Optimization of methanol biosynthesis from methane using Methylosinus trichosporium OB3b

Methylosinus trichosporium OB3b oxidized methane to methanol in the presence of a high concentration of Cu2+. Further oxidation of methanol to formaldehyde was prevented by adding 200 mM NaCl which acted as a methanol dehydrogenase H inhibitor. The bacterium, 0.6 mg dry cell ml(-1), in methane/air (1:4, v/v) at 25 degrees C in 12.9 mM phosphate buffer (pH 7) containing 20 mM sodium formate and 200 mM NaCl accumulated 7.7 mM methanol over 36 h.     

Copper-Binding Compounds from Methylosinus trichosporium OB3b

Two copper-binding compounds/cofactors (CBCs) were isolated from the spent media of both the wild type and a constitutive soluble methane monooxygenase (sMMO^C) mutant, PP319 (P. A. Phelps et al., Appl. Environ. Microbiol. 58:3701–3708, 1992), of Methylosinus trichosporium OB3b. Both CBCs are small polypeptides with molecular masses of 1,218 and 779 Da for CBC-L₁ and CBC-L₂, respectively. The amino acid sequence of CBC-L₁ is S?MYPGS?M, and that of CBC-L₂ is SPMP?S. Copper-free CBCs showed absorption maxima at 204, 275, 333, and 356 with shoulders at 222 and 400 nm. Copper-containing CBCs showed a broad absorption maximum at 245 nm. The low-temperature electron paramagnetic resonance (EPR) spectra of copper-containing CBC-L₁ showed the presence of a copper center with an EPR splitting constant between those of type 1 and type 2 copper centers (g_⊥ = 2.087, g_∥ = 2.42 G, |A_∥| = 128 G). The EPR spectrum of CBC-L₂ was more complex and showed two spectrally distinct copper centers. One signal can be attributed to a type 2 Cu²⁺ center (g_⊥ = 2.073, g_∥ = 2.324 G, |A_∥| = 144 G) which could be saturated at higher powers, while the second shows a broad, nearly isotropic signal near g_⊥ = 2.063. In wild-type strains, the concentrations of CBCs in the spent media were highest in cells expressing the pMMO and stressed for copper. In contrast to wild-type strains, high concentrations of CBCs were observed in the extracellular fraction of the sMMO^C mutants PP319 and PP359 regardless of the copper concentration in the culture medium.In methanotrophs, the relationship between the concentration of copper and expression of the two different methane monooxygenases (MMOs) is well characterized (8, 11, 45, 49, 50). Under low copper-to-biomass ratios, methane oxidation activity is observed in the soluble fraction, and the enzyme is referred to as the soluble methane monooxygenase (sMMO). At higher copper-to-biomass ratios, methane oxidation activity is observed in the membrane fraction, and the enzyme is referred to as the membrane-associated or particulate methane monooxygenase (pMMO). The polypeptides and structural genes for both enzymes have been characterized (4, 18–22, 24, 25, 32, 34–40, 43–45, 47–49, 51, 62, 63). In addition to expression of the two MMOs, four other physiological traits have been identified in cells expressing the pMMO that are affected by the copper concentration in the culture medium. First, the concentration of copper in the culture media is directly related to pMMO activity in cell-free fractions, although the levels of expression of pMMO polypeptides vary in different methanotrophs (1, 8, 30, 36, 50, 63). For example, the expression levels of the three pMMO polypeptides in Methylococcus capsulatus Bath remained constant with varying copper concentrations (8, 36), whereas in Methylomicrobium albus BG8, the expression level of the putative pMMO polypeptides increased with increased copper in the culture medium (8). Second, the concentrations of membrane-associated copper and iron show a proportional increase as the copper concentration in the culture medium is increased (36, 63). Third, the formation and level of intracytoplasmic membranes in cells cultured in copper-supplemented media are dependent on the copper concentration in the culture media (8, 11, 40, 48). Lastly, the K_s for methane oxidation by pMMO is altered by the copper concentration in the culture media (33a).Berson and Lidstrom (1) have recently noted that in spite of the central role of copper in the physiology of methanotrophs, the mechanism(s) of copper acquisition remains vague. Although true, a few studies have suggested the existence of a specific copper acquisition system in M. capsulatus Bath and M. trichosporium OB3b. The first indication of a specific copper uptake system was provided from phenotypic characterization of the constitutive sMMO mutants (sMMO^C) isolated by Phelps et al. (42). Fitch et al. (17) found that in M. trichosporium OB3b, these sMMO^C mutants were defective in copper uptake and showed preliminary evidence for an extracellular copper-complexing agent. Working with the same mutants, Téllez et al. partially purified this copper-complexing agent and determined that it was a small molecule with a molecular mass of approximately 500 Da with an association constant with copper of 1.4 × 10¹⁶ M⁻¹ (55). Other evidence for a specific copper uptake system was provided by the copper-binding cofactor (CBC) from M. capsulatus Bath (63). During the isolation of the pMMO from M. capsulatus Bath, CBC was identified in association with the purified enzyme, in the washed membrane fraction, and in the extracellular fraction. The CBC was determined to be a small polypeptide with a molecular mass of 1,232 Da. In M. capsulatus Bath, the cellular location of the CBC varied depending on the copper concentration in the culture medium and on the expression of the pMMO.This paper ties together and extends these observations on specific copper acquisition systems in M. trichosporium OB3b and M. capsulatus Bath. Here we describe the initial isolation and characterization of two copper-complexing agents, called CBC-L₁ and CBC-L₂, from the M. trichosporium OB3b wild type and sMMO^C mutant PP319. CBC-L₁ from M. trichosporium OB3b was identical to the CBC previously identified during the isolation of the pMMO from M. capsulatus Bath. This paper is also the first report of a second CBC, CBC-L₂, which may have been present as a contaminant in previous CBC preparations from M. capsulatus Bath. One or both of the CBCs appear to be the same copper-complexing agent partially purified by Téllez et al. (55). Lastly, this report describes the effect of the copper concentration in the culture medium on copper uptake, the expression of both MMOs, and extracellular concentration of the CBC in wild-type and sMMO^C mutant strains of M. trichosporium OB3b.     

