be non-enzymatic and mediated by extracellular reduced oxygen species such as hydrogen peroxide (H₂O₂), superoxide (O₂∪c-|_.), hydroxyl radical (·OH) or singlet oxygen (¹O₂) has been investigated with both microorganisms. Using methods which have not always been unequivocal, the question of involvement of reduced oxygen species in lignin degradation by P. chrysosporium has been examined exhaustively. Evidence for the involvement of H₂O₂ is conclusive. However, there is little evidence to support the involvement of other extracellular reduced oxygen species, including ·OH, directly in the process of lignin degradation. Scavenger studies have been inconclusive because of questions of their specificity. If activated oxygen species are involved, the activated oxygen is probably held within the active site of an enzyme molecule. With S. viridosporus, scavenger studies also strongly indicate that extracellular reduced oxygen species are not involved in lignin degradation since scavengers generally do not significantly affect the ligninolytic system. The involvement of specific enzymes in lignin degradation by both P. chrysosporium and S. viridosporus has now been confirmed. With P. chrysosporium, ligninolytic enzymes recently discovered include extracellular non-specific peroxidases and oxygenases. They show numerous activities including dehydrogenative, peroxidatic, oxygenative and C_α?C_β cleavages of lignin side chains. At least one P. chrysosporium enzyme, a unique H₂O₂-requiring oxygenase, has been purified to homogeneity. Evidence has been presented to show that S. viridosporus also produces a ligninolytic enzyme complex involved in demethylation of lignin's aromatic rings and in the oxidation of lignin side chains and cleavage of β-tether linkages within the polymer. The combined activites of these enzymes generate water-soluble polymeric modified lignin fragments, which are then slowly degraded further by S. viridosporus. The β-ether cleaving enzyme complex is probably membrane associated, but it is not extracellular. These first isolations of ligninolytic enzymes have changed the course of basic research on lignin biodegradation. New research priorities are already emerging and include enzyme purifications, kinetic studies, enzyme reaction mechanism studies and screenings for more enzymes. In addition, genetic studies are being carried out with both P. chrysosporium and S. viridosporus. Genetic manipulations include not only classical mutagenesis techniques, but also recombinant DNA techniques such as protoplast fusion. This latter technique has already been used to generate overproducers of the ligninolytic enzyme complex in S. viridosporus and it has been successfully used to recombine mutant strains of P. chrysosporium.     

Fungal biodegradation of lignopolystyrene graft copolymers.

White rot basidiomycetes were able to biodegrade styrene (1-phenylethene) graft copolymers of lignin containing different proportions of lignin and polystyrene [poly(1-phenylethylene)]. The biodegradation tests were run on lignin-styrene copolymerization products which contained 10.3, 32.2, and 50.4% (wt/wt) lignin. The polymer samples were incubated with the white rot fungi Pleurotus ostreatus, Phanerochaete chrysosporium, and Trametes versicolor and the brown rot fungus Gloeophyllum trabeum. White rot fungi degraded the plastic samples at a rate which increased with increasing lignin content in the copolymer sample. Both polystyrene and lignin components of the copolymer were readily degraded. Polystyrene pellets were not degradable in these tests. Degradation was verified for both incubated and control samples by weight loss, quantitative UV spectrophotometric analysis of both lignin and styrene residues, scanning electron microscopy of the plastic surface, and the presence of enzymes active in degradation during incubation. Brown rot fungus did not affect any of the plastics. White rot fungi produced and secreted oxidative enzymes associated with lignin degradation in liquid media during incubation with lignin-polystyrene copolymer.     

Factors Involved in the Regulation of a Ligninase Activity in Phanerochaete chrysosporium

The regulation of an H₂O₂-dependent ligninolytic activity was examined in the wood decay fungus Phanerochaete chrysosporium. The ligninase appears in cultures upon limitation for nitrogen or carbohydrate and is suppressed by excess nutrients, by cycloheximide, or by culture agitation. Activity is increased by idiophasic exposure of cultures to 100% O₂. Elevated levels of ligninase and, in some cases, of extracellular H₂O₂ production are detected after brief incubation of cultures with lignins or lignin substructure models, with the secondary metabolite veratryl alcohol, or with other related compounds. It is concluded that lignin degradation (lignin → CO₂) by this organism is regulated in part at the level of the ligninase, which is apparently inducible by its substrates or their degradation products.     

Overproduction of lignin-degrading enzymes by an isolate of Phanerochaete chrysosporium.

Phanerochaete chrysosporium is a white rot fungus which secretes a family of lignin-degrading enzymes under nutrient limitation. PSBL-1 is a mutant of this organism that generates the ligninolytic system under nonlimiting conditions during primary metabolism. Lignin peroxidase, manganese peroxidase, and glyoxal oxidase activities for PSBL-1 under nonlimiting conditions were 4- to 10-fold higher than those of the wild type (WT) under nitrogen-limiting conditions. PSBL-1 was still in the log phase of growth while secreting the enzymes, whereas the WT had ceased to grow by this time. As in the WT, manganese(II) increased manganese peroxidase activity in the mutant. However, manganese also caused an increase in lignin peroxidase and glyoxal oxidase activities in PSBL-1. Addition of veratryl alcohol to the culture medium stimulated lignin peroxidase activity, inhibited glyoxal oxidase activity, and had little effect on manganese peroxidase activity in PSBL-1, as in the WT. Fast protein liquid chromatography (FPLC) analysis shows production of larger amounts of isozyme H2 in PSBL-1 than in the WT. These properties make PSBL-1 very useful for isolation of large amounts of all ligninolytic enzymes for biochemical study, and they open the possibility of scale-up production for pratical use.