Methane Monooxygenase Activity Research Articles

Methylomonas lenta sp. nov., a methanotroph isolated from manure and a denitrification tank

Two methanotrophic bacteria, strains R-45377(T) and R-45370, were respectively isolated from a slurry pit of a cow stable and from a denitrification tank of a wastewater treatment plant in Belgium. The strains showed 99.9 % 16S rRNA gene sequence similarity. Cells were Gram-negative, motile rods containing type I methanotroph intracytoplasmic membranes. Colonies and liquid cultures appeared white to pale pink. The pmoA gene encoding particulate methane monooxygenase (pMMO) and the nifH gene encoding nitrogenase were present. Soluble methane monooxygenase (sMMO) activity, the presence of the mmoX gene encoding sMMO and the presence of the pxmA gene encoding a sequence-divergent pMMO were not detected. Methane and methanol were utilized as sole carbon sources. The strains grew optimally at 20 °C (range 15-28 °C) and at pH 6.8-7.3 (range pH 6.3-7.8). The strains grew in media supplemented with up to 1.2 % NaCl. The major cellular fatty acids were C16 : 1ω8c, C16 : 1ω5c, C16 : 1ω7c, C14 : 0, C15 : 0 and C16 : 0 and the DNA G+C content was 47 mol%. 16S rRNA gene- and pmoA-based phylogenetic analyses showed that the isolates cluster among members of the genus Methylomonas within the class Gammaproteobacteria, with pairwise 16S rRNA gene sequence similarities of 97.5 and 97.2 % between R-45377(T) and the closest related type strains, Methylomonas scandinavica SR5(T) and Methylomonas paludis MG30(T), respectively. Based on phenotypic characterization of strains R-45377(T) and R-45370, their low 16S rRNA gene sequence similarities and the formation of a separate phylogenetic lineage compared with existing species of the genus Methylomonas, we propose to classify these strains in a novel species, Methylomonas lenta sp. nov., with R-45377(T) ( = LMG 26260(T) = JCM 19378(T)) as the type strain.

Biological conversion of methane to methanol

The conversion of methane to methanol is important to economic utilization of natural/shale gas. Methanol is a valuable liquid fuel and raw material for various synthetic hydrocarbon products. Its industrial production is currently based on a two-step process that is energy-intensive and environmentally unfriendly, requiring high pressure and temperature. The biological oxidation of methane to methanol, based on methane monooxygenase activity of methanotrophic bacteria, is desirable because the oxidation is highly selective under mild conditions, but conversion rate and yield and stability of catalytic activity should be improved up to an industrially viable level. Since methanotrophic bacteria produce methanol as only a precursor of formaldehyde that is then used to synthesize various essential metabolites, the direct use of bacteria seems unsuitable for selective production of a large amount of methanol. There are two types of methane monooxygenase: soluble (sMMO) and particulate (pMMO) enzyme. sMMO consisting of three components (reductase, hydroxylase, and regulatory protein) features an (αβγ)2 dimer architecture with a di-iron active site in hydroxlase. pMMO, a trimer (pmoA, pmoB, and pmoC) in an α 3 β 3 γ 3 polypeptide arrangement is a copper enzyme with a di-copper active site located in the soluble domain of pmoB subunit. Since the membrane transports electrons well and delivers effectively methane with increased solubility in the lipid bilayer, pMMO seems more rationally designed enzyme in nature than sMMO. The engineering/evolution/modification of MMO enzymes using various biological and chemical techniques could lead to an optimal way to reach the ultimate goal of technically and economically feasible and environmentally friendly oxidation of methane. For this, multidisciplinary efforts from chemical engineering, protein engineering, and bioprocess research sectors should be systematically combined.

