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Cometabolic degradation of chlorinated alkenes by alkene monooxygenase in a propylene-grown Xanthobacter strain.

Propylene-grown Xanthobacter cells (strain Py2) degraded several chlorinated alkenes of environmental concern, including trichloroethylene, 1-chloroethylene (vinyl chloride), cis- and trans-1,2-dichloroethylene, 1,3-dichloropropylene, and 2,3-dichloropropylene. 1,1-Dichloroethylene was not degraded efficiently, while tetrachloroethylene was not degraded. The role of alkene monooxygenase in catalyzing chlorinated alkene degradations was established by demonstrating that glucose-grown cells which lack alkene monooxygenase and propylene-grown cells in which alkene monooxygenase was selectively inactivated by propyne were unable to degrade the compounds. C2 and C3 chlorinated alkanes were not oxidized by alkene monooxygenase, but a number of these compounds were inhibitors of propylene and ethylene oxidation, suggesting that they compete for binding to the enzyme. A number of metabolites enhanced the rate of degradation of chlorinated alkenes, including propylene oxide, propionaldehyde, and glucose. Propylene stimulated chlorinated alkene oxidation slightly when present at a low concentration but became inhibitory at higher concentrations. Toxic effects associated with chlorinated alkene oxidations were determined by measuring the propylene oxidation and propylene oxide-dependent O2 uptake rates of cells previously incubated with chlorinated alkenes. Compounds which were substrates for alkene monooxygenase exhibited various levels of toxicity, with 1,1-dichloroethylene and trichloroethylene being the most potent inactivators of propylene oxidation and 1,3- and 2,3-dichloropropylene being the most potent inactivators of propylene oxide-dependent O2 uptake. No toxic effects were seen when cells were incubated with chlorinated alkenes anaerobically, indicating that the product(s) of chlorinated alkene oxidation mediates toxicity.

Alkenes

Photoionization assessment of C3-C5 alkadienes and alkenes in urban air.

Hydrocarbons from samples of traffic-polluted urban air were separated by gas chromatography on an aluminium oxide column and assessed simultaneously by photoionization detection (PID) and flame ionization detection (FID) after effluent splitting. The 10.2 eV photoionization detector selectively detects alkadienes and alkenes but not alkanes and alkynes in the C3-C5 region. The maximum PID/FID response ratio for alkadienes and alkenes is also obtained in this region. The analytical system as a whole is particularly favourable for the C3-C5 alkenes. Analytical data are given for propadiene, 1,3-butadiene, propene, butenes and pentenes.

Air Pollutants

Effect of C6 to C9 alkenals on aflatoxin production in corn, cottonseed, and peanuts.

The effect on aflatoxin production in Aspergillus flavus-inoculated corn, cottonseed, and peanuts in static culture in the presence of gaseous phase C6 to C9 alkenals was investigated. Aflatoxin B1 production was stimulated in corn at the lowest alkenal concentration (1-microliters level) tested. Aflatoxin B1 was completely eliminated at the highest alkenal concentrations (20-microliters level) tested in both treated corn and cottonseed cultures.

Aflatoxins

Epoxide hydrase and glutathione S-transferase activities with selected alkene and adrene oxides in several marine species.

Epoxide hydrase and glutathione (GSH) S-transferase activities were measured in subcellular fractions prepared from liver or hepatopancreas and some extrahepatic organs of a number of marine species common to Maine or Florida. These activities were easily detected in the species studied. In fish, hepatic GSH S-transferase activities were normally higher than hepatic epoxide hydrase activities for the alkene oxide (styrene oxide and octene oxide) and arene oxide (benzo[a]pyrene 4,5-oxide) substrates studied, whereas in crustacea, hepatopancreas epoxide hydrase activities were higher than hepatopancreas GSH S-transferase activities with the same substrates. Extrahepatic organs from fish and crustacea usually had higher GSH S-transferase activities than epoxide hydrase activities with the alkene and arene oxide substrates. GSH S-transferase activity was also found in liver or hepatopancreas of every aquatic species studied and in a number of extrahepatic organs, when 1,2-dichloro-4-nitrobenzene or 1-chloro-2,4-dinitrobenzene served as substrate.

