Dephenolization of industrial wastewaters catalyzed by polyphenol oxidase

A new enzymatic method for the removal of phenols from industrial aqueous effluents has been developed. The method uses the enzyme polyphenol oxidase which oxidizes phenols to the corresponding o-quinones; the latter then undergo a nonenzymatic polymerization to form water-insoluble aggregates. Therefore, the enzyme in effect precipitates phenols from water. Polyphenol oxidase has been found to nearly completely dephenolize solutions of phenol in the concentration range from 0.01 to 1.0 g/L. The enzymatic treatment is effective over a wide range of pH and temperature; a crude preparation of polyphenol oxidase (mushroom extract) is as effective as a purified, commercially obtained version. In addition to phenol itself, polyphenol oxidase is capable of precipitating from water a number of substituted phenols (cresols, chlorophenols, naphthol, etc.). Also, even pollutants which are unreactive towards polyphenol oxidase can be enzymatically coprecipitated with phenol. The polyphenol oxidase treatment has been successfully used to dephenolize two different real industrial waste-water samples, from a plant producing triarylphosphates and from a coke plant. The advantage of the polyphenol oxidase dephenolization over the peroxidase-catalyzed one previously elaborated by the authors is that the former enzyme uses molecular oxygen instead of costly hydrogen peroxide (used by peroxidase) as an oxidant.     

19F-NMR study on the interaction of fluorobenzoate with porcine kidney D-amino acid oxidase

The interactions of competitive inhibitors, o-, m-, and p-fluorobenzoates, with porcine kidney D-amino acid oxidase (DAO) were studied by 19F-NMR spectroscopy. The 19F-signals of DAO-bound fluorobenzoates were observed as considerably broadened peaks. The chemical shifts, which are referenced to 20 mM NaF in 50 mM sodium phosphate, pH 7.0, were 6.0, 8.2, and 11.9 ppm for free o-, m-, and p-fluorobenzoates, respectively, while those of o-, m-, and p-fluorobenzoates bound to DAO were 12.5, 5.4, and 13.1 ppm, respectively. The 19F-signals of bound o- and p-fluorobenzoates were downfield-shifted relative to those of the free species, whereas the 19F-resonance of m-fluorobenzoate was up-field shifted from that of the free ligand. The magnitude of the chemical shift difference between the free and bound forms decreases in the order of o-, m-, and p-fluorobenzoates. The remarkably large downfield shift of the o-fluorobenzoate when bound to DAO was attributed to the close proximity of the ortho-fluorine atom to the flavin nucleus in comparison with meta- or para-fluorine. The pH-dependences of the 19F-resonances of o-, m-, and p-fluorobenzoates were observed and the pKa values of 3.33, 3.80, and 4.05 were obtained for the carboxyl groups of o-, m-, and p-fluorobenzoates, respectively. It was observed that the 19F-resonances of o- and p-fluorobenzoates are highly sensitive to the ionic state of the carboxyl group, while that of m-fluorobenzoate was moderately sensitive.     

Degradation of high concentrations of cresols by Pseudomonas sp. CP4

Pseudomonas sp. CP₄, a potent phenol-degrading laboratory isolate could mineralize all three isomers of cresol. This strain readily utilized up to 1.4, 1.1 and 2.2 g/l of o- m- and p-cresol, respectively as the sole sources of carbon and energy. These are the highest concentrations of cresols reported to be degraded by a bacterial strain. The rates of degradation of the three isomers were in the order: o- > p- > m-cresol. All the isomers of cresol were catabolized through a meta-cleavage pathway. Fairly high catechol 2,3-dioxygenase (C230) activity against catechol was observed in the cell-free extracts of the culture grown on these compounds and were in the order: m- > o- > p-cresol.     

Effects of some alkyl phenols on methanogenic degradation of phenol.

The effects of six phenolic compounds (o-, m-, and p-cresol and 2-, 3-, and 4-ethylphenol) on the anaerobic biodegradation of phenol was examined in batch methanogenic cultures. Results showed that ethylphenols were more inhibitory of phenol degradation than were cresols. The inhibitory effects of the three isomers of cresol and ethylphenol did not vary with the isomer but rather with the substituted functional group.     

