Michael A. Pickard

Industrial Dye Decolorization by Laccases from Ligninolytic Fungi

Abstract. White-rot fungi were studied for the decolorization of 23 industrial dyes. Laccase, manganese peroxidase, lignin peroxidase, and aryl alcohol oxidase activities were determined in crude extracts from solid-state cultures of 16 different fungal strains grown on whole oats. All Pleurotus ostreatus strains exhibited high laccase and manganese peroxidase activity, but highest laccase volumetric activity was found in Trametes hispida. Solid-state culture on whole oats showed higher laccase and manganese peroxidase activities compared with growth in a complex liquid medium. Only laccase activity correlated with the decolorization activity of the crude extracts. Two laccase isoenzymes from Trametes hispida were purified, and their decolorization activity was characterized.

Uptake and Active Efflux of Polycyclic Aromatic Hydrocarbons by Pseudomonas fluorescens LP6a

ABSTRACT The mechanism of transport of polycyclic aromatic hydrocarbons (PAHs) by Pseudomonas fluorescens LP6a, a PAH-degrading bacterium, was studied by inhibiting membrane transport and measuring the resulting change in cellular uptake. Three cultures were used: wild-type LP6a which carried a plasmid for PAH degradation, a transposon mutant lacking the first enzyme in the pathway for PAH degradation, and a cured strain without the plasmid. Washed cells were mixed with aqueous solutions of radiolabelled PAH; then the cells were removed by centrifugation, and the concentrations of PAH in the supernatant and the cell pellet were measured. The change in the pellet and supernatant concentrations after inhibitors of membrane transport (azide, cyanide, or carbonyl cyanide m-chlorophenyl hydrazone) were added indicated the role of active transport. The data were consistent with the presence of two conflicting transport mechanisms: uptake by passive diffusion and an energy-driven efflux system to transport PAHs out of the cell. The efflux mechanism was chromosomally encoded. Under the test conditions used, neither uptake nor efflux of phenanthrene by P. fluorescens LP6a was saturated. The efflux mechanism showed selectivity since phenanthrene, anthracene, and fluoranthene were transported out of the cell but naphthalene was not.

Purification, Characterization, and Chemical Modification of Manganese Peroxidase from Bjerkandera adusta UAMH 8258

Ten strains of Bjerkandera adusta from the University of Alberta Microfungus Collection and Herbarium (UAMH) were compared for manganese peroxidase production. The enzyme from B. adusta UAMH 8258 was chosen for further study. After purification the enzyme showed a molecular weight of 43 kDa on 15% SDS-PAGE, 36.6 kDa on matrix-assisted laser desorption ionization-time of flight mass spectrometry, and an isoelectric point of 3.55. The N-terminal amino acid sequence was determined to be VAXPDGVNTATNAAXXALFA, and the amino acid composition showed no tyrosine residues in the enzyme. Manganese peroxidase exhibited both Mn(II)-dependent (optimum pH 5) and Mn(II)-independent activity (optimum pH 3). The purified enzyme was chemically modified with cyanuric chloride-activated methoxypolyethylene glycol to enhance its surface hydrophobicity. The modified and native enzymes showed similar catalytic properties in the oxidation of Mn(II) and other substrates such as 2,6-dimethoxylphenol, veratryl alcohol, guaiacol, and 2,2′-azino-bis(3-ethylbenzthiazoline-6-sulfonate). However, the modified enzyme showed greater resistance to denaturation by hydrogen peroxide and stability to organic solvents such as acetonitrile, N,N-dimethylformamide, tetrahydrofuran, methanol, and ethanol. The PEG-modified enzyme also showed greater stability to higher temperatures and lower pH than the native enzyme. Thus, chemical modification of manganese peroxidase from B. adusta increases its potential usefulness for applied studies.