The Role of Copper in the Growth of<i> Methylosinus trichosporium</i> IMV 3011 and Poly-β-Hydroxybutyrate Biosynthesis

Methanotrophs are aerobic microorganisms that utilize methane as substrates for growth and PHB Biosynthesis. Copper plays an important role in cell growth and PHB biosynthesis. The effect of initial copper concentration on cultivation of M. trichosporium IMV 3011 on methane was investigated. With the addition of 30μmol/L CuSO4•5H2O, PMMO activity improved to 4 times of that without copper addition. The highest density of cultivated cells is 0.48g dry wtL-1, which is 2 times of that without copper addition. The lag time shortened to 15.87h, and the growth rate increased to 0.082h-1.The PHB content increased to 8.3%. It is found that certain initial copper concentration is beneficial to expression of high particulate methane monooxygenase activity, which may contribute to the synthesis of PHB in the cell.

Activities of Key Enzymes in the Biosynthesis of Poly-3-Hydroxybutyrate by Methylosinus trichosporium IMV3011

The activities of the key enzymes involved in the intracellular poly-3-hydroxybutyrate (PHB) synthesis of Methylosinus trichosporium IMV3011 were studied under various cultivation conditions. The enzymes were methane monooxygenase (MMO), β-ketothiolase, acetoacetyl-CoA reductase, PHB synthetase, and PHB depolymerase. Each enzyme had a unique catalytic mechanism. MMO activity decreased continuously with PHB production, but PHB at a high concentration was beneficial for maintaining MMO activity because more NADH was released by PHB depolymerization. The important reaction for entering the PHB cycle was catalyzed by β-ketothiolase. The monomer of β-hydroxybutyrate was synthesized by the catalysis of β-ketothiolase and acetoacetyl-CoA reductase. PHB synthetase played an important role in the PHB synthesis routes. The activity of PHB synthetase increased with PHB production. The changes of enzyme activities involved in PHB synthetase and PHB depolymerase occurred together, which indicated that the polymerization and depolymerization of intracellular PHB occurred simultaneously. The molecular weight of PHB was determined mainly by the combined actions of PHB synthetase and PHB depolymerase. Some important intermediates in the tricarboxylic acid cycle were helpful for PHB production because they increased related enzyme activities in the PHB cycle.

Priority pollutant degradation by the facultative methanotroph, Methylocystis strain SB2

Methylocystis strain SB2, a facultative methanotroph capable of growth on multi-carbon compounds, was screened for its ability to degrade the priority pollutants 1,2-dichloroethane (1,2-DCA), 1,1,2-trichloroethane (1,1,2-TCA), and 1,1-dichloroethylene (1,1-DCE), as well as cis-dichloroethylene (cis-DCE) when grown on methane or ethanol. Methylocystis strain SB2 degraded 1,2-DCA and 1,1,2-TCA when grown on either substrate and cis-DCE when grown on methane. Growth of Methylocystis strain SB2 on methane was inhibited in the presence of all compounds, while only 1,1-DCE and cis-DCE inhibited growth on ethanol. No degradation of any chlorinated hydrocarbon was observed in ethanol-grown cultures when particulate methane monooxygenase (pMMO) activity was inhibited with the addition of acetylene, indicating that competition for binding to the pMMO between the chlorinated hydrocarbons and methane limited both methanotrophic growth and pollutant degradation when this strain was grown on methane. Characterization of Methylocystis strain SB2 found no evidence of a high-affinity form of pMMO for methane, nor could this strain utilize 1,2-DCA or its putative oxidative products 2-chloroethanol or chloroactetic acid as sole growth substrates, suggesting that this strain lacks appropriate dehydrogenases for the conversion of 1,2-DCA to glyoxylate. As ethanol: (1) can be used as an alternative growth substrate for promoting pollutant degradation by Methylocystis strain SB2 as the pMMO is not required for its growth on ethanol and (2) has been used to enhance the mobility of chlorinated hydrocarbons in situ, it is proposed that ethanol can be used to enhance both pollutant transport and biodegradation by Methylocystis strain SB2.

