Involvement of singlet oxygen in the fungal degradation of lignin

The possible involvement of singlet oxygen (¹O₂) in the degradation of lignin by $\text{Phanerochaete}\text{chrysosporium}$ was examined. Ligninolytic cultures and photochemically generated ¹O₂ gave the same oxidation products from the lignin substructure model compound 1,2-bis(3-methoxy-4-alkoxyphenyl)propan-1,3-diol. Fluorescence and near UV absorbance of the specific ¹O₂ trapping agent anthracene-9,10-bisethanesulfonic acid (AES) disappeared in ligninolytic cultures, indicating that ¹O₂ was produced. AES strongly inhibited oxidation of ¹⁴C-lignin, but not ¹⁴C-glucose, to ¹⁴CO₂ in cultures, and also strongly suppressed oxidation of the model compound. These results indicate the ¹O₂ plays an integral role in lignin biodegradation.     

Effects of melecular oxygen on lignin degradation by Phanerochaete chrysosporium

Research has demonstrated that shallow stationary cultures of white-rot wood-destroying Basidiomycetes degrade lignin (¹⁴C-lignin → ¹⁴CO₂) at much higher rates under O₂ than under air. The present study, conducted with $\text{Phanerochaete chrysosporium}$, showed that the effect on rate is a dual one: a) Immediately preceeding appearance of the lignin-degrading system the partial pressure of O₂ determines the amount of ligninolytic activity that develops in cultures; and b) after the system develops, the partial pressure of O₂ affects the rate of oxidation.     

Characterization of glucose oxidase-negative mutants of a lignin degrading basidiomycete Phanerochaete chrysosporium

The isolation and characterization of glucose oxidase-negative (gox ^-) mutants of Phanerochaete chrysosporium, is described. These mutants are deficient not only in their ability to produce hydrogen peroxide (H₂O₂) but also in lignin degradation (2-¹⁴C-synthetic lignin¹⁴CO₂), ligninase and peroxidase activities, decolorization of the dye poly-R 481, and production of ethylene from -oxo--methylthiobutyric acid (KTBA). The gox ^- mutants retained, albeit at a lower level, the capacity to produce veratryl alcohol, a typical secondary metabolite, and produced conidia at a level comparable to that of the wild type. The addition of ligninase and/or glucose oxidase to a gox ^- mutant (GOX-10) did not enhance its capacity to degrade lignin. The Gox⁺ revertant strains regained glucose oxidase activity, the ability to degrade lignin, as well as the other characteristics that were missing in the gox ^- mutants. The results suggest that the genetic lesion in these mutants affects the regulation of a set of secondary metabolic characteristics.Abbreviations Gox glucose oxidase - KTBA -oxo--methylthiobutyric acid Journal article no. 11740 from the Michigan Agricultural Experiment Station     

An extracellular H2O2-requiring enzyme preparation involved in lignin biodegradation by the white rot basidiomycete Phanerochaete chrysosporium

An H₂O₂-requiring enzyme system was found in the extracellular medium of ligninolytic cultures of Phanerochaete chrysosporium. The enzyme system generated ethylene from 2-keto-4-thiomethyl butyric acid (KTBA), and oxidized a variety of lignin model compounds including the diarylpropane 1-(4′-ethoxy-3′-methoxyphenyl) 1,3-dihydroxy-2-(4″-methoxyphenyl)propane (I), a β-ether dimer 1-(4′-ethoxy-3′-methoxyphenyl)glycerol-β-guaiacyl ether (IV) and an olefin 1-(4′-ethoxy-3′-methoxy-phenyl)1,2-propene (VI). The products found were equivalent to the metabolic products previously isolated from intact ligninolytic cultures. In addition, the enzyme system partially degraded ¹⁴C-ring labeled lignin. The enzyme was not found in high nitrogen (N) cultures, nor in cultures of a ligninolytic mutant strain which is incapable of metabolizing lignin.     

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.     

