Reduction and partial degradation mechanisms of naphthylaminesulfonic azo dye amaranth by <Emphasis Type="Italic">Shewanella decolorationis</Emphasis> S12

Reduction and biodegradation mechanisms of naphthylaminesulfonic azo dye amaranth using a newly isolated Shewanella decolorationis strain S12 were investigated. Under anaerobic conditions, amaranth was reduced by strain S12, and a stoichiometric amount of two reduction products RP-1 and RP-2 were generated. UV/visible spectrophotometric and high performance liquid chromatography (HPLC) analysis indicated that RP-1 and RP-2 were 1-aminenaphthylene -4-sulfonic acid and 1-aminenaphthylene-2-hydroxy-3, 6-disulfonic acid. The result strongly supports a mechanism of azo dye reduction by the process via the reductive cleavage of the azo bond to form corresponding aromatic amines. The result of HPLC analyses revealed that these aromatic amines were not able to be mineralized by strain S12 under anaerobic conditions. But after re-aeration of the decolorized culture, RP-2 was mineralized completely by this microorganism, but the consumption of RP-1 was not observed. Ames test showed that amaranth had mutagenic but no cytotoxic potential. The mutagenic potential was relieved after the anaerobic treatment with strain S12 as the mutagenic effect of the two reduction products from amaranth was not detected by Ames test. Thus, the ability of strain S12 to reduce and partially mineralize the naphthylaminesulfonic azo dye efficiently was demonstrated, which can potentially be used to biodegrade and detoxify wastewater containing azo dyes using an alternating anaerobic/aerobic treatment procedure.     

Decolorization of Textile Dyes and Degradation of Mono-Azo Dye Amaranth by <Emphasis Type="Italic">Acinetobacter calcoaceticus</Emphasis> NCIM 2890

Acinetobacter calcoaceticus NCIM 2890 (A. caloaceticus) was found to decolorize 20 different textile dyes of various classes. Decolorization of an azo dye amaranth was observed effectively (91%) at static anoxic condition, whereas agitated culture grew well but showed less decolorization (68%) within 48 h of incubation. Induction of intracellular and extracellular lignin peroxidase, intracellular laccase, dichlorophenol indophenol (DCIP) reductase and riboflavin reductase represented their involvement in the biodegradation of amaranth. The products obtained after degradation of Amaranth were characterized as naphthalene sulfamide, hydroxyl naphthalene diazonium and naphthalene diazonium. The germination and growth of Sorghum vulgare and Phaseolus mungo seeds, and the growth of E. coli and Bacillus substilis were not inhibited by the metabolic products of the dye.     

Decolorization and detoxification of sulphonated azo dye Red HE7B by <Emphasis Type="Italic">Bacillus</Emphasis> sp. VUS

Bacillus sp. VUS decolorized Red HE7B dye (100%) within 18 h in static anoxic conditions. A significant increase in activities of lignin peroxidase, laccase, NADH-DCIP and azo reductase was observed up to complete decolourization of RHE7B. The biodegradation was monitored by UV–Visible spectroscopy (UV–VIS), Fourier Transform Infrared (FTIR) spectroscopy and High Performance Liquid Chromatography (HPLC). The final products 4-methyl-3-(1-sulfo-ethyl)-5-([1,3,5] triazin-2-ylamino)-benzenesulfonic acid; 3-(1-sulfo-ethyl)-5-([1,3,5] triazin-2-ylamino)-benzenesulfonic acid and 3-(1,2-dihydro-[1,3,5] triazin-2-ylamino)-5-sulfomethyl-benzenesulfonic acid were characterized by gas chromatography–mass spectrometry (GC–MS). The phytotoxicity study revealed the non-toxic nature of the generated products with respect to Sorghum bicolor and Triticum aestivum. The metabolites produced after degradation increased the chlorophyll content of crop seedlings. The Ames test revealed the non-mutagenicity and non-carcinogenicity of the degraded products.     