Alkenes

Microbial oxidation of gaseous hydrocarbons: epoxidation of C2 to C4 n-alkenes by methylotrophic bacteria.

Over 20 new cultures of methane-utilizing microbes, including obligate (types I and III) and facultative methylotrophic bacteria were isolated. In addition to their ability to oxidize methane to methanol, resting cell-suspensions of three distinct types of methane-grown bacteria (Methylosinus trichosporium OB3b [type II, obligate]; Methylococcus capsulatus CRL M1 NRRL B-11219 [type I, obligate]; and Methylobacterium organophilum CRL-26 NRRL B-11222 [facultative]) oxidize C2 to C4 n-alkenes to their corresponding 1,2-epoxides. The product 1,2-epoxides are not further metabolized and accumulate extracellularly. Methanol-grown cells do not have either the epoxidation or the hydroxylation activities. Among the substrate gaseous alkenes, propylene is oxidized at the highest rate. Methane inhibits the epoxidation of propylene. The stoichiometry of the consumption of propylene and oxygen and the production of propylene oxide is 1:1:1. The optimal conditions for in vivo epoxidation are described. Results from inhibition studies indicate that the same monooxygenase system catalyzes both the hydroxylation and the epoxidation reactions. Both the hydroxylation and epoxidation activities are located in the cell-free particulate fraction precipitated between 10,000 and 40,000 x g centrifugation.

Alkenes

Purification and properties of the NADH reductase component of alkene monooxygenase from Mycobacterium strain E3.

Alkene monooxygenase, a multicomponent enzyme system which catalyzes the epoxidation of short-chain alkenes, is induced in Mycobacterium strain E3 when it is grown on ethene. We purified the NADH reductase component of this enzyme system to homogeneity. Recovery of the enzyme was 19%, with a purification factor of 920-fold. The enzyme is a monomer with a molecular mass of 56 kDa as determined by gel filtration and sodium dodecyl sulfate-polyacrylamide gel electrophoresis. It is yellow-red with absorption maxima at 384, 410, and 460 nm. Flavin adenine dinucleotide (FAD) was identified as a prosthetic group at a FAD-protein ratio of 1:1. Tween 80 prevented irreversible dissociation of FAD from the enzyme during chromatographic purification steps. Colorimetric analysis revealed 2 mol each of iron and acid-labile sulfide, indicating the presence of a [2Fe-2S] cluster. The presence of this cluster was confirmed by electron paramagnetic resonance spectroscopy (g values at 2.011, 1.921, and 1.876). Anaerobic reduction of the reductase by NADH resulted in formation of a flavin semiquinone.

Alkenes

Alkene monooxygenase from Mycobacterium: a multicomponent enzyme.

A NADH- or NADPH-dependent alkene monooxygenase (AMO) activity has been detected in cell-free extracts of the ethene-utilizing Mycobacterium E3 and Mycobacterium aurum L1. The activity was not linear with protein concentration in the assay suggesting AMO is a multicomponent enzyme. The inhibition pattern of AMO activity was very similar to the inhibition patterns published for the three-component soluble methane monooxygenases. Fractionation of crude extracts revealed that combination of two fractions was required to restore alkene monooxygenase activity. The first fraction was inhibited by acetylene, indicating it contained an oxygenase component. The second fraction contained reductase activity which was absent from non-induced cells. This reductase activity is probably the NADH-acceptor reductase of AMO.

Chromatography, Gel

Metabolism of chlorinated alkenes and alkanes as related to toxicity.