Formate dehydrogenase from the methane oxidizer Methylosinus trichosporium OB3b.

Formate dehydrogenase (NAD+ dependent) was isolated from the obligate methanotroph Methylosinus trichosporium OB3b. When the enzyme was isolated anaerobically, two forms of the enzyme were seen on native polyacrylamide gels, DE-52 cellulose and Sephacryl S-300 columns; they were approximately 315,000 and 155,000 daltons. The enzyme showed two subunits on sodium dodecyl sulfate-polyacrylamide gels. The Mr of the alpha-subunit was 53,800 +/- 2,800, and that of the beta-subunit was 102,600 +/- 3,900. The enzyme (Mr 315,000) was composed of these subunits in an apparent alpha 2 beta 2 arrangement. Nonheme iron was present at a concentration ranging from 11 to 18 g-atoms per mol of enzyme (Mr 315,000). Similar levels of acid-labile sulfide were detected. No other metals were found in stoichiometric amounts. When the enzyme was isolated aerobically, there was no cofactor requirement for NAD reduction; however, when isolated anaerobically, activity was 80 to 90% dependent on the addition of flavin mononucleotide (FMN) to the reaction mixture. Furthermore, the addition of formate to an active, anoxic solution of formate dehydrogenase rapidly inactivated it in the absence of an electron acceptor; this activity could be reconstituted approximately 85% by 50 nM FMN. Flavin adenine dinucleotide could not replace FMN in reconstituting enzyme activity. The Kms of formate dehydrogenase for formate, NAD, and FMN were 146, 200, and 0.02 microM, respectively. "Pseudomonas oxalaticus" formate dehydrogenase, which has physical characteristics nearly identical to those of the M. trichosporium enzyme, was also shown to be inactivated under anoxic conditions by formate and reactivated by FMN. The evolutionary significance of this similarity is discussed.     