Contribution of manganese peroxidase and laccase to dye decoloration by Trametes versicolor

During dye decoloration by Trametes versicolor ATCC 20869 in modified Kirk’s medium, manganese peroxidase (MnP) and laccase were produced, but not lignin peroxidase, cellobiose dehydrogenase or manganese-independent peroxidase. Purified MnP decolorized azo dyes [amaranth, reactive black 5 (RB5) and Cibacron brilliant yellow] in Mn²⁺-dependent reactions but did not decolorize an anthraquinone dye [Remazol brilliant blue R (RBBR)]. However, the purified laccase decolorized RBBR five to ten times faster than the azo dyes and the addition of a redox mediator, 2,2′-azino-bis(3-ethylbenzthiazoline-6-sulfonic acid), did not alter decoloration rates. Amaranth and RB5 were decolorized the most rapidly by MnP since they have a hydroxyl group in an ortho position and a sulfonate group in the meta position relative to the azo bond. During a typical batch decoloration with the fungal culture, the ratio of laccase:MnP was 10:1 to 20:1 (based on enzyme activity) and increased to greater than 30:1 after decoloration was complete. Since MnP decolorized amaranth about 30 times more rapidly than laccase per unit of enzyme activity, MnP should have contributed more to decoloration than laccase in batch cultures.     

Mineralization of sulfonated azo dyes and sulfanilic acid by Phanerochaete chrysosporium and Streptomyces chromofuscus.

Five 14C-radiolabeled azo dyes and sulfanilic acid were synthesized and used to examine the relationship between dye substitution patterns and biodegradability (mineralization to CO2) by a white-rot fungus and an actinomycete. 4-Amino-[U-14C]benzenesulfonic acid and 4-(3-sulfo-4-aminophenylazo)-[U-14C]benzenesulfonic acid were used as representative compounds having sulfo groups or both sulfo and azo groups. Such compounds are not known to be present in the biosphere as natural products. The introduction of lignin-like fragments into the molecules of 4-amino-[U-14C]benzenesulfonic acid and 4-(3-sulfo-4-aminophenylazo)-[U-14C]benzenesulfonic acid by coupling reactions with guaiacol (2-methoxyphenol) resulted in the formation of the dyes 4-(3-methoxy-4-hydroxyphenylazo)-[U-14C]benzenesulfonic acid and 4-(2-sulfo-3'-methoxy-4'-hydroxy-azobenzene-4-azo)-[U-14C]benzenesulf oni c acid, respectively. The synthesis of acid azo dyes 4-(2-hydroxy-1-naphthylazo)-[U-14C]benzenesulfonic acid and 4-(4-hydroxy-1-naphthylazo)-[U-14C]benzenesulfonic acid also allowed the abilities of these microorganisms to mineralize these commercially important compounds to be evaluated. Phanerochaete chrysosporium mineralized all of the sulfonated azo dyes, and the substitution pattern did not significantly influence the susceptibility of the dyes to degradation. In contrast, Streptomyces chromofuscus was unable to mineralize aromatics with sulfo groups and both sulfo and azo groups. However, it mediated the mineralization of modified dyes containing lignin-like substitution patterns. This work showed that lignocellulolytic fungi and bacteria can be used for the biodegradation of anionic azo dyes, which thus far have been considered among the xenobiotic compounds most resistant to biodegradation.(ABSTRACT TRUNCATED AT 250 WORDS)     

Mineralization of sulfonated azo dyes and sulfanilic acid by Phanerochaete chrysosporium and Streptomyces chromofuscus.

Five 14C-radiolabeled azo dyes and sulfanilic acid were synthesized and used to examine the relationship between dye substitution patterns and biodegradability (mineralization to CO2) by a white-rot fungus and an actinomycete. 4-Amino-[U-14C]benzenesulfonic acid and 4-(3-sulfo-4-aminophenylazo)-[U-14C]benzenesulfonic acid were used as representative compounds having sulfo groups or both sulfo and azo groups. Such compounds are not known to be present in the biosphere as natural products. The introduction of lignin-like fragments into the molecules of 4-amino-[U-14C]benzenesulfonic acid and 4-(3-sulfo-4-aminophenylazo)-[U-14C]benzenesulfonic acid by coupling reactions with guaiacol (2-methoxyphenol) resulted in the formation of the dyes 4-(3-methoxy-4-hydroxyphenylazo)-[U-14C]benzenesulfonic acid and 4-(2-sulfo-3'-methoxy-4'-hydroxy-azobenzene-4-azo)-[U-14C]benzenesulf oni c acid, respectively. The synthesis of acid azo dyes 4-(2-hydroxy-1-naphthylazo)-[U-14C]benzenesulfonic acid and 4-(4-hydroxy-1-naphthylazo)-[U-14C]benzenesulfonic acid also allowed the abilities of these microorganisms to mineralize these commercially important compounds to be evaluated. Phanerochaete chrysosporium mineralized all of the sulfonated azo dyes, and the substitution pattern did not significantly influence the susceptibility of the dyes to degradation. In contrast, Streptomyces chromofuscus was unable to mineralize aromatics with sulfo groups and both sulfo and azo groups. However, it mediated the mineralization of modified dyes containing lignin-like substitution patterns. This work showed that lignocellulolytic fungi and bacteria can be used for the biodegradation of anionic azo dyes, which thus far have been considered among the xenobiotic compounds most resistant to biodegradation.(ABSTRACT TRUNCATED AT 250 WORDS)     