Evaluation of methane oxidation activity in waste biocover soil during landfill stabilization

Biocover soil has been demonstrated to have high CH4 oxidation capacity and is considered as a good alternative cover material to mitigate CH4 emission from landfills, yet the response of CH4 oxidation activity of biocover soils to the variation of CH4 loading during landfill stabilization is poorly understood. Compared with a landfill cover soil (LCS) collected from Hangzhou Tianziling landfill cell, the development of CH4 oxidation activity of waste biocover soil (WBS) was investigated using simulated landfill systems in this study. Although a fluctuation of influent CH4 flux occurred during landfill stabilization, the WBS covers showed a high CH4 removal efficiency of 94–96% during the entire experiment. In the LCS covers, the CH4 removal efficiencies varied with the fluctuation of CH4 influent flux, even negative ones occurred due to the storage of CH4 in the soil porosities after the high CH4 influent flux of ∼137gm−2d−1. The lower concentrations of O2 and CH4 as well as the higher concentration of CO2 were observed in the WBS covers than those in the LCS covers. The highest CH4 oxidation rates of the two types of soil covers both occurred in the bottom layer (20–30cm). Compared to the LCS, the WBS showed higher CH4 oxidation activity and methane monooxygenase activity over the course of the experiment. Overall, this study indicated the WBS worked well for the fluctuation of CH4 influent flux during landfill stabilization.

Bacteriohemerythrin bolsters the activity of the particulate methane monooxygenase (pMMO) in Methylococcus capsulatus (Bath)

Recently, a native bacteriohemerythrin (McHr) has been identified in Methylococcus capsulatus (Bath). Both the particulate methane monooxygenase (pMMO) and McHr are over-expressed in cells of this bacterium when this strain of methanotroph is cultured and grown under high copper to biomass conditions. It has been suggested that the role of the McHr is to provide a shuttle to transport dioxygen from the cytoplasm of the cell to the intra-cytoplasmic membranes for consumption by the pMMO. Indeed, McHr enhances the activity of the pMMO when pMMO-enriched membranes are used to assay the enzyme activity. We find that McHr can dramatically improve the activity of pMMO toward the epoxidation of propylene to propylene oxide. The maximum activity is observed at a pMMO to McHr concentration ratio of 4:1, where we have obtained specific activities of 103.7nmol propylene oxide/min/mg protein and 122.8nmol propylene oxide/min/mg protein at 45°C when the turnover is driven by NADH and duroquinol, respectively. These results are consistent with the suggestion that the bacterium requires McHr to deliver dioxygen to the pMMO in the intra-cytoplasmic membranes to accomplish efficient catalysis of methane oxidation when the enzyme is over-expressed in the cells.

Pollutant degradation by a Methylocystis strain SB2 grown on ethanol: bioremediation via facultative methanotrophy

A facultative methanotroph, Methylocystis strain SB2, was examined for its ability to degrade chlorinated hydrocarbons when grown on methane or ethanol. Strain SB2 grown on methane degraded vinyl chloride (VC), trans-dichloroethylene (t-DCE), trichloroethylene (TCE), 1,1,1-trichloroethane (1,1,1-TCA), and chloroform (CF), but not dichloromethane (DCM). Growth on methane was reduced in the presence of any chlorinated hydrocarbon. Strain SB2 grown on ethanol degraded VC, t-DCE, and TCE, and 1,1,1-TCA, but not DCM or CF. With the exception of 1,1,1-TCA, the growth of strain SB2 on ethanol was not affected by any individual chlorinated hydrocarbon. No degradation of any chlorinated hydrocarbon was observed when acetylene was added to ethanol-grown cultures, indicating that this degradation was due to particulate methane monooxygenase (pMMO) activity. When mixtures of chlorinated alkanes or alkenes were added to cultures growing on methane or ethanol, chlorinated alkene degradation occurred, but chlorinated alkanes were not, and growth was reduced on both methane and ethanol. Collectively, these data indicate that competitive inhibition of pMMO activity limits methanotrophic growth and pollutant degradation. Facultative methanotrophy may thus be useful to extend the utility of methanotrophs for bioremediation as the use of alternative growth substrates allows for pMMO activity to be focused on pollutant degradation.