Formate dehydrogenase from Methylosinus trichosporium OB3b. Purification and spectroscopic characterization of the cofactors.

NAD(+)-coupled formate dehydrogenase has been purified to near-homogeneity from the obligate methanotroph Methylosinus trichosporium OB3b. The inclusion of stabilizing reagents in the purification buffers has resulted in a 3-fold increase in specific activity (98 microM/min/mg; turnover number 600 s-1) and as much as a 25-fold increase in yield over previously reported purification protocols. The enzyme, (molecular weight 400,000 +/- 20,000) is composed of four subunit types (alpha, 98,000; beta, 56,000; gamma, 20,000; delta, 11,500) apparently associated as 2 alpha beta gamma delta protomers. The holoenzyme contains flavin (1.8 +/- 0.2), iron (46 +/- 6), inorganic sulfide (38 +/- 4), and molybdenum (1.5 +/- 0.1). The flavin is optically similar to the common flavin cofactors, but it is chromatographically distinct. Anaerobic incubation of the enzyme with formate, NADH, or sodium dithionite, resulted in approximately 50% reduction of the iron and elicited an electron paramagnetic resonance (EPR) spectrum (approximately 2.5 spins/protomer) from which the spectra of five distinct EPR-active centers could be resolved in the g = 1.94 region. Four of these spectra were characteristic of [Fe-S]x clusters. The fifth (gave = 1.99; approximately 0.1 spins/protomer) was similar to that observed for the molybdenum cofactor of xanthine oxidase, and it exhibited the expected hyperfine splitting when the enzyme was enriched with 95Mo (I = 5/2). M?ssbauer spectroscopy showed that all of the iron in the enzyme became reduced upon the addition of a redox mediator, proflavin, to the dithionite reduced enzyme at pH 8.0. Nevertheless, a decrease in the EPR-active spin concentration in the g = 1.94 region of the spectrum occurred and was attributed to the reduction of the molybdenum center to the EPR-silent Mo(IV) state (S = 1). The fully reduced enzyme also exhibited a new species with an S = 3/2 ground state (1-2 spins/protomer). Addition of 50% ethylene glycol to the fully reduced enzyme revealed no new species, but caused an increase in the EPR-detectable spin quantitation to 5-6 spins/protomer. This suggests that cluster spin-spin interactions may occur in both the partially and fully reduced native enzyme.     

High-rate conversion of methane to methanol by Methylosinus trichosporium OB3b

Methanol was produced from methane with a high conversion rate using a high cell density process with Methylosinus trichosporium OB3b in the presence of a high concentration of phosphate buffer. More than 1.1 g/L methanol accumulated in the reaction media under optimized reaction conditions (17 g dry cell/L, 400 mmol/L phosphate, and 10 mmol/L MgCl₂) in the presence of 20 mmol/L sodium formate. The conversion rate of methane was over 60%. About 0.95 g/L methanol was produced when the biotransformation was carried out in a membrane aerated reactor into which methane and oxygen were introduced via two separate dense silicone tubing. Our results provide an efficient method and a promising process for high-rate conversion of methane to methanol.     

Purification and physical-chemical properties of methanobactin: a chalkophore from Methylosinus trichosporium OB3b