Degradation of phenanthrene by <Emphasis Type="Italic">Burkholderia</Emphasis> sp. C3: initial 1,2- and 3,4-dioxygenation and <Emphasis Type="Italic">meta</Emphasis>- and <Emphasis Type="Italic">ortho</Emphasis>-cleavage of naphthalene-1,2-diol

Burkholderia sp. C3 was isolated from a polycyclic aromatic hydrocarbon (PAH)-contaminated site in Hilo, Hawaii, USA, and studied for its degradation of phenanthrene as a sole carbon source. The initial 3,4-C dioxygenation was faster than 1,2-C dioxygenation in the first 3-day culture. However, 1-hydroxy-2-naphthoic acid derived from 3,4-C dioxygenation degraded much slower than 2-hydroxy-1-naphthoic acid derived from 1,2-C dioxygenation. Slow degradation of 1-hydroxy-2-naphthoic acid relative to 2-hydroxy-1-naphthoic acid may trigger 1,2-C dioxygenation faster after 3 days of culture. High concentrations of 5,6-␣and 7,8-benzocoumarins indicated that meta-cleavage was the major degradation mechanism of phenanthrene-1,2- and -3,4-diols. Separate cultures with 2-hydroxy-1-naphthoic acid and 1-hydroxy-2-naphthoic acid showed that the degradation rate of the former to naphthalene-1,2-diol was much faster than that of the latter. The two upper metabolic pathways of phenanthrene are converged into naphthalene-1,2-diol that is further metabolized to 2-carboxycinnamic acid and 2-hydroxybenzalpyruvic acid by ortho- and meta-cleavages, respectively. Transformation of naphthalene-1,2-diol to 2-carboxycinnamic acid by this strain represents the first observation of ortho-cleavage of two rings-PAH-diols by a Gram-negative species.     

Gene encoding the hydrolase for the product of the meta-cleavage reaction in testosterone degradation by Comamonas testosteroni

In a previous study we isolated the meta-cleavage enzyme gene, tesB, that encodes an enzyme that carries out a meta-cleavage reaction in the breakdown of testosterone by Comamonas testeroni TA441 (M. Horinouchi et al., Microbiology 147:3367-3375, 2001). Here we report the isolation of a gene, tesD, that encodes a hydrolase which acts on the product of the meta-cleavage reaction. We isolated tesD by using a Tn5 mutant of TA441 that showed limited growth on testosterone. TesD exhibited ca. 40% identity in amino acid sequence with BphDs, known hydrolases of biphenyl degradation in Pseudomonas spp. The TesD-disrupted mutant showed limited growth on testosterone, and the culture shows an intense yellow color. High-pressure liquid chromatography analysis of the culture of TesD-disrupted mutant incubated with testosterone detected five major intermediate compounds, one of which, showing yellow color under neutral conditions, was considered to be the product of the meta-cleavage reaction. The methylation product was analyzed and identified as methyl-4,5-9,10-diseco-3-methoxy-5,9,17-trioxoandrosta-1(10),2-dien-4-oate, indicating that the substrate of TesD in testosterone degradation is 4,5-9,10-diseco-3-hydroxy-5,9,17-trioxoandrosta-1(10),2-dien-4-oic acid. 4,5-9,10-Diseco-3-hydroxy-5,9,17-trioxoandrosta-1(10),2-dien-4-oic acid was transformed by Escherichia coli-expressed TesD. Downstream of tesD, we identified tesE, F, and G, which encode for enzymes that degrade one of the products of 4,5-9,10-diseco-3-hydroxy-5,9,17-trioxoandrosta-1(10),2-dien-4-oic acid converted by TesD.     