Effects of some alkyl phenols on methanogenic degradation of phenol

The effects of six phenolic compounds (o-, m-, and p-cresol and 2-, 3-, and 4-ethylphenol) on the anaerobic biodegradation of phenol was examined in batch methanogenic cultures. Results showed that ethylphenols were more inhibitory of phenol degradation than were cresols. The inhibitory effects of the three isomers of cresol and ethylphenol did not vary with the isomer but rather with the substituted functional group.     

The effect of concentration of phenols on their batch methanogenesis

The biodegradability of phenol and six other phenolic compounds (o-, m-, and p-cresol, 2-, 3-, and 4-ethylphenol) was examined in batch methanogenic cultures. The effect of concentration of these alkyl phenols on the anaerobic biodegradation of phenol was also evaluated. The inoculum used in this study was cultivated in a continuous flow laboratory fermenter with phenol as the primary substrate. Phenol, at initial concentrations as high to 1400 mg/L was completely degraded to methane and carbondioxide after 350 hours incubation. Complete degradation of m- and p-cresol was also observed while the ethylphenols and o-cresol were not significantly degraded.At initial concentrations exceeding 600 mg/L, phenol inhibited the phenol-degrading microorganisms but not the methanogens. At about 600 mg/L, cresols reduced the rate of phenol degradation to 50% of that observed in a control culture containing only 200 mg/L phenol. Ethylphenols were more inhibitory than cresols. Phenol degrading microorganisms were more susceptible to inhibition by cresols and ethylphenols than were the methanogens. The inhibitory effects of the three isomers of cresol and ethylphenol did not vary with the isomer but rather with the substituted functional group.     

Horseradish peroxidase-catalyzed oxidative coupling of 3-methyl 2-benzothiazolinone hydrazone and methoxyphenols

The reaction between o-, m-, and p-methoxyphenols and 3-methyl-2-benzothiazolinone hydrazone (MBTH) is studied in the presence of horseradish peroxidase (HRP) and H₂O₂ as oxidative agent. The findings indicate that enzyme (H₂O₂ oxidoreductase; EC 1.11.1.7) catalyzes an oxidative coupling reaction between MBTH and phenols which produces azo dye compounds. On the basis of kinetic parameters and optimum pH values, a mechanism in which both MBTH and phenols seem to be activated by the HRP for achieving the oxidative coupling is proposed. Furthermore, in the current study, we have evaluated the possibility that these azo dyes may be useful in the measurement of peroxidase activity. The method is based on the observed increase in the absorbance at 502 nm (8,355 cm^{−1 −1} of extinction molar coefficient) due to the formation of a red azo dye compound resulting from the peroxidase-catalyzed oxidative coupling of MBTH and o-methoxyphenol (guaiacol). Using this assay system, HRP can be determined in picomolar levels by a fixed time method.     

Activation and inactivation of horseradish peroxidase by cobalt ions

The effect of cobalt ions (Co2+) on horseradish peroxidase (HRP) was studied in vitro by enzymatic activity assay, electronic absorption spectra, intrinsic fluorescence spectra and 8-anilo-1-naphthalenesulfonate(ANS)-binding fluorescence spectra. Co2+ at concentrations below 0.1 mM mildly increased the HRP activity, whereas higher concentrations of Co2+ significantly inactivated HRP in a time and concentration-dependent manner. Steady-state kinetic studies show that Co2+ was a noncompetitive inhibitor of o-dianisidine oxidation by HRP. The Ki value dropped as the incubation time increased. Furthermore, Co2+ was found to be an uncompetitive inhibitor of H2O2. These results suggested that Co2+ would slowly bind to the enzyme and progressively induce conformational changes. Spectroscopic analysis showed that even for high Co2+ concentrations, the structure of HRP as a whole only changed slightly; however, there were significant conformational changes near or in the active site of HRP. Based on the above results, we suggest that Co2+ may bind with some amino acids near or in the active site of HRP and the conformational changes of HRP induced by such binding should be the main reason for activation and inactivation effect of Co2+. The potential binding sites of Co2+ were also proposed.     

