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.     

Arylglycerol-γ-Formyl Ester as an Aromatic Ring Cleavage Product of Nonphenolic β-O-4 Lignin Substructure Model Compounds Degraded by Coriolus versicolor

4-Ethoxy-3-methoxyphenylglycerol-γ-formyl ester (compound IV) was identified as a degradation product of both 4-ethoxy-3-methoxyphenylglycerol-β-syringaldehyde ether (compound I) and 4-ethoxy-3-methoxyphenylglycerol-β-2,6-dimethoxyphenyl ether (compound II) by a ligninolytic culture of Coriolus versicolor. An isotopic experiment with a ¹³C-labeled compound (compound II′) indicated that the formyl group of compound IV was derived from the β-phenoxyl group of β-O-4 dimer as an aromatic ring cleavage fragment. However, compound IV was not formed from 4-ethoxy-3-methoxyphenylglycerol-β-guaiacyl ether (compound III). γ-Formyl arylglycerol (compound IV) could be a precursor of 4-ethoxy-3-methoxyphenylglycerol (compound VI), because 3-(4-ethoxy-3-methoxyphenyl)-1-formyloxy propane (compound VII) was cleaved to give 3-(4-ethoxy-3-methoxyphenyl)-1-propanol (compound VIII) by C. versicolor. 4-Ethoxy-3-methoxyphenylglycerol-β,γ-cyclic carbonate (compound V), previously found as a degradation product of compound III by Phanerochaete chrysosporium (T. Umezawa, and T. Higuchi, FEBS Lett., 25:123-126, 1985), was also identified from the cultures with compound I, II, and III and degraded to give the arylglycerol (compound VI). An isotopic experiment with ¹³C-labeled compounds II′ and III′ indicated that the carbonate carbon of compound V was derived from the β-phenoxyl groups of β-O-4 substructure.     

Incorporation of 18O2 and absence of stereospecificity in primary product formation during fungal metabolism of a lignin model compound

The metabolism of a lignin substructure model compound, 1,2-bis(3-methoxy-4-ethoxyphenyl)propane-1,3-diol (Ia) in ligninolytic cultures of Phanerochaete chrysosporium was studied to help elucidate the biochemical mechanism of lignin degradation. The primary reaction was cleavage of the model compound between C₁ and C₂ of the propane moiety to produce 1-(3-methoxy-4-ethoxyphenyl)ethane-1,2-diol and a C₆-C₁ product (probably 3-methoxy-4-ethoxybenzaldehyde). Other identified products arose secondarily; all were further metabolized. Even though the model compound was a mixture of four stereoisomers, no stereoselectivity was observed in its metabolism. In cultures under ¹⁸O₂, the initial cleavage produced the diol product with ≈70% enrichment by ¹⁸O in the benzyl alcohol group. The diol was a mixture of the two possible enantiomers, and the O₂-derived hydroxyl was incorporated at the asymmetric (benzyl) carbon. (Limited optical activity in the diol was traced to selective further metabolism of the D form.) These results show that the primary cleavage reaction lacked stereospecificity and was primarily oxygenative, implicating a nonspecific oxygenase or a nonenzymatic reaction involving activated oxygen. Preliminary experiments demonstrated no cell homogenate activity against Ia.     

Chlorination and Cleavage of Lignin Structures by Fungal Chloroperoxidases

Two fungal chloroperoxidases (CPOs), the heme enzyme from Caldariomyces fumago and the vanadium enzyme from Curvularia inaequalis, chlorinated 1-(4-ethoxy-3-methoxyphenyl)-2-(2-methoxyphenoxy)-1,3-dihydroxypropane, a dimeric model compound that represents the major nonphenolic structure in lignin. Both enzymes also cleaved this dimer to give 1-chloro-4-ethoxy-3-methoxybenzene and 1,2-dichloro-4-ethoxy-5-methoxybenzene, and they depolymerized a synthetic guaiacyl lignin. Since fungal CPOs occur in soils and the fungi that produce them are common inhabitants of plant debris, CPOs may have roles in the natural production of high-molecular-weight chloroaromatics and in lignin breakdown.     

Metabolism of non-phenolic diarylpropane lignin substructure model compound by Coriolus versicolor

Abstract A lignin substructure model, 1-(4-ethoxy-3,5-dimethoxyphenyl)-2-(4-ethoxy-3-methoxyphenyl)-propane-1,3-diol(I), was actively metabolized by a white-rot fungus Coriolus versicolor in low nitrogen stationary cultures favouring the ligninolytic activity in the fungus. Cleavage of the dimer I between C_α and C_β of the propanoid side chain was the major degradative reaction by the fungus.     