Reduction of azo dyes by redox mediators originating in the naphthalenesulfonic acid degradation pathway of Sphingomonas sp. strain BN6.

The anaerobic reduction of azo dyes by Sphingomonas sp. strain BN6 was analyzed. Aerobic conversion of 2-naphthalenesulfonate (2NS) by cells of strain BN6 stimulated the subsequent anaerobic reduction of the sulfonated azo dye amaranth at least 10-fold. In contrast, in crude extracts, the azo reductase activity was not stimulated. A mutant of strain BN6 which was not able to metabolize 2NS showed increased amaranth reduction rates only when the cells were resuspended in the culture supernatant of 2NS-grown BN6 wild-type cells. The same increase could be observed with different bacterial strains. This suggested the presence of an extracellular factor which was formed during the degradation of 2NS by strain BN6. The addition of 1,2-dihydroxynaphthalene, the first intermediate of the degradation pathway of 2NS, or its decomposition products to cell suspensions of the mutant of strain BN6 (2NS-) increased the activity of amaranth reduction. The presence of bacterial cells was needed to maintain the reduction process. Thus, the decomposition products of 1,2-dihydroxynaphthalene are suggested to act as redox mediators which are able to anaerobically shuttle reduction equivalents from the cells to the extracellular azo dye.     

Degradation characteristics and metabolic pathway of 17β-estradiol (E2) by <Emphasis Type="Italic">Rhodococcus sp. DS201</Emphasis>

In this study an E2-degrading bacterium was isolated from the activated sludge of a municipal treatment plant that treats the waste from a contraceptive medicine-processing factory in Beijing, China. Using the observed morphological and physiological features of the bacterium and 16S rRNA sequence analysis, this bacterial strain was identified as Rhodococcus sp. DS201. Using single-factor experiments and orthogonal tests, it was demonstrated that, when strain DS210 bacteria were inoculated into MM medium at an initial concentration of 1 mg/L with an initial pH of 7 and an inoculum amount of 1%, complete degradation of E2 by this strain was achieved within 3 days at 30oC. After strain DS201 had degraded the E2, several E2 metabolites were detected in the culture extracts using high-performance liquid chromatography (HPLC); they were then further identified using HPLC with tandem mass spectrometry (LC-MS/MS). Mass spectrum analysis of the E2 degradation identified the following products: pent-4-enoic acid; 2-ethyl-3-hydroxy-6-methylcyclohexane-1-carboxylic acid; 3-(7a-methyl-1,5-dioxooctahydro-1H-inden-4-yl) propanoic acid; and 5-hydroxy-4-(3-hydroxypropyl)-7a-methyloctahydro-1H-inden-1-one. These products have not previously been reported as parts of a mechanism for microbial E2 degradation and were suspected to be new metabolite products. Therefore, the E2 degradation pathway by strain DS201 is proposed herein.     

Effect of inducers on the decolorization and biodegradation of textile azo dye Navy blue 2GL by Bacillus sp. VUS

Bacillus sp. VUS decolorized azo dye Navy blue 2GL in 48 h at static anoxic condition in yeast extract medium, whereas it took only 18 h for the decolorization in presence of CaCl₂. Different inducers played role in the decolorization of Navy blue 2GL. CaCl₂ found to be the most effective inducer among all inducers tested. The activity of enzymes like lignin peroxidase, laccase and reductases viz. NADH-DCIP, azo and riboflavin induced during decolorization represents their role in the biodegradation. Extracellular LiP and intracellular laccase activity induced with CaCl₂. Yeast extract was best medium for faster decolorization than other media. UV–vis spectrophotometer analysis and visual examinations showed decolorization of dye. High performance liquid chromatography, Fourier transforms infrared spectroscopy showed degradation of dye. Gas Chromatography-Mass Spectroscopy revealed formation of 4-Amino-3-(2-bromo-4, 6-dinitro-phenylazo)-phenol and acetic acid 2-(-acetoxy-ethylamino)-ethyl ester as final products. Bacillus sp. VUS also decolorized synthetic effluent. Phytotoxicity study showed detoxification of Navy blue 2GL.     