Stimulation of Methanotroph Activity by Cu-Substituted Borosilicate Glass

Previous investigations have shown that bacteria can derive benefits from elements within mineral assemblages associated with/or proximal to their point of attachment; however to date, no study has shown a direct connection between mineral dissolution and the biological oxidation of the greenhouse gas methane (CH4). Here we investigate linkages between the Cu content of silicate glasses (Si-glasses) and CH4 oxidation rates in Methylosinus trichosporium OB3b, a type II methanotroph. A series of batch growth experiments were performed under varying solid phase Cu (0, 80, 200, 400, and 800 ppm Cu) and initial aqueous phase methane concentrations (40, 70, and 130 nM CH4). Under near equilibrium conditions, the release of Cu from the glasses increased in association with M. trichosporium OB3b activity. The acquisition of Cu from the glasses directly influenced CH4 oxidation rates of M. trichosporium OB3b, presumably by promoting the expression and activity of copper-containing particulate methane monooxygenase (pMMO), the most efficient MMO for methane oxidation produced. Highest CH4 oxidation rates were observed in glasses with 80 ppm Cu. However, rates generally displayed an inverted-U relationship with solid-phase Cu concentration; i.e., rates were lower with solid phase Cu concentrations < 80 ppm or > 200 ppm. We conclude that in situ methanotroph activity in soils and sediments is strongly influenced by ambient solid-phase Cu concentrations, which has important implications to interpreting greenhouse gas flux data in geologic settings.

Copper enhances the activity and salt resistance of mixed methane-oxidizing communities

Effluents of anaerobic digesters are an underestimated source of greenhouse gases, as they are often saturated with methane. A post-treatment with methane-oxidizing bacterial consortia could mitigate diffuse emissions at such sites. Semi-continuously fed stirred reactors were used as model systems to characterize the influence of the key parameters on the activity of these mixed methanotrophic communities. The addition of 140 mg L(-1) NH (4) (+) -N had no significant influence on the activity nor did a temperature increase from 28 degrees C to 35 degrees C. On the other hand, addition of 0.64 mg L(-1) of copper(II) increased the methane removal rate by a factor of 1.5 to 1.7 since the activity of particulate methane monooxygenase was enhanced. The influence of different concentrations of NaCl was also tested, as effluents of anaerobic digesters often contain salt levels up to 10 g NaCl L(-1). At a concentration of 11 g NaCl L(-1), almost no methane-oxidizing activity was observed in the reactors without copper addition. Yet, reactors with copper addition exhibited a sustained activity in the presence of NaCl. A colorimetric test based on naphthalene oxidation showed that soluble methane monooxygenase was inhibited by copper, suggesting that the particulate methane monooxygenase was the active enzyme and thus more salt resistant. The results obtained demonstrate that the treatment of methane-saturated effluents, even those with increased ammonium (up to 140 mg L(-1) NH (4) (+) -N) and salt levels, can be mitigated by implementation of methane-oxidizing microbial consortia.

Epoxypropane biosynthesis by whole cell suspension of methanol-growth Methylosinus trichosporium IMV 3011

Methanotrophs containing methane monooxygenase (MMO) can catalyze the epoxidation of propene to epoxypropane. Methane cannot support dense biomass growth due to its low aqueous solubility. Low growth rate is important limiting factor for the application of methanotrophs. Methanol can act as growth substrate, but direct addition of methanol is toxic to most methanotrophs. The MMO activity during growth on methanol is also uncertain. In this paper, methanol-adapted Methylosinus trichosporium IMV 3011 was successfully cultivated at high cell densities using methanol as sole carbon source. A biomass density of 1.68 g dry weight cell l−1 was achieved and cells contained almost 80% of the MMO activity measured for cells grown with methane. It has been found that methanol can also act as the electron-donating substrate to regenerate the NADH and drive epoxypropane synthesis. The effect of methanol supply on the epoxidation capacity of Methylosinus trichosporium IMV3011 was studied in batch reactor. 0.016% methanol concentration was found to give the highest propene epoxidation capacity.