Methanobactin is an extracellular, copper-binding chromopeptide from the methane-oxidizing bacterium, Methylosinus trichosporium OB3b, believed to be involved in copper detoxification, sequestration, and uptake. Although small (1217.2 Da), methanobactin possesses a complex three-dimensional macrocyclic structure with several unusual moieties. The molecule binds one copper and has the N-2-isopropylester-(4-thionyl-5-hydroxyimidazolate)-Gly(1)-Ser(2)-Cys(3)-Tyr(4)-pyrrolidine-(4-hydroxy-5-thionylimidazolate)-Ser(5)-Cys(6)-Met(7) sequence [Kim, H. J., et al. (2004) Science 305, 1612-1615]. We report methods for purifying methanobactin from M. trichosporium OB3b and present initial evidence of its physiological function. MALDI-TOF MS was used to systematically monitor samples for optimizing purification conditions, and for detecting and analyzing specific metal-methanobactin complexes. Purification was performed by first stabilizing the extracted compound with copper followed by separation using reversed-phase HPLC in neutral pH buffers. Purified methanobactin exhibited UV-visible maxima at 342 nm, a shoulder at 388 nm, and a broad peak at 282 nm. These features were lost upon CuCl(2) titration with appearance of new features at 335, 356, 290, and 255 nm. Furthermore, methanobactin contains two fluorescent moieties, which exhibit broad emissions at 440-460 nm (lambda(max)(ex) at 388 nm) and 390-430 nm (lambda(max)(ex) = 342 nm), respectively. Finally, methanobactin eliminates the growth lag in M. trichosporium OB3b and substantially increases growth rates when cultures are exposed to elevated copper levels.     

Purification and properties of the methane mono-oxygenase enzyme system from Methylosinus trichosporium OB3b.

1. A three-component enzyme system that catalyses the oxidation of methane to methanol has been highly purified from Methylosinus trichosporium. 2. The components are (i) a soluble CO-binding cytochrome c, (ii) a copper-containing protein and (iii) a small protein; the mol. wts. are 13 000, 47 000 and 9400 respectively. The cytochrome component cannot be replaced by similar cytochrome purified from Pseudomonas extorquens or by horse heart cytochrome c. 3. The stoicheiometry suggests a mono-oxygenase mechanism and the specific activity with methane as substrate is 6 micronmol/min per mg of protein. 4. Other substrates rapidly oxidized are ethane, n-propane, n-butane and CO. Dimethyl ether is not a substrate. 5. The purified enzyme system utilizes ascorbate or, in the presence of partially purified M. trichosporium methanol dehydrogenase, methanol as electron donor but not NADH or NADPH. 6. Activity is highly sensitive to low concentrations of a variety of chelating agents, cyanide, 2-mercaptoethanol and dithiothreitol. 7. Activity is highly pH-dependent (optimum 6.9-7.0) and no component of the enzyme is stable to freezing. 8. The soluble CO-binding cytochrome c shows oxidase acitivity and the relationship between this and the oxygenase activity is discussed.     

Detoxification of Mercury by Methanobactin from Methylosinus trichosporium OB3b

Many methanotrophs have been shown to synthesize methanobactin, a novel biogenic copper-chelating agent or chalkophore. Methanobactin binds copper via two heterocyclic rings with associated enethiol groups. The structure of methanobactin suggests that it can bind other metals, including mercury. Here we report that methanobactin from Methylosinus trichosporium OB3b does indeed bind mercury when added as HgCl₂ and, in doing so, reduced toxicity associated with Hg(II) for both Alphaproteobacteria methanotrophs, including M. trichosporium OB3b, M. trichosporium OB3b ΔmbnA (a mutant defective in methanobactin production), and Methylocystis sp. strain SB2, and a Gammaproteobacteria methanotroph, Methylomicrobium album BG8. Mercury binding by methanobactin was evident in both the presence and absence of copper, despite the fact that methanobactin had a much higher affinity for copper due to the rapid and irreversible binding of mercury by methanobactin. The formation of a gray precipitate suggested that Hg(II), after being bound by methanobactin, was reduced to Hg(0) but was not volatilized. Rather, mercury remained associated with methanobactin and was also found associated with methanotrophic biomass. It thus appears that although the mercury-methanobactin complex was cell associated, mercury was not removed from methanobactin. The amount of biomass-associated mercury in the presence of methanobactin from M. trichosporium OB3b was greatest for M. trichosporium wild-type strain OB3b and the ΔmbnA mutant and least for M. album BG8, suggesting that methanotrophs may have selective methanobactin uptake systems that may be based on TonB-dependent transporters but that such uptake systems exhibit a degree of infidelity.     