Degradation of phenol and phenolic compounds by Pseudomonas putida EKII

Summary The phenol-degrading strain Pseudomonas putida EKII was isolated from a soil enrichment culture and utilized phenol up to 10.6 mM (1.0 g·1 ^-1) as the sole source of carbon and energy. Furthermore, cresols, chlorophenols, 3,4-dimethylphenol, and 4-chloro-m-cresol were metabolized as sole substrates by phenol-grown resting cells of strain EKII. Under conditions of cell growth, degradation of these xenobiotics was achieved only in co-metabolism with phenol. Phenol hydroxylase activity was detectable in whole cells but not in cell-free extracts. The specificity of the hydroxylating enzyme was found during transformation of cresols and chlorophenols: ortho- and meta-substituted phenols were degraded via 3-substituted catechols, while degradation of para-substituted phenols proceeded via 4-substituted catechols. In cell-free extracts of phenol-grown cells a high level of catechol 2,3-dioxygenase as well as smaller amounts of 2-hydroxymuconic semialdehyde hydrolyase and catechol 1,2-dioxygenase were detected. The ring-cleaving enzymes were characterized after partial purification by DEAE-cellulose chromatography.     

Toxicity and kinetic parameters of the aerobic biodegradation of the phenol and alkylphenols by a mixed culture

A mixed culture aerobically metabolized phenol, cresol isomers (o-,m-,p-), 2-ethylphenol and xylenol isomers (2,5-DMP and 3,4-DMP) as the sole carbon and energy source. This culture had a high tolerance towards phenol with values of maximum degradation rate (V_\max) of 47 M phenol mg^–1 protein h^–1 and inhibition substrate constant (Ki) of 10 mM. These kinetic parameters were considerably diminished and the toxicity increased with the alkylphenols. For example with 2,5-xylenol, V_\max and Ki values of 0.8 M 2,5-xylenol mg^–1 protein h^–1 and 1.3 mM, respectively, were obtained. The cresols were 5-fold more toxic than phenol, whereas 2-ethylphenol and 3,4-xylenol were 11-fold more toxic, and 2,5-xylenol was 34-fold more toxic than phenol.     

Response of a chlorophenols degrading mixed culture to changing loads of phenol,chlorophenol and cresols

Summary A phenol and solvents degrading mixed culture from soil and sludge supplemented with Pseudomonas sp. strain B13 which harbors genes coding the sequence for chlorocatechol breakdown was acclimated to monochlorophenol degradation. Pyrocatechase activity was used as an indicator for the adaptation status of the culture.In the fully acclimated culture, strain B13 was partially replaced by hybrid strains which had acquired the chlorocatechol degrading sequence. This culture degraded changing loads of phenol, chlorophenols and cresols without accumulation of DOC (dissolved organic carbon). When high cresol concentrations were supplied simultaneously with the chlorophenols, strains were enriched which degrade cresols and 3-methylbenzoate via ortho-cleavage pathway.     

Phenol removal from aqueous solutions by peroxidase extracted from horseradish

Horseradish peroxidase (HRP) is one of the most recently used enzymes in the process of enzymatic phenol removal. It has a catalytic ability over a broad range of pH, temperature and contaminant concentrations. In this study we revealed the possibility of successful use the crude peroxidase obtained from horseradish roots for the phenol removal from aqueous solutions in the presence of the low molecular polyethylene glycol (PEG 300) at room temperature (20°C) and pH 7.2. Reaction was monitored by direct measuring of the absorbance changes in a samples taken at certain time intervals from the reaction mixture. At the first time PEG 300 was shown to be a more stabilizing effect on crude HRP and provided a higher phenol removal in comparison with PEG 3350. Crude HRP used in these study demonstrated a greater resistance on phenol and hydrogen peroxide inactivation that allowed a higher phenol removal. The highest phenol removal was achieved when the concentration of PEG 300, phenol and hydrogen peroxide were 300 mg/L, 2.0 and 2.5 mM, respectively.     