Influence of poisonous gases on the bio-oxidation of coalmine gas

Carbon monoxide (CO), hydrogen sulphide (H2S) and sulphur dioxide (SO2), which commonly appear and mix in coalmine gas, were investigated in terms of their effects on methane oxidation of methanotroph systems using single-factor and multi-factor experiments. The single-factor experiments that were performed showed that the methane oxidation rate and methane monooxygenase (MMO) activity of the test group at different concentrations had no evident variability when compared with the control group. Multi-factor experiments indicated that a mixture of CO, H2S and SO2 at various concentrations slightly inhibited the methane oxidation process of the methanotroph system. A pairwise comparison on the basis of sodium dodecyl sulphate polyacrylamide gel electrophoresis (SDS-PAGE) protein profiles demonstrated a high Jaccard index (ranging from 79 to 93%) similar to that of the methanotroph system, while the existence of CO, H2S and SO2, did not have evident effects on methane oxidation in the methanotroph system. Therefore, the possible concentrations of these gases in coalmines have no obvious influence on the methane oxidation of the methanotroph system. This system can be used effectively in the treatment of coalmine gas.

The Methane Monooxygenase Intrinsic Activity of Kinds of Methanotrophs

Methanotrophs have promising applications in the epoxidation of some alkenes and some chlorinated hydrocarbons and in the production of a biopolymer, poly-beta-hydroxybutyrate (poly-3-hydroxybutyrate; PHB). In contrast with methane monooxygenase (MMO) activity and ability of PHB synthesis of four kinds of methanotrophic bacteria Methylosinus trichosporium OB3b, M. trichosporium IMV3011, Methylococcus capsulatus HD6T, Methylomonas sp. GYJ3, and the mixture of the four kinds of strains, M. trichosporium OB3b is the highest of the four in the activity of propene epoxidation (10.72 nmol/min mg dry weight of cell [dwc]), the activity of naphthalene oxidation (22.7 mmol/mg dwc), and ability in synthesis of PHB(11% PHB content in per gram dry weight of cell in 84 h). It could be feasible to improve the MMO activity by mixing four kinds of methanotrophs. The MMO activity dramatically decreased when the cellular PHB accumulated in the second stage. The reason for this may be the dilution of the MMO system in the cells with increasing PHB contents. It has been found that the PHB contents at the level of 1-5% are beneficial to the cells for maintenance of MMO epoxidation activity when enough PHB have been accumulated. Moreover, it was also found that high particulate methane monooxygenase activity may contribute to the synthesis of PHB in the cell, which could be used to improve the yield of PHB in methanotrophs.

Characterization of cultivable methanotrophs from paddy soils and rice roots

Characterization of methanotrophs isolated from paddy soils and rice (Oryza sativa) roots was investigated in the present study. The number of methanotrophs in root homogenates of the rice cultivar Mutsuhomare was 4.9 × 107 most-probable-number (MPN) g−1 dry roots, in Yumeakari it was 2.0 × 108 MPN g−1 dry roots and in Kirara it was 4.6 × 107 MPN g−1 dry roots. Although bacterial cells were observed infrequently on the surface and in the interiors of roots before incubation, a large number of colonies, measuring 0.5–5 mm in diameter, were observed on the sterilized roots after incubation on nitrate mineral agar plates under methane in air. In particular, a large number of colonies were observed at the emergence sites of lateral roots and root hairs. Strains MD5-1 and M1 were isolated from the roots of Mutsuhomare and strain R62 was isolated from the root homogenate of Yumeakari. All isolates were catalase-positive and oxidase-positive, Gram-negative, straight-rod-shaped and curved-rod-shaped bacteria, and formed exospores. The isolates were able to fix nitrogen and grew in the absence of copper. In addition, all were found to be positive for naphthalene-oxidizing activities (corresponding to soluble methane mono-oxygenase activities). Strains MD5-1, M1 and R62 were closely related to Methylosinus sporium. Methanotrophic strains W3-6, SD3-5 and 2-19, isolated previously from paddy field soils, were classified into Methylosinus (W3-6) and Methylocystis (SD3-5 and 2-19) type II methanotrophs. Isolates from the rice roots (MD5-1, R62 and M1) grew logarithmically when casamino acid was used as the nitrogen source; however, the growth of these strains was reduced on the nitrate medium. These strains preferred amino acids over inorganic nitrogen as a nitrogen source for growth.