Biodegradation of trichloroethylene by Methylosinus trichosporium OB3b

The methanotroph Methylosinus trichosporium OB3b, a type II methanotroph, degraded trichloroethylene at rates exceeding 1.2 mmol/h per g (dry weight) following the appearance of soluble methane monooxygenase in continuous and batch cultures. Cells capable oxidizing trichloroethylene contained components of soluble methane monooxygenase as demonstrated by Western blot (immunoblot) analysis with antibodies prepared against the purified enzyme. Growth of cultures in a medium containing 0.25 microM or less copper sulfate caused derepression of the synthesis of soluble methane monooxygenase. In these cultures, the specific rates of methane and methanol oxidation did not change during growth, while trichloroethylene oxidation increased with the appearance of soluble methane monooxygenase. M. trichosporium OB3b cells that contained soluble methane monooxygenase also degraded vinyl chloride, 1,1-dichloroethylene, cis-1,2-dichloroethylene, and trans-1,2-dichloroethylene.     

Degradation of dimethyl nitrosamine by Methylosinus trichosporium OB3b

The degradation of dimethyl nitrosoamine (DMNA) by a methanotroph, Methylosinus trichosporium OB3b, was studied using 14C-labelled DMNA. The organism was capable of assimilating DMNA-carbon and converting it to CO2. The rates of CO2 production (VCO2) from DMNA and its cellular uptake (VP) were linearly correlated with DMNA concentrations of 0.03-10 mM, which corresponded to approximately 3% of added DMNA metabolized in 24 h. These rates were two to three orders of magnitude less than the rate of uptake of methane (VCH4. VCH4 was suppressed when the concentrations of DMNA exceeded 0.3 mM. In the presence of 0.1 mM DMNA, VP and VCO2 were essentially the same in the presence or absence of methane in the first 8 h of incubation, but declined sharply thereafter only when methane was absent. These observations suggest that the metabolism of DMNA was carried out by methane monooxygenase (MMO), and that NADH, a cofactor for MMO, may be provided by the oxidation of the stored compounds in the cells when methane is not available.     

X-ray absorption spectroscopic studies of the methane monooxygenase hydroxylase component from Methylosinus trichosporium OB3b

The conversion from methane to methanol is catalyzed by methane monooxygenase (MMO) in methanotrophic bacteria. Earlier work on the crystal structures of the MMO hydroxylase component (MMOH) from Methylococcus capsulatus (Bath) at 4??°C and –160??°C has revealed two different core arrangements for the diiron active site. To ascertain the generality of these results, we have now carried out the first structural characterization on MMOH from Methylosinus trichosporium OB3b. Our X-ray absorption spectroscopic (XAS) analysis suggests the presence of two Fe-Fe distances of about 3?Å and 3.4?Å, which are proposed to reflect two populations of MMOH molecules with either a bis(μ-hydroxo)(μ-carboxylato)- or a (μ-hydroxo)(μ-carboxylato)diiron(III) core structure, respectively. The observation of these two different core structures, together with the crystallographic results of the MMOH from Methylococcus capsulatus (Bath), suggests the presence of an equilibrium that may reflect a core flexibility that is required to accommodate the various intermediates in the catalytic cycle of the enzyme. XAS studies on the binding of component B (MMOB) to the hydroxylase component show that MMOB does not perturb either this equilibrium or the gross structure of the oxidized diiron site in MMOH.     

Biodegradation of trichloroethylene by Methylosinus trichosporium OB3b.