Chlorophenol degradation by Phanerochaete chrysosporium

Degradation of chlorophenols by P. chrysosporium in static cultures has been studied. The influences of mycelium acclimation, co-substrate concentration and nitrogen source on phenol degradation were analyzed. With non-acclimated mycelium the maximal concentrations degraded were 150 ppm of o-chorophenol and 100 ppm of the isomers m- and p-chlorophenol. The substituted ortho-position on the aromatic ring was the preferred attack position. Meta- and para-positions were less reactive and resulted in a slower degradation rate than the ortho position. Nevertheless, with acclimated mycelium, an increase in the ability to degrade chlorophenol and a higher reactivity in meta- and para-positions were observed (degraded chlorophenol increased by up to 70% for the o-isomer and 50% for the m- and p-isomers with respect to non-acclimated mycelium). A decrease in glucose concentration caused a decrease in chlorophenol degradation rate. Twelve days were needed for complete degradation of o-chlorophenol with 10 g/l of glucose and 22 days when glucose concentration was decreased to 2.5 g/l. The reduction of ammonium tartrate caused a greater lag time, but not a decrease in chlorophenol degradation rate. Replacement of ammonium tartrate by ammonium chloride caused a decrease in chlorophenol degradation rate.     

Immobilization of horseradish peroxidase on activated wool

This work is aimed to immobilize partially purified horseradish peroxidase (HRP) on wool activated by multifunctional reactive center, namely cyanuric chloride. The effect of cyanuric chloride concentration, pH and enzyme concentration on immobilization of HRP was studied. FT-IR and SEM analyses were detected for wool, activated wool and immobilized wool-HRP. The wool-HRP, prepared at 2% (w/v) cyanuric chloride and pH 5.0, retained 50% of initial activity after seven reuses. The wool-HRP showed broad optimum pH at 7.0 and 8.0, which was higher than that of the soluble HRP (pH 6.0). The soluble HRP had an optimum temperature of 30 °C, which was shifted to 40 °C for immobilized enzyme. The soluble and wool-HRP were stable up to 30 and 40 °C after incubation for 1 h, respectively. The apparent kinetic constant values (K_ms) of wool-HRP were 10 mM for guiacol and 2.5 mM for H₂O₂, which were higher than that of soluble HRP. The wool-HRP was remarkably more stable against proteolysis mediated by trypsin. The wool-HRP exhibited more resistance to heavy metal induced inhibition. The wool-HRP was more stable to the denaturation induced by urea, Triton X-100, isopropanol, butanol and dioxan. The wool-HRP was found to be the most stable under storage. In conclusion, the wool-HRP could be more suitable for several industrial and environmental purposes.     

Base-exchange reactions of the phospholipids in cardiac membranes

Canine cardiac microsomes were shown to incorporate the nitrogenous bases, serine, ethanolamine, and choline, into their respective phospholipids by the energy-independent, Ca2+-stimulated base-exchange reactions. The optimal Ca2+ concentration was 2.5 mM. Metal ions other than Ca2+ either inhibited or had no effect on the activities. La3+ and Mn2+ were both potent inhibitors. The pH optimum for the reactions at 2.5 mM Ca2+ was approx. 7.8 and depended upon Ca2+ concentration. Apparent Km values at 2.5 mM Ca2+ were 0.06 mM for L-serine, 0.13 mM for ethanolamine and 0.49 mM for choline. The kinetic and metal ion inhibition studies suggest that the choline-exchange reaction is a separate process from the serine and ethanolamine reactions. The ATP-stimulated Ca2+ binding system of the cardiac membranes was not related to the base-exchange reactions; however, the energy-independent Ca2+ binding to the membranes appears to be related to the exchange reactions.     