Chloroperoxidase, a peroxidase with potential

SummaryChloroperoxidase is an extracellular heme glycoprotein produced by the imperfect fungusCaldariomyces fumago. The enzyme can catalyse chlorination reactions as well as act as a catalase or a peroxidase. As a peroxidase, it has a wide substrate specificity and we are interested in some applied aspects of this activity, requiring the production and purification of moderate quantities of the enzyme. High levels of chloroperoxidase are produced in a fructose synthetic medium, and highest enzyme production occurs in a low-shear environment. fungal pellets produce enzyme continuously at low medium replacement rates and at up to 0.6 g enzyme per 1: chloroperoxidase is essentially the only extracellular enzyme produced. Enzyme purification is uncomplicated and gives good yields of high purity. Pure enzyme is stable for weeks at room temperature and under pH control. Chloroperoxidase can be ionically bound to aminopropyl glass, then covalently immobilized by glutaraldehyde crosslinking. Immobilized preparations have been washed and re-used five times, and are most stable at pH 5.5-6. Like many peroxidases, chloroperoxidase will oxidize phenols and phenolics, often causing a precipitate, and can totally remove phenols at low aqueous concentrations. Chloroperoxidase incubation with the petroporphyrin component of crude oil asphaltene (fraction 5) causes a reduction or removal of the Soret band (410 nm) and the α-peak (573 nm). This petroporphyrin fraction is enriched with vanadium which poisons the chemical catalyst used in cracking crude oil.

Biological remediation of anthracene-contaminated soil in rotating bioreactors

Soil impregnated with anthracene was subjected to bacterial treatment as a model for remediation of soils contaminated with polycyclic aromatic hydrocarbons (PAHs). Roller bottles were used to simulate the mixing of solids in rotating drums. The soil was prepared as a 60 weight % slurry in salts medium, and inoculated with a mixed culture, selected for the ability to mineralize anthracene as its sole carbon source. The degradation of anthracene followed zero-order kinetics when it was well dispersed on the soil particles, consistent with a rate limitation by dissolution of solid hydrocarbon. Maximum degradation rates of 300 μg/g per day were achieved in repeated batch operation, using a 10% volume of soil slurry as the inoculum for the succeeding batch. Anthracene degradation activity was maintained through 18 such transfers on a 3- to 4-day cycle. The culture produced soluble compounds that enhanced the solubility of anthracene in aqueous solution. Soil components did not have a significant effect on growth or degradation. Degradation of anthracene ceased when the concentration in soil dropped to approx. 30 μg/g, from an initial value of 600 μg/g.

On the mechanism of chlorination by chloroperoxidase.

Spectral-scan results obtained on the millisecond time scale are reported for reactions of chloroperoxidase with peracetic acid and chloride ion in both the presence and the absence of monochlorodimedone. A multimixing experiment is performed in which stoichiometric amounts of chloroperoxidase and peracetic acid are premixed for 0.7 s before the resultant compound I is reacted with chloride ion. The combined results show that the only detectable enzyme intermediate species is compound I (except in very late stages of the reaction), that the disappearance of compound I is accelerated by the presence of chloride ion, and that it is further accelerated if both chloride and monochlorodimedone are present. It is concluded that compound I is an obligate intermediate species in the reaction. Experiments are performed on the reaction of monochlorodimedone with hypochlorous acid in both the presence and the absence of added chloride ion, but in the absence of chloroperoxidase. The presence of chloride ion greatly accelerates the reaction rate apparently by setting off a chlorine chain reaction. This reaction would be important in the enzyme-catalyzed reaction if hypochlorous acid were liberated into the solution. A careful analysis of steady-state kinetic results shows that in the chlorination of monochlorodimedone at least, liberation of free hypochlorous acid is not important in the enzyme-catalyzed pathway. Rather the reaction proceeds from compound I to formation of iron(III)-OCl by chloride ion addition to the ferryl oxygen atom. This obligate intermediate species then chlorinates the substrate. It is well described as enzyme-activated hypochlorous acid, in which replacement of the proton in HOCl by the heme iron ion produces a Cl+ species of great potency. Thus the enzyme controls chlorination of monochlorodimedone rather than unleashing an uncontrolled chain reaction in which it would be rapidly destroyed.