The methanotroph Methylosinus trichosporium OB3b, a type II methanotroph, degraded trichloroethylene at rates exceeding 1.2 mmol/h per g (dry weight) following the appearance of soluble methane monooxygenase in continuous and batch cultures. Cells capable oxidizing trichloroethylene contained components of soluble methane monooxygenase as demonstrated by Western blot (immunoblot) analysis with antibodies prepared against the purified enzyme. Growth of cultures in a medium containing 0.25 microM or less copper sulfate caused derepression of the synthesis of soluble methane monooxygenase. In these cultures, the specific rates of methane and methanol oxidation did not change during growth, while trichloroethylene oxidation increased with the appearance of soluble methane monooxygenase. M. trichosporium OB3b cells that contained soluble methane monooxygenase also degraded vinyl chloride, 1,1-dichloroethylene, cis-1,2-dichloroethylene, and trans-1,2-dichloroethylene.     

Role of iron in particulate methane monooxygenase from Methylosinus trichosporium OB3b

The effect of iron ions on particulate methane monooxygenase was studied by using the EDTA-treated membranes from Methylosinus trichosporium OB3b. When the membrane was treated with EDTA the activity remained 82% of the as-isolated membranes, and the activity of the EDTA-treated membranes was strongly influenced by the addition of metal ions. Among the metal ions, ferric, ferrous and cupric ions stimulated the activity, indicating those ions were needed for the activity. When propargylamine was added, pMMO activity decreased and also the iron ESR signal decreased. As the ESR signal involves the ferrous nitrosyl complex in EDTA-treated membranes, the active site of pMMO may contain a mononuclear non-heme iron.     

The metal centers of particulate methane monooxygenase from Methylosinus trichosporium OB3b

Particulate methane monooxygenase (pMMO) is a membrane-bound metalloenzyme that oxidizes methane to methanol in methanotrophic bacteria. The nature of the pMMO active site and the overall metal content are controversial, with spectroscopic and crystallographic data suggesting the presence of a mononuclear copper center, a dinuclear copper center, a trinuclear center, and a diiron center or combinations thereof. Most studies have focused on pMMO from Methylococcus capsulatus (Bath). pMMO from a second organism, Methylosinus trichosporium OB3b, has been purified and characterized by spectroscopic and crystallographic methods. Purified M. trichosporium OB3b pMMO contains approximately 2 copper ions per 100 kDa protomer. Electron paramagnetic resonance (EPR) spectroscopic parameters indicate that type 2 Cu(II) is present as two distinct species. Extended X-ray absorption fine structure (EXAFS) data are best fit with oxygen/nitrogen ligands and reveal a Cu-Cu interaction at 2.52 A. Correspondingly, X-ray crystallography of M. trichosporium OB3b pMMO shows a dinuclear copper center, similar to that observed previously in the crystal structure of M. capsulatus (Bath) pMMO. There are, however, significant differences between the pMMO structures from the two organisms. A mononuclear copper center present in M. capsulatus (Bath) pMMO is absent in M. trichosporium OB3b pMMO, whereas a metal center occupied by zinc in the M. capsulatus (Bath) pMMO structure is occupied by copper in M. trichosporium OB3b pMMO. These findings extend previous work on pMMO from M. capsulatus (Bath) and provide new insight into the functional importance of the different metal centers.     

Molecular cloning of the methanol dehydrogenase structural gene fromMethylosinus trichosporium OB3b

A 4-kb fragment encoding methanol dehydrogenase (MDH) (EC 1.1.99.8) fromMethylosinus trichosporium OB3b has been cloned, with lambda gt11, and expressed inEscherichia coli K12. Organisms infected with recombinant phage express a fusion protein of bigger molecular weight than the purified MDH protein fromM. trichosporium OB3b. Subcloning of this fragment into pUC18 allowed identification of a recombinant plasmid, pCIT328, which contained a 2.1-kb fragment that expressed a protein that comigrated with purified MDH on polyacrylamide gels and cross-reacted with the antibody, indicative that the full MDH structural protein was encoded. This fragment also hybridized with an appropriate sized fragment fromM. trichosporium OB3b total DNA.     