Lignin degradation byPhanerochaete chrysosporium: Metabolism of a phenolic phenylcoumaran substructure model compound

The degradation of a lignin substructure model compound, 5-formyl-3-hydroxymethyl-2-(4-hydroxy-3,5-dimethoxyphenyl)-7-methoxycoumaran (I), in ligninolytic culture of a white-rot wood decay fungus,Phanerochaete chrysosporium, was investigated. It was found that I was hydroxylated or dehydrogenated in its coumaran ring to give 2-(5-formyl-2-hydroxy-3-methoxyphenyl)-3-hydroxypropiosyringone (II) and two coumarones, 5-formyl-3-hydroxymethyl-2-(4-hydroxy-3,5-dimethyoxyphenyl)-7-methoxycoumarone (V) and 3,5-diformyl-2-(4-hydroxy-3,5-dimethoxyphenyl)-7-methoxycoumarone (VI), II was further converted to 2,6-dimethoxy-p-benzoquinone (IV), syringic acid (III), and 5-carboxyvanillic acid (VIII). These metabolic products were identified by mass spectrometric comparison with the authentic compounds. A proposed pathway for the degradation of I is presented on the basis of these metabolic products. The degradation could be catalyzed mainly by phenol-oxidizing enzymes.Non-Standard Abbreviations TLC thin layer chromatography     

Degradation of sulfonated azo dyes by the purified lignin peroxidase from <Emphasis Type="Italic">Brevibacillus laterosporus</Emphasis> MTCC 2298

Lignin peroxidase (EC 1.11.1.14) was purified from the Brevibacillus laterosporus MTCC 2298 by ion exchange chromatography. The K_m value of the purified lignin peroxidase (using n-propanol as substrate) was 1.6 mM. The MW of purified enzyme determined with the help of MW-standard markers was approximately 205 kDa. Purity of the enzyme was confirmed by native polyacrylamide gel electrophoresis (PAGE) and the activity staining using a substrate L-DOPA. Sulfonated azo dyes such as Methyl orange and Blue-2B were degraded by the purified lignin peroxidase. Degradation of the dyes was confirmed by HPLC, GC-MS, and FTIR spectroscopy. The mainly elected products of Methyl orange were 4-substituted hexanoic acid (m/z = 207), 4-cyclohexenone lactone cation (m/z = 191), and 4-isopropanal-2, 5-cyclohexa-dienone (m/z = 149) and for Blue-2B were 4-(2-hexenoic acid)-2, 5-cyclohexa-diene-one (m/z = 207; M − 1 = 206) and dehydro-acetic acid derivative (m/z = 223).     

Gene Encoding the Hydrolase for the Product of the meta-Cleavage Reaction in Testosterone Degradation by Comamonas testosteroni

In a previous study we isolated the meta-cleavage enzyme gene, tesB, that encodes an enzyme that carries out a meta-cleavage reaction in the breakdown of testosterone by Comamonas testeroni TA441 (M. Horinouchi et al., Microbiology 147:3367-3375, 2001). Here we report the isolation of a gene, tesD, that encodes a hydrolase which acts on the product of the meta-cleavage reaction. We isolated tesD by using a Tn5 mutant of TA441 that showed limited growth on testosterone. TesD exhibited ca. 40% identity in amino acid sequence with BphDs, known hydrolases of biphenyl degradation in Pseudomonas spp. The TesD-disrupted mutant showed limited growth on testosterone, and the culture shows an intense yellow color. High-pressure liquid chromatography analysis of the culture of TesD-disrupted mutant incubated with testosterone detected five major intermediate compounds, one of which, showing yellow color under neutral conditions, was considered to be the product of the meta-cleavage reaction. The methylation product was analyzed and identified as methyl-4,5-9,10-diseco-3-methoxy-5,9,17-trioxoandrosta-1(10),2-dien-4-oate, indicating that the substrate of TesD in testosterone degradation is 4,5-9,10-diseco-3-hydroxy-5,9,17-trioxoandrosta-1(10),2-dien-4-oic acid. 4,5-9,10-Diseco-3-hydroxy-5,9,17-trioxoandrosta-1(10),2-dien-4-oic acid was transformed by Escherichia coli-expressed TesD. Downstream of tesD, we identified tesE, F, and G, which encode for enzymes that degrade one of the products of 4,5-9,10-diseco-3-hydroxy-5,9,17-trioxoandrosta-1(10),2-dien-4-oic acid converted by TesD.     