Lignocellulose Degradation during Solid-State Fermentation: Pleurotus ostreatus versus Phanerochaete chrysosporium

Lignocellulose degradation and activities related to lignin degradation were studied in the solid-state fermentation of cotton stalks by comparing two white rot fungi, Pleurotus ostreatus and Phanerochaete chrysosporium. P. chrysosporium grew vigorously, resulting in rapid, nonselective degradation of 55% of the organic components of the cotton stalks within 15 days. In contrast, P. ostreatus grew more slowly with obvious selectivity for lignin degradation and resulting in the degradation of only 20% of the organic matter after 30 days of incubation. The kinetics of ¹⁴C-lignin mineralization exhibited similar differences. In cultures of P. chrysosporium, mineralization ceased after 18 days, resulting in the release of 12% of the total radioactivity as ¹⁴CO₂. In P. ostreatus, on the other hand, 17% of the total radioactivity was released in a steady rate throughout a period of 60 days of incubation. Laccase activity was only detected in water extracts of the P. ostreatus fermentation. No lignin peroxidase activity was detected in either the water extract or liquid cultures of this fungus. 2-Keto-4-thiomethyl butyric acid cleavage to ethylene correlated to lignin degradation in both fungi. A study of fungal activity under solid-state conditions, in contrast to those done under defined liquid culture, may help to better understand the mechanisms involved in lignocellulose 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.     

Effects of Nitrogen Supplements on Degradation of Aspen Wood Lignin and Carbohydrate Components by Phanerochaete chrysosporium

A supplement of KH₂PO₄, MgSO₄, CaCl₂, trace elements, and thiamine accelerated the initial rate of aspen wood decay by Phanerochaete chrysosporium but did not increase the extent of lignin degradation. Asparagine, casein hydrolysate, and urea supplements (1% added N) strongly inhibited lignin degradation and weight loss. The complex nitrogen sources peptone and yeast extract stimulated lignin degradation and weight loss. Albumen and NH₄Cl had intermediate effects. Conversion of [¹⁴C]lignin to ¹⁴CO₂ and water-soluble materials underestimated lignin degradation in the presence of the complex N sources. The highest ratio of lignin degradation to total weight loss and the largest increase in cellulase digestibility occurred during the decay of unsupplemented wood. Rotting of aspen wood by P. chrysosporium gives smaller digestibility increases than have been found with some other white-rot fungi.     

Factors affecting lignin degradation in lignocellulose by Phanerochaete chrysosporium

Cultural conditions affecting lignin degradation by Phanerochaete chrysosporium in various lignocellulosic materials were studied in comparison to an isolated lignin preparation. With shallow mycelial cultures, the degradation of lignin in wood proceeded more slowly in a 100% O₂-atmosphere than in an air atmosphere, indicating that pure oxygen was toxic to the fungus. The organism was able to degrade lignin efficiently even under 30% CO₂ and 10% O₂ concentrations. Evolution of ¹⁴CO₂ from labelled lignocellulosic materials was shown not to be representative of total lignin degradation. Addition of glucose to the culture did not affect lignin degradation measured by ¹⁴CO₂ evolution, whereas lignin degradation measured by Klason lignin method stopped completely (poplar) or slowed considerably (straw). Due to partial depolymerization of lignin to soluble products, measuring only the evolution of ¹⁴CO₂ results in an underestimation of the total amount of lignin bioaltered. The soluble products from all of the tested lignocellulosic materials and from the isolated lignin had an average molecular weight of about 1,000 and the products could be further fractionated by ion exchange chromatography. The relative amount of these products could be varied from 15 to 45% from the original lignin.     

Effects of Nitrogen Sources on Cellulose and Synthetic Lignin Degradation by Phanerochaete chrysosporium

Phanerochaete chrysosporium degraded cellulose faster with organic nitrogen sources than with NH₄Cl. Simple and complex nitrogen sources added at the time of inoculation to N-limited cultures of P. chrysosporium, with glucose as carbon/energy source, transiently stimulated degradation of synthetic [¹⁴C]lignin to ¹⁴CO₂. The same nitrogen sources added 5 days after inoculation, when the cultures were entering secondary metabolism, delayed ¹⁴CO₂ production. The various N sources affected synthetic lignin degradation in defined medium differently than lignin degradation in aspen wood.     

Degradation of the γ-Carboxyl-Containing Diarylpropane Lignin Model Compound 3-(4′-Ethoxy-3′-Methoxyphenyl)-2-(4″-Methoxyphenyl)Propionic Acid by the Basidiomycete Phanerochaete chrysosporium

The white-rot basidiomycete Phanerochaete chrysosporium metabolized 3-(4′-ethoxy-3′-methoxyphenyl)-2-(4″-methoxyphenyl)propionic acid (V) in low-nitrogen, stationary cultures, conditions under which ligninolytic activity is expressed. The ability of several fungal mutant strains to degrade V reflected their ability to degrade [¹⁴C]lignin to ¹⁴CO₂. 1-(4′-Ethoxy-3′-methoxyphenyl)-2-(4″-methoxyphenyl)-2- hydroxyethane (VII), anisyl alcohol, and 4-ethoxy-3-methoxybenzyl alcohol were isolated as metabolic products, indicating an initial oxidative decarboxylation of V, followed by α, β cleavage of the intermediate (VII). Exogenously added VII was rapidly converted to anisyl alcohol and 4-ethoxy-3-methoxybenzyl alcohol. When the degradation of V was carried out under ¹⁸O₂, ¹⁸O was incorporated into the β position of the diarylethane product (VII), indicating that the reaction is oxygenative.     

