Degradation of 2,4-dichlorophenol by the lignin-degrading fungus Phanerochaete chrysosporium.

Under secondary metabolic conditions the white rot basidiomycete Phanerochaete chrysosporium mineralizes 2,4-dichlorophenol (I). The pathway for the degradation of 2,4-dichlorophenol (I) was elucidated by the characterization of fungal metabolites and of oxidation products generated by purified lignin peroxidase and manganese peroxidase. The multistep pathway involves the oxidative dechlorination of 2,4-dichlorophenol (I) to yield 1,2,4,5-tetrahydroxybenzene (VIII). The intermediate 1,2,4,5-tetrahydroxybenzene (VIII) is ring cleaved to produce, after subsequent oxidation, malonic acid. In the first step of the pathway, 2,4-dichlorophenol (I) is oxidized to 2-chloro-1,4-benzoquinone (II) by either manganese peroxidase or lignin peroxidase. 2-Chloro-1,4-benzoquinone (II) is then reduced to 2-chloro-1,4-hydroquinone (III), and the latter is methylated to form the lignin peroxidase substrate 2-chloro-1,4-dimethoxybenzene (IV). 2-Chloro-1,4-dimethoxybenzene (IV) is oxidized by lignin peroxidase to generate 2,5-dimethoxy-1,4-benzoquinone (V), which is reduced to 2,5-dimethoxy-1,4-hydroquinone (VI). 2,5-Dimethoxy-1,4-hydroquinone (VI) is oxidized by either peroxidase to generate 2,5-dihydroxy-1,4-benzoquinone (VII) which is reduced to form the tetrahydroxy intermediate 1,2,4,5-tetrahydroxybenzene (VIII). In this pathway, the substrate is oxidatively dechlorinated by lignin peroxidase or manganese peroxidase in a reaction which produces a p-quinone. The p-quinone intermediate is then recycled by reduction and methylation reactions to regenerate an intermediate which is again a substrate for peroxidase-catalyzed oxidative dechlorination. This unique pathway apparently results in the removal of both chlorine atoms before ring cleavage occurs.     

An extracellular NADH-oxidizing peroxidase produced by a lignin-degrading basidiomycete,Phanerochaete chrysosporium

A lignin-degrading basidiomycete, Phanerochaete chrysosporium, produces an extracellular peroxidase which in turn produces H₂O₂ by catalyzing the oxidation of NADH and NADPH. The high enzyme activity was observed in the culture grown under nutrient nitrogen limitation (low-N) and high oxygen tension (high-O₂). The enzyme activity was absent in non-ligninolytic agitated culture and in the cultures of non-ligninolytic mutant strains of this organism. The culture method using polyurethane foam cubes as a support for the growing mycelia showed the beneficial effect of producing a large amount of the enzyme. The enzyme is capable of catalyzing the oxidation of NADH and NADPH in the absence of added H₂O₂, and its activity was inhibited strongly by catalase and superoxide dismutase. It is suggested that this peroxidase participates in the ligninolytic system of Phanerochaete chrysosporium as a donor of H₂O₂, which is required for the lignin-peroxidase reaction, by oxidizing extracellular NADH and NADPH.     