Purification and characterization of an extracellular H2O2-requiring diarylpropane oxygenase from the white rot basidiomycete, Phanerochaete chrysosporium

An H2O2-requiring oxygenase found in the extracellular medium of ligninolytic cultures of the white rot fungus Phanerochaete chrysosporium was purified by DEAE-Sepharose ion-exchange chromatography and gel filtration on Sephadex G-100. Sodium dodecyl sulfate (SDS)-disc gel electrophoresis indicated that the purified protein was homogeneous. The Mr of the enzyme as determined by gel filtration and SDS-polyacrylamide gel electrophoresis was 41,000. The absorption spectrum of the enzyme indicated the presence of a heme prosthetic group. The absorption maximum of the native enzyme (407 nm) shifted to 435 nm in the reduced enzyme and to 420 nm in the reduced-CO complex. The pyridine hemochrome absorption spectrum indicated that the enzyme contained one molecule of heme as iron protoporphyrin IX. Both CN- and N-3 bound readily to the native enzyme, indicating an available coordination site and that the heme iron was high spin. The purified enzyme generated ethylene from 2-keto-4-thiomethyl butyric acid, and oxidized a variety of lignin model compounds, including the diarylpropane, 1-(3'4'-diethoxyphenyl)1,3-dihydroxy-2-(4"-methoxyphenyl)propane (I); a beta-ether dimer, 1-(4'-ethoxy-3'-methoxyphenyl)glycerol-beta-guaiacyl ether (V); an olefin, 1-(4'-ethoxy-3'-methoxyphenyl)-1,2 propene (III); and a diol, 1-(4'-ethoxy-3'-methoxyphenyl)-1,2-propane diol (IV). The products found were equivalent to the metabolic products previously isolated from intact ligninolytic cultures.     

Aromatic ring cleavage of a non-phenolic beta-O-4 lignin model dimer by laccase of Trametes versicolor in the presence of 1-hydroxybenzotriazole

The novel cleavage products, 2,3-dihydroxy-1-(4-ethoxy-3-methoxyphenyl)-1-formyloxypropane (II) and 1-(4-ethoxy-3-methoxyphenyl)-1,2,3-trihydroxypropane-2,3-cyclic carbonate (III) were identified as products of a non-phenolic beta-O-4 lignin model dimer, 1,3-dihydroxy-2-(2,6-dimethoxylphenoxy)-1-(4-ethoxy-3-methoxypheny l)propane (I), by a Trametes versicolor laccase in the presence of 1-hydroxybenzotriazole (1-HBT). An isotopic experiment with a 13C-labeled lignin model dimer, 1,3-dihydroxy-2-(2,6-[U-ring-13C] dimethoxyphenoxy)-1-(4-ethoxy-3-methoxyphenyl)propane (I-13C) indicated that the formyl and carbonate carbons of products II and III were derived from the beta-phenoxy group of beta-O-4 lignin model dimer I as aromatic ring cleavage fragments. These results show that the laccase-1-HBT couple could catalyze the aromatic ring cleavage of non-phenolic beta-O-4 lignin model dimer in addition to the beta-ether cleavage, Calpha-Cbeta cleavage, and Calpha-oxidation.     

Production of Ligninases and Degradation of Lignin in Agitated Submerged Cultures of Phanerochaete chrysosporium

Research on the extracellular hemeprotein ligninases of Phanerochaete chrysosporium has been hampered by the necessity to produce them in stationary culture. This investigation examined the effects of detergents on development of ligninase activity in agitated submerged cultures. Results show that addition of Tween 80, Tween 20, or 3-[(3-colamidopropyl)dimethylammonio]1-propanesulfonate to the cultures permits development of ligninase activity comparable to that routinely obtained in stationary cultures. The detergent-amended cultures express the entire ligninolytic system, assayed as the complete oxidation of [¹⁴C]lignin to ¹⁴CO₂. The detergent effect is evidently not merely in facilitating release of extant enzyme. Development of ligninolytic activity in the agitated cultures, as in stationary cultures, is idiophasic. Ion-exchange fast protein-liquid chromatography indicated that the heme protein profiles in agitated and stationary cultures are very similar. These findings should make it possible to scale up production of ligninolytic enzymes in stirred tank fermentors.     

Biochemistry of the oxidation of lignin by Phangerochate chrysosporium

The objective of this research was to identify the biochemical agents responsible for the oxidative degradation of lignin by the white-rot fungus . We examined the hypothesis that activated oxygen species are involved, and we also sought the agent in ligninolytic cultures responsible for a specific oxidative degradative reaction in substructure model compounds. Results of studies of the production of activated oxygen species by cultures, of the effect of their removal on ligninolytic activity, and of their action on substructure model compounds support a role for hydrogen peroxide (H₂O₂) and possibly superoxide (O₂ ·^-) in lignin degradation. Involvement of hydroxyl radical (·OH) or singlet oxygen (¹O₂) is not supported by our data. The actual biochemical agent responsible for one important oxidative C-C bond cleavage reaction in non-phenolic lignin substructure model compounds, and in lignin itself, was found to be an enzyme. The enzyme is extracellular, has a molecular weight of 42,000 daltons, is azide-sensitive, and requires H₂O₂ for activity.     