The ligninolytic activities of Lentinus edodes and Phanerochaete chrysosporium

Summary Two important lignin-degrading fungi with existing or potential applications in the production of food, feed and/or fiber products from wood are Lentinus edodes (Berk.; Sing.=Lentinula edodes [Pegler]) and Phanerochaete chrysosporium (Burds). This study discusses their relative ability to degrade lignin and the factors controlling their ligninolytic activity (synthetic ¹⁴C-lignin¹⁴CO₂). Ligninolytic activity in P. chrysosporium is known to develop after the fungus ceases vegetative growth, and to require both O₂ and an exogenous carbon source such as glucose. It has an extracellular ligninase in high titer which is assayed by the oxidation of veratryl alcohol to veratraldehyde. Here, P. chrysosporium was found to have a high capacity for lignin degradation (it was not easily saturated with lignin). Certain inorganic elements, including Fe²⁺, Ca²⁺ and Mo⁶⁺, were found to stimulate its ligninolytic activity. Calcium addition was required, with 40 ppm Ca²⁺ giving the highest activity. As in P. chrysosporium, ligninolytic activity in L. edodes was found to require both O₂ and an exogenous carbon source. However, in contrast to P. chrysosporium, L. edodes was only moderately ligninolytic, had a lower capacity for lignin degradation (was more easily saturated with lignin), and showed maximal activity only during the vegetative growth period. Also in contrast to P. chrysosporium, ligninolytic activity in L. edodes was not stimulated by Ca²⁺. Instead, manganese was required, with 10 ppm Mn²⁺ giving optimal activity. An extracellular ligninase capable of oxidizing veratryl alcohol to veratraldehyde was not detected in L. edodes.     

Influence of laboratory maintenance,relative humidity and coprophagy on [14C]lignin degradation by Nasutitermes exitiosus

[¹⁴C](lignin)-Acer rubrum L. was produced by infusing stems of A. rubrum with [¹⁴C](3′-side chain)-cinnamic acid. Groups (1g) of Nasutitermes exitiosus (Hill) were placed in sealed flasks which were aspirated over a 2-week period. These released up to 8.3% of the [¹⁴C](lignin)-A. rubrum as ¹⁴CO₂. Termites maintained under standard conditions as 50 g non-breeding groups for 4 months or more showed diminished ability to degrade lignin. Optimal lignin degradation and survival of N. exitiosus was at 90 and 96% relative humidity (r.h.). At 75, 80 and 85% r.h., fungal growth in bioassay flasks was seen, but lignin degradation did not increase. At 100% r.h. where bacterial growth in faeces may have been encouraged due to the development of free water, termite survival was poor and lignin degradation decreased. Starved termites contained much more radioactivity (21.8 and 30.8%) than fed termites (1.6% radioactivity), probably due to greater coprophagy on deprivation of food. However, lignin degradation was only marginally higher in starved termites, suggesting lignin becomes progressively more resistant to termite degradation after passage through the gut.     

Factors influencing fungal degradation of lignin in a representative lignocellulosic,thermomechanical pulp

This research examined culture parameters influencing the rate of degradation of lignin in lignocellulosic substrates by the Basidiomycete Phanerochaete chrysosporium. Thermomechanical pulps prepared from western hemlock (Tsuga heterophylla) and red alder (Alnus rubra) were chosen as model substrates. Degradation of lignin in shallow, liquid-phase, stationary cultures was 10 times as rapid as in agitated cultures. Lignin degradation was at least 50% more rapid in cultures under 100% O₂ than in those under air. Addition of 0.12% nutrient N (dry pulp basis) increased the rate of lignin degradation two- to fivefold; 1.2% added N at first suppressed, then stimulated, lignin degradation. Lignin in the alder pulp was degraded over five times as rapidly as in the hemlock pulp. Addition of glucose (35% of dry pulp) to the pulps containing 0.12% added N completely suppressed polysaccharide depletion during two weeks, but did not influence lignin degradation. The maximum rate of lignin degradation was 3%/day over a two-week incubation, or approximately 2.9 mg/mg fungal cell protein/day. The influence of the examined parameters was in complete accord with those found earlier for synthetic ¹⁴C-lignin metabolism by P. chrysosporium.     