A potent peroxidase from solid cell culture of Ocimum basilicum with high sensitivity for blood glucose determination

Extensive applications of peroxidase (POX) have raised the global market demand at a considerable rate during the forecast period of 2020–2025. Nonetheless, the large-scale POX preparation still relies on the extraction from agricultural products, while there is an accumulative driving force toward employing biotechnological processes with agricultural hassle free identity. Consequently, a novel heme peroxidase was purified to homogeneity (MW of 40 kD) from the callus culture of basil in darkness on Murashige-Skoog medium supplemented by 2,4-dichlorophenoxyacetic acid (10^–6 M) and kinetin (10^–5 M). The highest activity of the purified peroxidase (ObPOX) was observed in Tris-base buffer at pH 7.5 and 80 °C. ObPOX showed high stability over pH(s) 5 to 7.5 and temperatures of 15 to 60 °C. ObPOX specific activity was 1245.142 AU mg^?1 in the presence of phenol, 4 times higher than that of HRP. ObPOX showed moderate affinity for guaiacol (K_m?=?21.5 mM), but obtained an exceptionally high specificity constant (k_cat/K_m?=?66,743.7 s^?1 M^?1) for GASA (4-[(4-Hydroxy-3-methoxyphenyl) azo]-benzenesulfonic acid), the introduced substrate for determination of blood sugar. Applying ObPOX instead of HRP in glucose measurements of the real samples improved the regression constant of the correlation diagram between the tests and the lab results from 0.958 to 0.981. Physicochemical properties of ObPOX as well as the growth rate of basil callus (5.04 g L^?1 per day) and the yield of ObPOX production (35 mg per 100 g dry biomass per subculture) designates O. basilicum cell culture for large-scale production of a robust peroxidase.

     

Oxidation of phenolic and non-phenolic substrates by the lignin peroxidase of Streptomyces viridosporus T7A

Summary Numerous single-ring, aromatic, phenolic and non-phenolic compounds were tested as substrates of Streptomyces viridosporus T7A extracellular lignin peroxidase. Oxidations were monitored by spectroscopy, with and without 4-aminoantipyrine (4-AAP) as a color-forming reagent. The oxidation of phenols containing one or no carbon groups in the para position resulted in coupling with 4-AAP to form a red color. Thin layer chromatography and mass spectroscopy showed that the oxidation of vanillic acid (4-hydroxy-3-methoxybenzoic acid) and syringic acid (4-hydroxy-3,5-dimethoxybenzoic acid) resulted in a direct coupling between 4-AAP and the phenol ring to form a quinone structure. In the reaction with vanillyl acetone (4-(4-hydroxy-3-methoxyphenyl)-3-buten-2-one) and 4-AAP, 4-AAP coupled to Á-carbon of vanillyl acetone. As shown by UV-visible spectroscopy, S. viridosporus T7A peroxidase oxidized phenolic compounds, but was unable to oxidize non-phenolic ones.Paper no. 91 517 of the Idaho Agricultural Experiment Station Correspondence to: D. L. Crawford     

Influence of PAHs on ligninolytic enzymes of the fungus <Emphasis Type="Italic">Pleurotus ostreatus</Emphasis> D1

Polycyclic aromatic hydrocarbons (PAHs), their derivatives, and their degradation products were assayed for the ability to enhance activities of ligninolytic enzymes (laccase and versatile peroxidase) of the fungus Pleurotus ostreatus D1. The activities of both laccase and versatile peroxidase were induced by the PAHs, their derivatives, and their degradation products. Laccase was produced mostly in the first 7–10 days, whereas the production of versatile peroxidase began after 5–7 days of cultivation. Non-denaturing PAGE showed the presence of additional forms of laccase and versatile peroxidase in the presence of the xenobiotics in the cultivation medium. The difference in the production time for these enzymes may reflect that laccases are involved in the first stages of PAHs degradation and that versatile peroxidase can be necessary for oxidation of some degradation products. This is the first report on versatile peroxidase induction by PAHs and their derivatives.     