Comparison of nuclear 5 alpha-reductase activities in the stromal and epithelial fractions of human prostatic tissue

The nuclear conversion of testosterone (T) to dihydrotestosterone (DHT) was compared in the separated stromal and epithelial fractions of hyperplastic (n = 20), malignant (n = 5) and normal (n = 1) prostatic tissues. Standard assay conditions were: 1 microM testosterone, plus 4-6 X 10(5) DPM [3H]T, 1.0 mM NADPH, 2.0 mM EDTA and 0.5-1.0 mg nuclear protein in a total volume of 1.1 ml HEPES buffer, pH 7.4 (stroma) or MES buffer, pH 6.5 (epithelium). The apparent Km values for the stromal enzyme were 0.2, 0.2 and 0.3 microM, respectively, for the enzymes in hyperplastic, malignant and normal tissues. The Vmax values were 26 +/- 4.2, 2.8 +/- 0.6 and 4.1 pmol/mg protein/30 min incubation, respectively, for these same tissues. The apparent Km values for the epithelial enzymes, from the same tissues, were 0.03, 0.07 and 0.08 microM. The Vmax values for the epithelial enzymes were 4.8 +/- 1.2, 0.69 +/- 0.08 and 1.1 pmol/mg protein/30 min incubation. The pH optimum for the stromal enzyme lay between pH 6.5 and 7.5, whereas the pH optimum for the epithelial enzyme lay between 5.5 and 6.5. Enzymatic activity in both fractions revealed a biphasic response to zinc. In the absence of EDTA, microM quantities of zinc enhanced enzymatic activity while mM quantities inhibited this activity. These results would suggest that differences in the conversion of T to DHT help to explain, at least in part, the higher DHT levels seen in hyperplastic tissue and the higher T levels seen in the malignant prostate.     

Deuterium isotope effects on toluene metabolism. Product release as a rate-limiting step in cytochrome P-450 catalysis

Liver microsomes from phenobarbital-induced rats oxidize toluene to a mixture of benzyl alcohol plus o-, m- and p-cresol (ca. 69:31). Stepwise deuteration of the methyl group causes stepwise decreases in the yield of benzyl alcohol relative to cresols (ca. 24:76 for toluene-d3). For benzyl alcohol formation from toluene-d3 DV = 1.92 and D(V/K) = 3.53. Surprisingly, however, stepwise deuteration induces stepwise increases in total oxidation, giving rise to an inverse isotope effect overall (DV = 0.67 for toluene-d3). Throughout the series (i.e. d0, d1, d2, d3) the ratios of cresol isomers remain constant. These results are interpreted in terms of product release for benzyl alcohol being slower than release of cresols (or their epoxide precursors), and slow enough to be partially rate-limiting in turnover. Thus metabolic switching to cresol formation causes a net acceleration of turnover.     

Removal of linear and branched alkylphenols from aqueous solutions with horseradish peroxidase

Alkylphenols were effectively treated with horseradish peroxidase at pH 7.0 and 30 degrees C in the presence of H(2)O(2) and poly(ethylene glycol) irrespective of the relative position or isomeric form of the alkyl chains. Water-insoluble oligomer precipitates were readily filtered out after enzymatic treatment, and transparent and colorless solutions were obtained for all p- and m-alkylphenols used.     

Unusual pattern of nucleoside polyphosphate hydrolysis by the acid phosphatase (optimum pH = 2.5) of Escherichia coli.

An acid phosphatase with an optimum pH of 2.5, was partially extracted by a single wash of whole cells of E. coli by 1 mM EDTA 50 mM Tris buffer pH 7.8. Its enrichment coefficient in this extract was about 100. Ribonucleoside polyphosphates were hydrolyzed by the enzyme at very different rates according both to the nature of the base and the position of the phosphate group. UTP and ppGpp were the most sensitive. The significance of these differences are briefly discussed.     

The enzymatic system of phospholipid deacylation-reacylation in rat liver lysosomal membranes

It has been shown for the first time that lysosomal (tritosomal) membranes of rat liver contain enzymes that are responsible for the deacylation-reacylation of phospholipids; their activity optimum lies at pH 7.0. Deacylation of lysosomal membrane phospholipids is controlled by a cascade of enzymatic reactions involving Ca2(+)-dependent phospholipase A1 which exhibits the maximal activity at 2.5 mM Ca2+ and at neutral values of pH, as well as lysophospholipase. Reacylation of lyso-derivatives of phospholipids is catalyzed by Mg2(+)-activated oleoyl-CoA:lysophosphatidylcholine acyltransferase having an activity optimum at pH 7.2.