Solubilization and Mineralization of Lignin by White Rot Fungi

The white rot fungi Lentinula edodes, Phanerochaete chrysosporium, Pleurotus sajor-caju, Flammulina velutipes, and Schizophyllum commune were grown in liquid media containing ¹⁴C-lignin-labelled wood, and the formation of water-soluble ¹⁴C-labelled products and ¹⁴CO₂, the growth of the fungi, and the activities of extracellular lignin peroxidase, manganese peroxidase, and laccase were measured. Conditions that affect the rate of lignin degradation were imposed, and both long-term (0- to 16-day) and short-term (0- to 72-h) effects on the production of the two types of product and on the activities of the enzymes were monitored. The production of ¹⁴CO₂-labelled products from the aqueous ones was also investigated. The short-term studies showed that the different conditions had different effects on the production of the two products and on the activities of the enzymes. Nitrogen sources inhibited the production of both products by all species when differences in growth could be discounted. Medium pH and manganese affected lignin degradation by the different species differently. With P. chrysosporium, the results were consistent, with lignin peroxidase playing a role in lignin solubilization and manganese peroxidase being important in subsequent CO₂ production.     

Poplar Lignin Decomposition by Gram-Negative Aerobic Bacteria

Eleven gram-negative aerobic bacteria (Pseudomonadaceae and Neisseriaceae) out of 122 soil isolates were selected for their ability to assimilate poplar dioxane lignin without a cosubstrate. Dioxane lignin and milled wood lignin degradation rates ranged between 20 and 40% of initial content after 7 days in mineral medium, as determined by a loss of absorbance at 280 nm; 10 strains could degrade in situ lignin, as evidenced by the decrease of the acetyl bromide lignin content of microtome wood sections. No degradation of wood polysaccharides was detected. Lignin biodegradation by Pseudomonas 106 was confirmed by ¹⁴CO₂ release from labeled poplar wood, although in lower yields compared with results obtained through chemical analysis based on acetyl bromide residual lignin determination.     

Methanol formation during lignin degradation by Phanerochaete chrysosporium

Summary Methanol formation during the degradation of synthetic lignin (DHP), spruce and birch milled wood lignin (MWL) by Phanerochaete chrysosporium Burds. was studied under different culture conditions. When 100-ml flasks with 15–20 ml volumes of culture media containing high glucose and low nitrogen concentrations were used the metabolism of methanol to formaldehyde, formic acid and CO₂ was repressed thereby facilitating methanol determination. In standing cultures with oxygen flushing the fungus converted up to 25% of the DHP-methoxyl groups to methanol and 0.5–1.5% to ¹⁴CO₂ within 22–24 h. Methanol formation from methoxyl-labelled DHP was strongly repressed by high nitrogen in the medium, by addition of glutamic acid and by culture agitation. These results indicate that methanol is formed only under ligninolytic conditions and during secondary metabolism. Methanol is most likely released both from the lignin polymer itself and from lignin degradation products. Methanol was also formed from MWL preparations with higher percentage yields produced from birch as compared to spruce MWL.Small amounts of methanol detected in cultures without lignin probably emanated from demethoxylation of veratryl alcohol synthesized de novo from glucose by the fungus during secondary metabolism. Catalase or superoxide dismutase added to the fungal culture prior to addition of lignin, did not decrease methanol formation. Horseradish peroxidase plus H₂O₂ in vitro caused 5–7% demethoxylation of O¹⁴CH₃-DHP in 22 h, while laccase gave smaller amounts of methanol (1.8%). Since addition of H₂O₂ gave similar results as peroxidase plus H₂O₂, it seems likely that the main effect of peroxidase demethoxylation emanates from the hydrogen peroxide.     