Copper methanobactin: a molecule whose time has come

Copper plays a key role in the physiology of methanotrophs. One way that these bacteria meet their high copper requirement is by the biosynthesis and release of high affinity copper binding compounds called methanobactins. Recent advances in methanobactin characterization include the first crystal structure, detailed spectroscopic analyses, and studies of metal ion specificity. Methanobactin may function in copper uptake, regulation of methane monooxygenase expression, protection against copper toxicity, and particulate methane monooxygenase activity. Methanobactin can extract copper from insoluble minerals and could be important for mineral weathering. Many methanobactin properties are reminiscent of iron siderophores, suggesting a similar mechanism of handling. Methanobactin-like compounds have also been identified in yeast mitochondria, suggesting that these molecules are a more universal phenomenon.

Copper(II) coordination polymers derived from triethanolamine and pyromellitic acid for bioinspired mild peroxidative oxidation of cyclohexane

The new inorganic 1D coordination polymer [Cu2(H3tea)2(mu4-pma)]n has been prepared, via self-assembly in aqueous medium, from copper(II) nitrate, triethanolamine (H3tea), pyromellitic acid (H4pma) and lithium hydroxide, and characterized by IR spectroscopy, elemental and single-crystal X-ray diffraction analyses. This compound and the related 2D polymer [Cu2(mu-H2tea)(2){mu3-Na2(H2O)4}(mu6-pma)]n.10nH2O are shown to mimic the alkane partial oxidation activity of the multicopper particulate methane monooxygenase, acting as catalysts precursors for the peroxidative oxidation of cyclohexane into cyclohexanol and cyclohexanone, by hydrogen peroxide (as green oxidant) and at room temperature in acidic MeCN/H2O medium. An overall yield (based on cyclohexane) of 29% has been achieved.

Mixed Pollutant Degradation by Methylosinus trichosporium OB3b Expressing either Soluble or Particulate Methane Monooxygenase: Can the Tortoise Beat the Hare?

Methanotrophs have been widely investigated for in situ bioremediation due to their ubiquity and their ability to degrade halogenated hydrocarbons through the activity of methane monooxygenase (MMO). It has been speculated that cells expressing the soluble form of MMO (sMMO) are more efficient in cleaning up sites polluted with halogenated hydrocarbons due to its broader substrate range and relatively fast degradation rates compared cells expressing the other form of MMO, the particulate MMO (pMMO). To examine this issue, the biodegradation of mixtures of chlorinated solvents, i.e., trichloroethylene (TCE), trans-dichloroethylene (t-DCE), and vinyl chloride (VC), by Methylosinus trichosporium OB3b in the presence of methane using either form of MMO was investigated over longer time frames than those commonly used, i.e., days instead of hours. Growth of M. trichosporium OB3b along with pollutant degradation were monitored and analyzed using a simple comparative model developed from the Omega model created for analysis of the competitive binding of oxygen and carbon dioxide by ribulose bisphosphate carboxylase. From these findings, it appears that at concentrations of VC, t-DCE, and TCE greater than 10 microM each, methanotrophs expressing pMMO have a competitive advantage over cells expressing sMMO due to higher growth rates. Despite such an apparent growth advantage, pMMO-expressing cells degraded less of these substrates at these concentrations than sMMO-expressing cells during active growth. If the concentrations were increased to 100 muM, however, not only did pMMO-expressing cells grow faster, they degraded more of these pollutants and did so in a shorter amount of time. These findings suggest that the relative rates of growth substrate and pollutant degradation are important factors in determining which form of MMO should be considered for pollutant degradation.