Aromatic ring cleavage of a β-biphenyl ether dimer catalyzed by lignin peroxidase of phanerochaete chrysosporium

Under aerobic conditions homogeneous lignin peroxidase catalyzed the oxidation of 1-(4'-methoxyphenyl)-2-(2″,5′-dimethoxy-4″-phenylphenoxy)-1,3-dihydroxypropane (I) to yield four products: 1-(4'-methoxy-phenyl)-1,2,3-trihydroxypropane (X), 4-[-hydroxy--(4'-methoxyphenyl)-methyl]-1,3-dioxolane-2-one (V), 4-(4'-methoxyphenyl)-5-hydroxymethyl-1,3-dioxolane-2-one (VI) and 5-hydroxy-5-carbomethoxy-4-phenyl-oxol-3-en-2-one (VIII). V, VI and VIII are all products of ring opening reactions. When the reaction was conducted under anaerobic conditions, the substrate was oxidized but no ring-cleaved products were detected. During the oxidation of I, 4 atoms of ¹⁸O from ¹⁸O₂ were incorporated into the lactol product VIII.     

Phenyl propenoic side chain degradation of ferulic acid by Pycnoporus cinnabarinus - elucidation of metabolic pathways using [5-2H]-ferulic acid

The white-rot fungus Pycnoporous cinnabarinus (DMS-1184) was submerged cultured for 22 days under controlled conditions in a bioreactor. After 6, 9, and 15 days of culture the growth medium was supplemented with [5-2H]-labelled ferulic acid (I). The major phenolic compounds identified labelled were four lignans, the methyl esters of ferulic (I) and vanillic acid (VIII), (E)-coniferyl aldehyde (II), (E)-coniferyl alcohol (III), vanillic acid (VIII), vanillin (IX) and vanillyl alcohol (X). The detection of considerable amounts of labelled 4-hydroxy-3-methoxyacetophenone (VII) in the late growth phase suggested the increasing formation and decarboxylation of free 4-hydroxy-3-methoxybenzoylacetic acid (VI) and, thus, a beta-oxidation-like degradation of ferulic acid (I) or its methyl ester to vanillic acid (VIII). 4-Hydroxy-3-methoxybenzoylacetic acid methyl ester (VI) and 3-hydroxy-(4-hydroxy-3-methoxyphenyl)-propanoic acid methyl ester (V) were synthesised and then identified as metabolites in the culture medium. The fungal degradation of the phenyl propenoic side chain of ferulic acid (I), a principal key step of lignin decomposition, appeared to proceed analogous to fatty acids.     

Sustainable and practical degradation of intact chicken feathers by cultivating a newly isolated thermophilic <Emphasis Type="Italic">Meiothermus ruber</Emphasis> H328

The sustainable and practical degradation of intact chicken feathers by a newly isolated thermophilic bacterium Meiothermus ruber H328 was presented with extensive data. Aerobic cultivation with moderately thermophilic strain H328 at 55°C for 6 days led to the apparently complete decay of the truly intact feathers and provided 1.89 mmol free amino acids and 7.32 mmol acid-hydrolyzed amino acids from 50 ml of culture containing 3% (w/v) intact chicken feathers. The amino acid components in the soluble fraction of the culture conspicuously agreed with those calculated from the intact feathers. This demonstrated that more than 55% of total keratin proteins were solubilized from the intact chicken feathers into the culture in the forms of free amino acid and/or soluble oligopeptide, and most of them are directly derived from the intact feathers by proteolytic digestion. Feather degradation by strain H328 surpasses that by any other microorganisms with regard to degradation efficiency, absence of requirement for pretreatment of the feathers, and product fidelity in the amino acid component. Furthermore, the culture containing the degradative products from the intact feathers was subjected to matrix-assisted laser desorption ionization mass spectrometry-time-of-flight analysis, and it was revealed that the molecular masses of the solubilized products, oligopeptides, were less than 1,000. This result allows us to investigate the bioactivities of oligopeptides derived from the degradation of chicken feathers by cultivation with strain H328 as well as the production of amino acids for feedstuffs.