Biodegradation of 2,4,6-trinitrotoluene byPhanerochaete chrysosporium: Identification of initial degradation products and the discovery of a TNT metabolite that inhibits lignin peroxidases

Biodegradation of 2,4,6-trinitrotoluene (TNT) by the wood-rotting BasidiomycetePhanerochaete chrysosporium was studied in a fixed-film silicone membrane bioreactor and in agitated pellected cultures. The initial intermediate products of TNT biodegradation were shown to be 2-amino-4,6-dinitrotoluene (2amDNT) and 4-amino-2,6-dinitrotoluene (4amDNT). These intermediates were also degraded byP. chrysosporium. However, their rates of degradation were slow and appeared to represent rate-limiting steps in TNT degradation. The fact that 2amDNT and 4amDNT were further degraded is of importance. In most other microbial systems these compounds are typically not further degraded or are dimerized to even more persistent azo and azoxydimers. Similar to previous studies performed in stationary cultures, it was shown that substantial amounts of [¹⁴C]-TNT were degrade to [¹⁴C]-carbon dioxide in agitated pelleted cultures. Lignin peroxidase activity (assayed by veratryl alcohol oxidation) virtually disappeared upon addition of TNT to ligninolytic cultures ofP. chrysosporium. However, TNT, 2amDNT, and 4amDNT did not inhibit lignin peroxidase activity, nor were they substrates for this enzyme. Subsequent studies revealed that 4-hydroxylamino-2,6-dinitrotoluene, an intermediate in TNT reduction, was a potent lignin peroxidase inhibitor. Further studies revealed that this compound was also a substrate for lignin peroxidase H8.     

Ligninolytic system of Phanerochaete chrysosporium: Inhibition by o-Phthalate

The degradation rate of [synthetic-¹⁴C]-lignin to ¹⁴CO₂ by Phanerochaete chrysosporium in cultures buffered with 0.01 M 2,2-dimethylsuccinate (DMS) was twice that in 0.01 M o-phthalate-buffered cultures. This difference could be totally accounted for by o-phthalate inhibition of the activity of the ligninolytic system. ¹⁴CO₂ production from ring-, sidechain-, and methoxyl-labeled lignins was inhibited, the degree of inhibition being dependent on o-phthalate concentration. Oxidations of ¹⁴C-glucose, ¹⁴C-acetovanillone, and ¹⁴C-apocynol were not inhibited; thus o-phthalate is not a general inhibitor, and might inhibit activities involved in attack of the lignin polymer. DMS is a suitable buffer for the ligninolytic system. Degradation rates of ring-labeled lignin to ¹⁴CO₂ of 10–15% in 24 h were obtained consistently over the pH range 3.6–4.5, with an optimum near pH 4.0.Non-Standard Abbreviations DMS dimethylsuccinate     

Iron(II)-bleomycin. Biochemical and spectral properties in the presence of radical scavengers

Consistent with a recent literature report (Repine, J. E. $\text{et}$$\text{al.}$ (1981) $\text{Proc.}$$\text{Nat.}$$\text{Acad.}$$\text{Sci.}$$\text{USA}$$\text{7}\text{?}$$\text{8}\text{?}$, 1001–1003), the release of [³H]-thymine from PM-2 DNA by Fe(II)-H₂O₂-generated ·OH was suppressed by dimethyl sulfoxide. In contrast, DMSO did not affect [³H]-thymine release mediated by Fe(II)-bleomycin. Under aerobic conditions in the presence of $\text{t}$-butyl phenylnitrone, Fe(II)-BLM produces an epr signal that has been presumed to arise by transfer of ·OH or $\text{O}{}_2{}^{\mathrm{<mtext>?</mtext>}}$ from the “active complex” of bleomycin to the spin trap. Remarkably, high concentrations (80 mM) of PBN had no effect on the ability of Fe(II)-BLM to solubilize [³H]-thymine, although the ability of authentic ·OH to degrade DNA was completely suppressed under these condition. The suproxide dismutase catalyst tetrakis(4-N-methylpyridyl)porphineiron(III) also failed to suppress BLM-mediated DNA degradation. Moreover, the epr signal observed with 1.6 mM Fe(II)-BLM in the presence of 80 mM PBN was found to be much less intense than that produced by 1.6 mM Fe(II) and 290 mM H₂O₂, but equivalent in intensity to that obtained with 45 mM Fe(II) and exoess H₂O₂. We conclude that the fragmentation of DNA produced by Fe(II)-BLM can be due neither to free ·OH nor to $\text{O}{}_2{}^{\mathrm{<mtext>?</mtext>}}$. We suggest that DNA degradation is initiated by an “active complex” consisting of BLM, metal and oxygen that functions by abstracting H· from susceptible sites on DNA.