Development and mathematical modeling of a two-stage reactor system for trichloroethylene degradation using Methylosinus trichosporium OB3b

A two-stage reactor system was developed for the continuous degradation of gas-phase trichloroethylene (TCE). Methylosinus trichosporium OB3b was immobilized on activated carbon in a TCE degradation reactor, trickling biofilter (TBF). The TBF was coupled with a continuous stirred tank reactor (CSTR) to allow recirculation of microbial cells from/to the TBF for the reactivation of inactivated cells during TCE degradation. The mass transfer aspect of the TBF was analyzed, and mass transfer coefficient of 3.9 h(-1) was estimated. The loss of soluble methane monooxygenase (sMMO) activity was modeled based on a material balance on the CSTR and TBF, and transformation capacity (T (c)) was determined to be 20.2 micromol mg(-1). Maximum TCE degradation rate of 525 mg 1(-1) d(-1) was obtained and reactor has been stably operated for more than 270 days.

Effect of methanobactin on the activity and electron paramagnetic resonance spectra of the membrane-associated methane monooxygenase in Methylococcus capsulatus Bath

Improvements in the purification of methanobactin (mb) from either Methylosinus trichosporium OB3b(T) or Methylococcus capsulatus Bath resulted in preparations that stimulated methane-oxidation activity in both whole-cell and cell-free fractions of Methylococcus capsulatus Bath expressing the membrane-associated methane monooxygenase (pMMO). By using washed membrane factions with pMMO activities in the 290 nmol propylene oxidized min(-1) (mg protein)(-1) range, activities approaching 400 nmol propylene oxidized min(-1) (mg protein)(-1) were commonly observed following addition of copper-containing mb (Cu-mb), which represented 50-75 % of the total whole-cell activity. The stimulation of methane-oxidation activity by Cu-mb was similar to or greater than that observed with equimolar concentrations of Cu(II), without the inhibitory effects observed with high copper concentrations. Stimulation of pMMO activity was not observed with copper-free mb, nor was it observed when the copper-to-mb ratio was <0.5 Cu atoms per mb. The electron paramagnetic resonance (EPR) spectra of mb differed depending on the copper-to-mb ratio. At copper-to-mb ratios of <0.4 Cu(II) per mb, Cu(II) addition to mb showed an initial coordination by both sulfur and nitrogen, followed by reduction to Cu(I) in <2 min. At Cu(II)-to-mb ratios between 0.4 and 0.9 Cu(II) per mb, the intensity of the Cu(II) signal in EPR spectra was more representative of the Cu(II) added and indicated more nitrogen coordination. The EPR spectral properties of mb and pMMO were also examined in the washed membrane fraction following the addition of Cu(II), mb and Cu-mb in the presence or absence of reductants (NADH or duroquinol) and substrates (CH4 and/or O2). The results indicated that Cu-mb increased electron flow to the pMMO, increased the free radical formed following the addition of O2 and decreased the residual free radical following the addition of O2 plus CH4. The increase in pMMO activity and EPR spectral changes to the pMMO following Cu-mb addition represent the first positive evidence of interactions between the pMMO and Cu-mb.

Evaluation of transformation capacity for degradation of ethylene chlorides byMethylosinus trichosporium OB3b

The transformation capacity (Tc) ofMethylosinus trichosporium OB3b in the degradation of ethylene chlorides was determined by measuring the decrease of soluble methane monooxygenase (sMMO) activity of resting cells in batch experiments. All measurements of sMMO activity were taken in the presence of 20 mM formate to avoid the deficiency of reducing power, and within 2 hrs to avoid the effect of natural inactivation from instability of the resting cells. The constant Tc values of 0.58±0.132 and 0.80±0.17 μmol/mg cell were obtained for trichloroethylene (TCE) and 1,2-dichloroethylene (cis andtrans-1,2-DCE), respectively, regardless of their concentrations. The transformation capacity measured by this method can be used to predict the amount of cells that should be stimulated inin-situ bioremediation.