Redox behavior of copper in particulate methane monooxygenase from Methylosinus trichosporium OB3b

The redox properties of the copper in particulate methane monooxygenase from Methylosinus trichosporium OB3b were investigated. The ESR spectrum of the pMMO-containing membranes from M. trichosporium OB3b indicated a typical type II copper (II) signal (g = 2.24, A = 18.4 mT, g = 2.06, ₂= 0.84). By anaerobic addition of excess amounts of duroquinol, an optimum reductant of pMMO, the ESR spectra indicated that the copper cluster in membranes was reduced and successively oxidized by dioxygen, a substrate of pMMO. The result suggests that the copper is the active site of pMMO or an electron carrier. During the titration, the intensity of the type II copper signal decreased with decreasing potential and the multiple hyperfine structure at g = 2.06 appeared clearly. Although the copper signal did not change by treatment of the EDTA-treated membranes with duroquinol and dioxygen, the copper signal intensity decreased with decreasing potential in the redox titration. These results suggest that some redox mediators play a role as an electron carrier between the active site and a reductant, and the presence of at least two types of copper sites in pMMO- containing membranes. On the basis of the ESR spectra of the EDTA-treated membranes and the as-isolated membranes, it is concluded that one type of the copper sites functions as the active site of pMMO (A-site), and the other type of copper sites plays a role as an electron carrier (E-site)     

Growth of Methylosinus trichosporium OB3b on methane and poly-beta-hydroxybutyrate biosynthesis

Optimal conditions for batch cultivation of the obligate methanotroph Methylosinus trichosporium OB3b on methane without superatmospheric pressure were chosen. The yield of absolutely dry biomass after 120 h of growth reached 20 g/l. This biomass contained 30% poly-beta-hydroxybutyrate (PHB) with molecular weight 300 kDa. The growth process included the stages of biomass growth and PHB biosynthesis. The latter stage occurred under nitrogen-deficiency conditions. It was accompanied by an increase in the activity of PHB biosynthesis enzymes (beta-ketothiolase, acetoacetyl-CoA reductase, and PHB synthase) and the main NAD(P)H producer, methylenetetrahydromethanopterin dehydrogenase. The activity of PHB depolymerase increased insignificantly.     

Trichloroethylene degradation and mineralization by pseudomonads and Methylosinus trichosporium OB3b

 To examine the trichloroethylene (C₂HCl₃)-degrading capability of five microorganisms, the maximum rate, extent, and degree of C₂HCl₃ mineralization were evaluated for Pseudomonas cepacia G4, Pseudomonas cepacia G4 PR1, Pseudomonas mendocina KR1, Pseudomonas putida F1, and Methylosinus trichosporium OB3b using growth conditions commonly reported in the literature for expression of oxygenases responsible for C₂HCl₃ degradation. By varying the C₂HCl₃ concentration from 5 μM to 75 μM, V _max and K _m values for C₂HCl₃ degradation were calculated as 9 nmol/(min mg protein) and 4 μM for P. cepacia G4, 18 nmol/(min mg protein) and 29 μM for P. cepacia G4 PR1, 20 nmol/(min mg protein) and 10 μM for P. mendocina KR1, and 8 nmol/(min mg protein) and 5 μM for P. putida F1. This is the first report of these Michaelis-Menten parameters for P. mendocina KR1, P. putida F1, and P. cepacia G4 PR1. At 75 μM, the extent of C₂HCl₃ that was degraded after 6 h of incubation with resting cells was 61%–98%; the highest degradation being achieved by toluene-induced P. mendocina KR1. The extent of C₂HCl₃ mineralization in 6 h (as indicated by concentration of chloride ion) was also measured and varied from 36% for toluene-induced P. putida F1 to 102% for M. trichosporium OB3b. Since C₂HCl₃ degradation requires new bio-mass, the specific growth rate (μ_max) of each of the C₂HCl₃-degradation microorganisms was determined and varied from 0.080/h (M. trichosporium OB3b) to 0.864/h (P. cepacia G4 PR1). Received: 1 May 1995/Received revision: 11 July 1995/Accepted: 26 July 1995