Production of Phanerochaete chrysosporium lignin peroxidase

Liginin peroxidase (ligninase) of the white rot fungus Phanerochaete chrysosporium Burdsall was discovered in 1982 as a secondary metabolite. Today multiple isoenzymes are known, which are often collectively called as lignin peroxidase. Lignin peroxidase has been characterized as a veratryl alcohol oxidizing enzyme, but it is a relatively unspecific enzyme catalyzing a variety of reactions with hydrogen peroxide as the electron acceptor. P. chrysosporium ligninases are heme glycoproteins. At least a number of isoenzymes are also phosphorylated. Two of the major isoenzymes have been crystallized. Until recently lignin peroxidase could only be produced in low yields in very small scale stationary cultures owing to shear sensitivity. Most strains produce the enzyme only after grown under nitrogen or carbon limitation, although strains producing lignin peroxidase under nutrient sufficiency have also been isolated. Activities over 2000 U dm(-3) (as determined at 30 degrees to 37 degrees C) have been reported in small scale Erlenmeyer cultures with the strain INA-12 grown on glycerol in the presence of soybean phospholipids under nitrogen sufficiency. In about 8 dm(3) liquid volume pilot scale higher than 100 U dm(-3) (as determined at 23 degrees C) have been obtained under agitation with immobilized P. chrysosporium strains ATCC 24725 or TKK 20512. Good results have been obtained for example with nylon web, polyurethane foam, sintered glass or silicon tubing as the carrier. The immobilized biocatalyst systems have also made large scale repeated batch and semicontinuous production possible. With nylon web as the carrier, lignin peroxidase production has recently been scaled up to 800 dm(3) liquid volume semicontinuous industrial production process.     

Degradation kinetics of pentachlorophenol by Phanerochaete chrysosporium

The extracellular enzymes and cell mass from the pregrown Phanerochaete chrysosporium cultures were used for the degradation of PCP. The use of both extracellular enzymes and cell mass resulted in extensive mineralization of PCP, while the action of only the crude extracellular enzymes led to the formation of a degradation intermediate (TCHD). A kinetic model, which describes the relationship among PCP degradation, initial PCP concentration, dosage of extracellular enzymes, and cell mass concentration, was developed. Based on this model, various effects of initial PCP concentration, dosage of extracellular enzymes, and cell mass concentration were evaluated experimentally. It was found that when initial PCP concentration is lower than 12 mumol/L, the model of a parallel-series first-order reaction is sufficient to describe the degradation process. PCP disappearance and mineralization were enhanced by increasing either the extracellular enzyme concentration or the cell mass concentration. As high as 70% of PCP mineralization could be obtained by using a higher dosage of extracellular enzymes and cell mass. Various parameters of the kinetic model were determined and the model was verified experimentally. Simulation using this model provided the criteria needed to choose rational dosages of extracellular enzymes and cell mass for the degradation of PCP. Data reported allow some insight into the function of the extracellular enzymes and cell mass of P. chrysosporium in degradation processes of toxic pollutants and assist in the design and evaluation of practical bioremediation methods.     

Continuous production of lignin peroxidase by Phanerochaete chrysosporium

Phanerochaete chrysosporium spores were immobilized both in agarose and agar gel beads, and used for the production of lignin peroxidase in repeated batch cultures on carbon-limited medium both with 0.5 g l⁻¹ glucose and without glucose. Veratryl alcohol was used as an activator of enzyme production. The biocatalyst was more stable in agarose gel with the maximum activity of 245 U l⁻¹ obtained in a 70 h batch. The biocatalyst could be used for at least 12 batches on the glucose medium with a gradual decrease in lignin peroxidase activity after the sixth batch. Further, mycelium pellets grown on carbon-limited medium were employed both in vertical and horizontal column reactors for the continuous production of lignin peroxidase. The bioreactor produced lignin peroxidase for at least 20 days in the horizontal system at 49 h residence time, with a maximum activity of 95 U l⁻¹.     

Influence of culture parameters on extracellular peroxidase activity and transformation of low-rank coal by Phanerochaete chrysosporium