Metabolism of Radiolabeled β-Guaiacyl Ether-Linked Lignin Dimeric Compounds by Phanerochaete chrysosporium

Phanerochaete chrysosporium metabolized the radiolabeled lignin model compounds [γ-¹⁴C]guaiacylglycerol-β-guaiacyl ether and [4-methoxy-¹⁴C]veratrylglycerol-β-guaiacyl ether (VI) to ¹⁴CO₂ in stationary and in shaking cultures. ¹⁴CO₂ evolution was greater in stationary culture. ¹⁴CO₂ evolution from [γ-¹⁴C]guaiacyl-glycerol-β-guaiacyl ether and [4-methoxy-¹⁴C]veratrylglycerol-β-guaiacyl ether in stationary cultures was two- to threefold greater when 100% O₂ rather than air (21% O₂) was the gas phase above the cultures. ¹⁴CO₂ evolution from the metabolism of the substrates occurred only as the culture entered the stationary phase of growth. The presence of substrate levels of nitrogen in the medium suppressed ¹⁴CO₂ evolution from both substrates in stationary cultures. [¹⁴C]veratryl alcohol and 4-ethoxy-3-methoxybenzyl alcohol were formed as products of the metabolism of VI and 4-ethoxy-3-methoxyphenylglycerol-β-guaiacyl ether, respectively.     

Chlorination and cleavage of lignin structures by fungal chloroperoxidases

Two fungal chloroperoxidases (CPOs), the heme enzyme from Caldariomyces fumago and the vanadium enzyme from Curvularia inaequalis, chlorinated 1-(4-ethoxy-3-methoxyphenyl)-2-(2-methoxyphenoxy)-1,3-dihydroxypropane, a dimeric model compound that represents the major nonphenolic structure in lignin. Both enzymes also cleaved this dimer to give 1-chloro-4-ethoxy-3-methoxybenzene and 1,2-dichloro-4-ethoxy-5-methoxybenzene, and they depolymerized a synthetic guaiacyl lignin. Since fungal CPOs occur in soils and the fungi that produce them are common inhabitants of plant debris, CPOs may have roles in the natural production of high-molecular-weight chloroaromatics and in lignin breakdown.     

New alkaloids from Aegle marmelos

Four new alkaloids, O-(3,3-dimethylallyl)-halfordinol, N-2-ethoxy-2-(4-methoxyphenyl)ethylcinnamamide, N-2-methoxy-2-[4-(3′,3′-dimethyl     

FT-IR and 1H NMR spectroscopic evidence of sugar ring conformational change in NH4GpG on complexation to form cis-[Pt(NH3)2(GpG)]+

The conformational change of the ribose ring in NH₄GpG and cis-[Pt(NH₃)₂(GpG)]⁺ was confirmed by FT-IR spectroscopic evidence as being C2′-endo, C3′-endo, anti, gg sugar ring pucker in the solid state. These results were compared with ¹H NMR spectral data in aqueous solution. The FT-IR spectrum of NH₄GpG shows marker bands at 802 cm^?1 and 797 cm^?1 which are assigned to the C3′-endo, anti, gg sugar-phosphate vibrations of ribose (?pG) and ribose (Gp?), respectively. The FT-IR spectrum of cis-[Pt(NH₃)₂(GpG)]⁺ (with N7N7 chelation in the GpG sequence) shows a marker band at 800 cm^?1 which is assigned to the C3′-endo, and a new shoulder band at 820 cm^?1 related to a C2′-endo ring pucker. The ribose conformation of (?pG) moiety in NH₄-GpG, C3′-endo, anti, gg changes into C2′-endo, anti, gg when a platinum atom is chelated to N7N7 in the GpG sequence.     

Dilignol glycosides from needles of Picea abies

(2R,3R)-2 3-Dihydro-2-(4′-hydroxy-3′-methoxyphenyl)-3-(hydroxymethyl)-7-methoxy-5-benzofuranpropanol 4′-O-β-d-glucopyranoside [dihydrodehydrodiconiferyl alcohol glucoside], (2R,3R)-2 3-dihydro-7-hydroxy-2-(4′-hydroxy-3′-methoxyphenyl)-3-(hydroxymethyl)-5-benzofuranpropanol 4′-O-β-d-glucopyranoside and 4′-O-α-l-rhamnopyranoside, 1-(4′-hydroxy-3′-methoxyphenyl)-2- [2″-hydroxy-4″-(3-hydroxypropyl)phenoxy]-1, 3-propanediol 1-O-β-d-glucopyranoside and 4′-O-β-d-xylopyranoside, 2,3-bis[(4′-hydroxy-3′-methoxyphenyl)-methyl]-1,4-butanediol 1-O-β-d-glucopyranoside [(?)-seco-isolariciresinol glucoside] and (1R,2S,3S)-1,2,3,4-tetrahydro-7-hydroxy-1-(4′-hydroxy-3′-methoxyphenyl)-6-methoxy-2 3-naphthalenedimethanol α²-O-β-d-xylopyranoside [(?)-isolariciresinol xyloside] have been isolated from needles of Picea abies and identified.     