Dibenzyl Sulfide Metabolism by White Rot Fungi

ABSTRACT Microbial metabolism of organosulfur compounds is of interest in the petroleum industry for in-field viscosity reduction and desulfurization. Here, dibenzyl sulfide (DBS) metabolism in white rot fungi was studied. Trametes trogii UAMH 8156, Trametes hirsuta UAMH 8165, Phanerochaete chrysosporium ATCC 24725, Trametes versicolor IFO 30340 (formerly Coriolus sp.), and Tyromyces palustris IFO 30339 all oxidized DBS to dibenzyl sulfoxide prior to oxidation to dibenzyl sulfone. The cytochrome P-450 inhibitor 1-aminobenzotriazole eliminated dibenzyl sulfoxide oxidation. Laccase activity (0.15 U/ml) was detected in the Trametes cultures, and concentrated culture supernatant and pure laccase catalyzed DBS oxidation to dibenzyl sulfoxide more efficiently in the presence of 2,2′-azinobis(3-ethylbenzthiazoline-6-sulfonate) (ABTS) than in its absence. These data suggest that the first oxidation step is catalyzed by extracellular enzymes but that subsequent metabolism is cytochrome P-450 mediated.

Fungal Enzymes for Environmental Purposes, a Molecular Biology Challenge

In their capacity to transform xenobiotics and polluting compounds, fungal peroxidases and their use in the environmental field have a recognized and important potential. However, both fundamental and practical issues, such as enzyme stability and availability, have delayed the development of industrial applications. Three main protein engineering challenges have been identified: (1) Enhancement of operational stability, specifically hydrogen peroxide stability in the case of fungal peroxidases. (2) Increase of the enzyme redox potential in order to widen the substrate range. (3) Development of heterologous expression and industrial production. The bottlenecks, advances and strategies that have been proven successful are discussed.

Monitoring the biological treatment of anthracene-contaminated soil in a rotating-drum bioreactor

A 2-kg-capacity rotating-drum reactor was used for biological conversion of nearly insoluble organic contaminants in soil. The rotating motion allowed effective operation at a solids content of over 60% by weight. A mixed bacterial culture was used to degrade anthracene that had been impregnated into a representative high-clay soil. The activity of the culture was sustained over a period of months in repeated batch operation, in which fresh soil was inoculated with 20% spent slurry from the previous run. Maximum degradation rates of 100–150 mg anthracene (kg soil)−1 day−1 were achieved throughout the experiments. Evolution of carbon dioxide from the bioreactor showed that degradation and mineralization of anthracene occurred simultaneously, and that 55% of the anthracene was mineralized. When the culture was switched from anthracene as sole carbon source to a mixture of three polynuclear aromatic hydrocarbons, the culture was able to degrade each of these in the sequence: anthracene, phenanthrene and finally pyrene.

Surfactant inhibition of bacterial growth on solid anthracene

Surfactants have been proposed as a promising method to enhance bioremediation of hydrophobic compounds in contaminated soils. However, the results of effects of surfactants on bioremediation are not consistent. This study showed that Triton X-100 at low concentration (0.024 mM or 0.09 CMC) inhibited the rate of growth of either a Mycobacterium sp. or a Pseudomonas sp. on solid anthracene as sole carbon source. Recovery of microbial growth rate could be achieved by dilution of surfactants, while addition of more surfactant gave an immediate decrease in growth rate. No inhibition of growth by Triton X-100 was observed with growth on glucose. The surfactant sorbed onto the surfaces of both the cells and the anthracene particles, which could inhibit uptake of anthracene. The results were consistent with the hypothesis that inhibition of microbial adhesion of cells to anthracene was responsible for the inhibition of growth by Triton X-100.