The white-rot fungus Phanerochaete chrysosporium can degrade macromolecules in low-rank coal, offering the potential for converting coal to specific products. We investigated the influence of temperature, veratryl alcohol and oxygen on transformation of a solubilised fraction of Morwell brown coal (SWC6 coal) and on the activity of lignin peroxidase and manganese (Mn) peroxidase in N-limited cultures of P. chrysosporium. After 20 days, the mass and A ₄₀₀ of SWC6 coal recovered from cultures containing 0.03% SWC6 coal, incubated at 28 °C under hyperbaric oxygen, were reduced by over 95%. The modal apparent molecular mass of the residuum was reduced by 50%. Addition of 2 mM veratryl alcohol had little effect on the transformation of SWC6 coal. The extent of transformation was reduced in cultures incubated at 37 °C or under air. In cultures under air, coal molecules were transiently polymerised. Decolourisation of SWC6 coal reflects conversion to products that cannot be recovered from the medium, not the destruction of chromophores within recoverable material. The activity of lignin peroxidase, measured in cultures free of SWC6 coal to avoid interference with the assay, correlates directly with the degradation of SWC6 coal as measured by the decline in A ₄₀₀. The data suggest that lignin peroxidase is more important than Mn peroxidase in converting SWC6 coal to products that are assimilated by cells. Received: 16 July 1997 / Received revision: 14 November 1997 / Accepted: 18 November 1997     

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.     

Rapid Degradation of Isolated Lignins by Phanerochaete chrysosporium

Phanerochaete chrysosporium degraded purified Kraft lignin, alkali-extracted and dioxane-extracted straw lignin, and lignosulfonates at a similar rate, producing small-molecular-weight (~1,000) soluble products which comprised 25 to 35% of the original lignins. At concentrations of 1 g of lignin liter⁻¹, 90 to 100% of the acid-insoluble Kraft, alkali straw, and dioxane straw lignins were degraded by 1 g of fungal mycelium liter⁻¹ within an active ligninolytic period of 2 to 3 days. Cultures with biomass concentrations as low as 0.16 g liter⁻¹ could also completely degrade 1 g of lignin liter⁻¹ during an active period of 6 to 8 days. The absorbance at 280 nm of 2 g of lignosulfonate liter⁻¹ increased during the first 3 days of incubation and decreased to 35% of the original value during the next 7 days. The capacity of 1 g of cells to degrade alkali-extracted straw lignin under optimized conditions was estimated to be as high as 1.0 g day⁻¹. This degradation occurred with a simultaneous glucose consumption rate of 1.0 g day⁻¹. When glucose or cellular energy resources were depleted, lignin degradation ceased. The ability of P. chrysosporium to degrade the various lignins in a similar manner and at very low biomass concentrations indicates that the enzymes responsible for lignin degradation are nonspecific.     

黄孢原毛皮革菌降解苯胺的工艺研究

通过正交试验优化筛选了适合黄孢原毛皮革菌降解苯胺的适宜培养基和摇瓶培养降解条件。结果表明：其适宜降解的液体培养基组成为：蔗糖20g／L,可溶性淀粉20g／L,(NH4)2SO4l0g／L,Mn^2 lμmol／L,Tween-800．3％,蛋白胨30g／L。适宜降解的摇瓶培养条件为：接种量为20％、pH为7．0、温度为30℃、培养时间为12d．此条件下的苯胺最高降解率可达95．5％。     

Degradation of synthetic lignin by the protoplasts of Phanerochaete chrysosporium in the presence of lignin peroxidase or manganese peroxidase

Lignin was mineralized in the experiments in which ¹⁴C-lignin was incubated with lignin peroxidase or manganese peroxidase in a tartrate buffer in the presence of cycloheximide-treated protoplasts obtained from the ligninolytic mycelia of Phanerochaete chrysosporium. The rate of lignin mineralization was dependent on the lignin peroxidase or manganese peroxidase concentration in the medium. In the experiments in which lignin was incubated with lignin peroxidase or manganese peroxidase, lignin was repolymerized irrespective of the presence of protoplasts mineralizing lignin, suggesting that an active degradation of lignin and repolymerization took place. Taking into account that lignin peroxidase and manganese peroxidase were the only extracellular enzymes in the experiments in which lignin was mineralized by the protoplasts, it is postulated that lignin peroxidase and/or manganese peroxidase can degrade lignin into small fragments which can then be further absorbed by the fungal cells and subsequently degraded to CO₂.     