Influence of NaCl and Na2SO4 on the kinetics and dye decolorization ability of crude laccase from Ganoderma lucidum

In a solid state medium using yellow passion fruit waste as substrate, the basidiomycete Ganoderma lucidum produced a laccase as the main ligninolytic enzyme. This crude enzyme presented Michaelian behavior with both substrates tested, namely 3-ethylbenzthiazoline-6-sulphonic acid (ABTS) and the anthraquinone dye remazol brilliant blue R (RBBR). The K_M’s for these substrates were, respectively, 0.232 × 10⁻³ and 0.602 × 10⁻³ M. The actions of NaCl and Na₂SO₄, two important salts usually found in textile wastewaters, were investigated. The enzyme was inhibited by NaCl, but not by Na₂SO₄. Inhibition by NaCl was of the mixed type with two different inhibition constants. The enzyme was able to completely decolorize RBBR in the presence of 1.0 M Na₂SO₄ and 50% decolorization was found in the presence of 0.1 M NaCl. Such properties certainly make the enzyme a good agent for textile dye effluent treatment considering the fact that wastewaters of this industry usually contain high concentrations of NaCl and Na₂SO₄.     

Degradation of the gamma-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 [C]lignin to CO(2). 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 alpha, beta 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 O(2), O was incorporated into the beta position of the diarylethane product (VII), indicating that the reaction is oxygenative.     

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.     

p-Benzoquinone monoketals,novel degradation products of β-O-4 lignin model compounds by Coriolus versicolor and lignin peroxidase of Phanerochaete chrysosporium

2-(4-Ethoxy-3-methoxyphenyl)-3-hydroxymethyl-6,10-dimethoxy-1,4-dioxaspiro[4,5]deca-6,9-diene-8-one (III) and its isomer IV were identified as catabolites of 4-ethoxy-3-methoxyphenylglycerol-β-syringaldehyde ether (I) by the culture of Coriolus versicolor. Compound III was also produced from 4-ethoxy-3-methoxyphenylglycerol-β-syringic acid ether (II) by lignin peroxidase of Phanerochaete chrysosporium. An isotopic experiment showed that molecular oxygen was incorporated into the quinone oxygen of III in the degradation of II by lignin peroxidase.     

Arylglycerol-gamma-Formyl Ester as an Aromatic Ring Cleavage Product of Nonphenolic beta-O-4 Lignin Substructure Model Compounds Degraded by Coriolus versicolor

4-Ethoxy-3-methoxyphenylglycerol-gamma-formyl ester (compound IV) was identified as a degradation product of both 4-ethoxy-3-methoxyphenylglycerol-beta-syringaldehyde ether (compound I) and 4-ethoxy-3-methoxyphenylglycerol-beta-2,6-dimethoxyphenyl ether (compound II) by a ligninolytic culture of Coriolus versicolor. An isotopic experiment with a C-labeled compound (compound II') indicated that the formyl group of compound IV was derived from the beta-phenoxyl group of beta-O-4 dimer as an aromatic ring cleavage fragment. However, compound IV was not formed from 4-ethoxy-3-methoxyphenylglycerol-beta-guaiacyl ether (compound III). gamma-Formyl arylglycerol (compound IV) could be a precursor of 4-ethoxy-3-methoxyphenylglycerol (compound VI), because 3-(4-ethoxy-3-methoxyphenyl)-1-formyloxy propane (compound VII) was cleaved to give 3-(4-ethoxy-3-methoxyphenyl)-1-propanol (compound VIII) by C. versicolor. 4-Ethoxy-3-methoxyphenylglycerol-beta,gamma-cyclic carbonate (compound V), previously found as a degradation product of compound III by Phanerochaete chrysosporium (T. Umezawa, and T. Higuchi, FEBS Lett., 25:123-126, 1985), was also identified from the cultures with compound I, II, and III and degraded to give the arylglycerol (compound VI). An isotopic experiment with C-labeled compounds II' and III' indicated that the carbonate carbon of compound V was derived from the beta-phenoxyl groups of beta-O-4 substructure.     

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.