The chlorine substitution in aliphatic compounds results, by its electron attracting effect, in a destabilization in alkanes and a stabilization in alkenes. Thus, with alkanes the main pathways of metabolic transformation to reactive intermediates are radical formation by C-C break or dechlorination, or dehydrochlorination. In alkenes, the stability of the molecule increases with the number of chlorine substitutions. In the series of chlorinated ethylenes, the first step of metabolic transformation is the oxidation to electrophilic oxiranes which may be hydrolized enzymatically or non-enzymatically, react with cellular nucleophiles, or rearrange to either chlorinated aldehydes or acyl chlorides. With tetra-, 1,2-cis- and trans-di-, 1,1-di-, and monochloroethylene, the metabolites identified in in vivo experiments are identical with the thermal rearrangement products of the respective oxiranes. An important exception is found with trichloroethylene, where the thermal rearrangement product is dichloroacetyl chloride; the metabolites in vivo, however, are entirely derived from trichloroacetaldehyde (chloral). The reason for this peculiar behavior is most probably a Lewis acid catalysis by the oxidizing enzyme system. Mutagenic and carcinogenic activities in the series of chlorinated ethylenes are determined by the stability of their oxiranes, which is higher in symmetrical than in unsymmetrical chlorine substitution: the relatively unstable and unsymmetric oxiranes of trichloroethylene, 1, 1,-dichloro-, and monochloroethylene are mutagenic in the Ames test; the more stable symmetric oxiranes of tetra-, 1,2-cis- and trans-dichloroethylenes are inactive.

Animals

Monitoring exposure to simple epoxides and alkenes through gas chromatographic determination of hemoglobin adducts.

A method for monitoring exposure to ethylene oxide (EO) and propylene oxide (PO) and their corresponding alkenes through the analysis of adducts to N-terminal valine in hemoglobin (Hb) using gas chromatography (GC) and electron-capture detection has been developed. The method is a further development of the so-called N-alkyl Edman method, which has thus far been carried out using gas chromatography-mass spectrometry (GC/MS). The correlation between GC and GC/MS determinations of adduct levels in human samples was found to be good. The newly developed GC method enables the determination of adducts to Hb from EO and PO down to levels of about 100 pmol/g globin. This adduct level corresponds to the expected increment from ethene in inhaled tobacco smoke in a smoker of about 10 cigarettes/day or from an average exposure to about 50 ppb EO or 1 ppm PO during working hours.

Alkenes

Long-chain (Z)-9-alkenes are "psychedelics" to houseflies with regard to visually stimulated sex attraction and aggregation.

Three different tests on houseflies (Musca domestica L.) revealed that both pheromone-free pseudoflies and male partner flies exhibit in the presence of mixtures of long-chain (Z)-9-alkenes or pure (Z)-9-tricosene enhanced releasing effects for two optical cues, which stimulate male houseflies to mating strikes and houseflies of both sexes to aggregation.

Alkenes

The soluble methane mono-oxygenase of Methylococcus capsulatus (Bath). Its ability to oxygenate n-alkanes, n-alkenes, ethers, and alicyclic, aromatic and heterocyclic compounds.

1. Methane mono-oxygenase of Methylococcus capsulatus (Bath) catalyses the oxidation of various substituted methane derivatives including methanol. 2. It is a very non-specific oxygenase and, in some of its catalytic properties, apparently resembles the analogous enzyme from Methylomonas methanica but differs from those found in Methylosinus trichosporium and Methylomonas albus. 3. CO is oxidized to CO2. 4. C1-C8 n-alkanes are hydroxylated, yielding mixtures of the corresponding 1- and 2-alcohols; no 3- or 4-alcohols are formed. 5. Terminal alkenes yield the corresponding 1,2-epoxides. cis- or trans-but-2-ene are each oxidized to a mixture of 2,3-epoxybutane and but-2-en-1-ol with retention of the cis or trans configuration in both products; 2-butanone is also formed from cis-but-2-ene only. 6. Dimethyl ether is oxidized. Diethyl ether undergoes sub-terminal oxidation, yielding ethanol and ethanal in equimolar amounts. 7. Methane mono-oxygenase also hydroxylates cyclic alkanes and aromatic compounds. However, styrene yields only styrene epoxide and pyridine yields only pyridine N-oxide. 8. Of those compounds tested, only NADPH can replace NADH as electron donor.