Biodegradation of phenanthrene by Phanerochaete chrysosporium: on the role of lignin peroxidase

Lignin peroxidase H8 from the wood rotting basidiomycete Phanerochaete chrysosporium is able to catalyse oxidation of 9-phenanthrol, forming phenanthrene-9, 10-quinone. This is of interest because 9-phenanthrol is an intermediate in the major pathway for phenanthrene degradation that occurs in this fungus under non-ligninolytic conditions whereas the product, phenanthrene-9, 10-quinone, is an intermediate in the pathway that occurs under ligninolytic conditions. It thus appears reasonable to suggest that, at the onset of idiophase (when cultures become ligninolytic), lignin peroxidases may function to link these two pathways.     

Removal of hazardous compounds by lignin peroxidase from Phanerochaete chrysosporium

Phenolic compounds, which are present in many industrial wastewaters, have become a cause for worldwide concern due to their persistence, toxicity and health risks. Enzymatic approaches to remove phenol have been tried for some years as they have several advantages compared with the conventional methods. This paper reports some studies on the use of the white rot fungus Phanerochaete chrysosporium which produces the enzyme lignin peroxidases for the removal of phenol, chlorophenol, and dyes. Batch studies in Erylenmeyer flasks showed complete removal of phenol (500 2 10^х kg/m³) in 30 h. It was also seen that phenol has a significant inhibitory effect on the biomass growth and the enzyme synthesis if added in the early stages of the growth. However, phenol was effectively removed when added after attaining the maximum enzyme activity. 90% of the dyes were removed in about three days, whereas only 62% of the added 4-chlorophenol was removed in about ten days.     

Biosorption of 2,4-dichlorophenol by immobilized white-rot fungus Phanerochaete chrysosporium from aqueous solutions

The fungus Phanerochaete chrysosporium was immobilized in several polymer matrices: Ca-alginate, Ca-alginate-polyvinyl alcohol (PVA) and pectin, and was then used as a biosorbent for removing 2,4-dichlorophenol (2,4-DCP) in wastewater. Immobilization of P. chrysosporium onto pectin was less efficient than that onto other matrices because of its poor mechanical strength and low adsorption efficiency. Ca-alginate immobilized fungal beads with biocompatibility exhibited good mechanical strength and adsorption efficiency over 60%. Among the different biomass dosages in Ca-alginate immobilized fungal beads, 1.25% (w/v) was the optimum. The adsorption data of 2,4-DCP on the blank Ca-alginate beads, free, and immobilized fungal biomass could be described by the Langmuir and Freundlich isotherms very well. Desorption operation was efficiently completed by using distilled water as eluant, and the desorption efficiency reached 82.16% at an optimum solid/liquid ratio of 14.3. The consecutive adsorption/desorption cycles studies employing the Ca-alginate immobilized fungal beads demonstrated that the immobilized fungal biomass could be reused in five cycles without significant loss of adsorption efficiency and adsorbent weight.     

Characterization of reactions catalyzed by manganese peroxidase from Phanerochaete chrysosporium

Manganese peroxidase (MnP) is one of two extracellular peroxidases believed to be involved in lignin biodegradation by the white-rot basidiomycete Phanerochaete chrysosporium. The enzyme oxidizes Mn(II) to Mn(III), which accumulates in the presence of Mn(III) stabilizing ligands. The Mn(III) complex in turn can oxidize a variety of organic substrates. The stoichiometry of Mn(III) complex formed per hydrogen peroxide consumed approaches 2:1 as enzyme concentration increases at a fixed concentration of peroxide or as peroxide concentration decreases at a fixed enzyme concentration. Reduced stoichiometry below 2:1 is shown to be due to Mn(III) complex decomposition by hydrogen peroxide. Reaction of Mn(III) with peroxide is catalyzed by Cu(II), which explains an apparent inhibition of MnP by Cu(II). The net decomposition of hydrogen peroxide to form molecular oxygen also appears to be the only observable reaction in buffers that do not serve as Mn(III) stabilizing ligands. The nonproductive decomposition of both Mn(III) and peroxide is an important finding with implications for proposed in vitro uses of the enzyme and for its role in lignin degradation. Steady-state kinetics of Mn(III) tartrate and Mn(III) malate formation by the enzyme are also described in this paper, with results largely corroborating earlier findings by others. Based on a comparison of pH effects on the kinetics of enzymatic Mn(III) tartrate and Mn(III) malate formation, it appears that pH effects are not due to ionizations of the Mn(III) complexing ligand.     