Alkanes

Microbial oxidation of gaseous hydrocarbons. II. Hydroxylation of alkanes and epoxidation of alkenes by cell-free particulate fractions of methane-utilizing bacteria.

Cell-free particulate fractions derived from methylotrophic bacteria catalyze the oxygen- and reduced nicotinamide adenine dinucleotide-dependent epoxidation of alkenes and hydroxylation of alkanes. Evidence presented indicates that the hydroxylation and epoxidation reactions are catalyzed by the same or a similar metal-containing monooxygenase.

Alkanes

Purification and characterization of 2-alkenal reductase.

The purification of a 2-alkenal reductase to homogeneity from a rat liver 100 000 times g supernatant is described. Its molecular weight has been determined by Sephadex G-100 chromatography and sodium dodecylsulfate polyacrylamide gel electrophoresis before and after reduction with mercaptoethanol and carboxymethylation. The monometric form has a molecular weight of 45 000. It tends to form, to a very small extent, dimeric and trimeric aggregates of molecular weights 90 000 and 135 000. The isoelectric point (IP) was determined to be 6.2 by isoelectric focusing.

Alkenes

Reaction of hydrogen sulphide with 2-alkenals.

Depending on the types of solvent and catalyst, different products are formed in the reaction of hydrogen sulphide with 2-alkenals. The structures of many of these products have been elucidated, and the reaction sequences leading to them are proposed.

Aldehydes

Hydration of arene and alkene oxides by epoxide hydrase in human liver microsomes.

The comparative hydration of styrene 7,8-oxide, octene 1,2-oxide, naphthalene 1,2-oxide, phenanthrene 9,10-oxide, benzo[a]anthracene 5,6-oxide, 3-methylcholanthrene 11,12-oxide, dibenzo[a,h]anthracene 5,6-oxide, and benzo[a, 7,8-, 9,10-, and 11,12-oxides to their respective dihydrodiols was investigated in microsomes from nine human autopsy livers. The substrate specificity of the epoxide hydrase in human liver microsomes was very similar to that of the epoxide hydrase in rat liver microsomes. Phenanthrene 9,10-oxide was the best substrate for the human and rat epoxide hydrases and dibenzo[a,h]anthracene 5,6-oxide and benzo[a-a)pyrene 11, 12-oxide were the poorest substrates. Plotting epoxide hydrase activity obtained with one substrate against epoxide hydrase activity for another substrate for each of the nine human livers revealed excellent correlations for all combinations of the 11 substrates studied (r = 0.87 to 0.99). The data suggest the presence in human liver of a single epoxide hydrase with broad substrate specificity. However, the results do not exclude the possible presence in human liver of several epoxide hydrases that are under similar regulatory control. These results suggest the need for further investigation to determine whether there is a safe epoxide of a drug whose in vivo metabolism is predictive of the capacity of different individuals to metabolize a wide variety of epoxides of drugs and environmental chemicals.

Alkenes

Stereoselective epoxidation of phenyl allyl ether by alkene-utilizing bacteria.

Eighteen newly isolated ethene- and propene-utilizing bacteria were screened for the ability to produce phenyl glycidyl ether, a common precursor for the synthesis of beta blockers, from phenyl allyl ether. These organisms included Aerococcus, Alcaligenes, Micrococcus and Staphylococcus spp. and a variety of Gram-negative, Gram-positive and Gram-variable mesophilic rods/coccobacilli not yet identified. The majority of ethene- and propene-grown cultures (14 strains) accumulated phenyl glycidyl ether (0.4-1.7 mM) as the sole oxidation product. The bioconversions with the three most promising ethene-utilizers (M26, M90C, M93A) were scaled-up to yield essentially optically pure (enantiomeric excess = 93%) S-(+)-phenyl glycidyl ether. This is currently under investigation for commercial production of optically pure beta blockers.

Alkenes