Suppressive effect of l-phenylalanine on manganese peroxidase in the white-rot fungus Phanerochaete chrysosporium

Abstract The effect of added l-amino acids and NH₄⁺ on manganese peroxidase activity in ligninolytic cultures of Phanerochaete chrysosporium were investigated. Among 11 amino acids (0.2 mM) tested, including phenylalanine, glutamate, glutamine, histidine, alanine, iso-leucine, ornithine, glycine, aspartate, proline, and arginine, phenylalanine was the most effective in suppression of manganese peroxidase synthesis. However, all the amino acids tested except proline completely suppressed the enzyme synthesis at 2 mM concentration.     

Suppressive effect of l-phenylalanine on lignin peroxidase in the white-rot fungus Phanerochaete chrysosporium

Abstract Guanosine-5'-diphosphate-3'-diphosphate (ppGpp), an effector for many metabolic pathways, is synthesized by the relA gene product after amino acid limitation. Studies of stringent controlled Escherichia coli CP78 (relA⁺) and relaxed controlled E. coli CP79 (relA⁻) were carried out to test whether these strains differ in the appearance of their cytoplasmic membranes after induction of stringent and relaxed response. Cytoplasmic membrane structures of the cells were investigated by freeze-fracture electron microscopy after cooling the cells. The obtained micrographs showed a net-like distribution of the particles in the cytoplasmic membranes of relaxed controlled cells whereas such a pattern was not detectable in the stringent controlled counterparts.     

Degradation of fluorene in soil by fungus Phanerochaete chrysosporium

During investigation of biodegradation in soil, we have found that classical or standard techniques for introduction of compounds and the growth of fungus into soil are ill-defined and inadequate. In response to this deficiency, a method for controlled introduction of extractable compounds and for the growth of fungus in soils has been developed. This method was successfully used to study the degradation of fluorene in soil by the fungus Phanerochaete chrysosporium.     

Degradation of polychlorinated biphenyls by extracellular enzymes of Phanerochaete chrysosporium produced in a perforated plate bioreactor

The white rot fungus Phanerochaete chrysosporium was cultivated in a perforated plate bioreactor and the expression of activities of manganese-dependent peroxidase (MnP) and lignin peroxidase (LiP) was measured. Peak activities of the two enzymes were reached close to day 11 and therefore the cultivation was terminated on that day. Extracellular proteins were concentrated and both peroxidases separated by isoelectric focusing. Degradation of technical PCB mixtures containing low and highly chlorinated congeners (Delor 103 and Delor 106 as equivalents of Aroclor 1242 and Aroclor 1260, respectively) was performed using intact mycelium, crude extracellular liquid and enriched MnP and LiP. A decrease in PCB concentration caused by a 44-h treatment with mycelium (74% w/w for Delor 103 and 73% for Delor 106) or crude extracellular liquid (62% for Delor 103 and 58% for Delor 106) was observed. The degradation was not substrate-specific, because no significant differences between the respective degradation rates were observed with di-, tri-, tetra-, penta-, hexa-, hepta-, and octachlorinated congeners. In contrast, MnP and LiP isolated from the above-mentioned extracellular liquid did not catalyse any degradation.