Expression of the tmoA-F gene cluster from Pseudomonas mendocina KRI in Escherichia coli BL21(DE3) produces a catalytically active form of the toluene-4-monooxygenase (T4MO) complex. Here we report the purification and characterization of four soluble proteins required for the in vitro reconstitution of T4MO catalytic activity. These proteins are a diiron hydroxylase (T4MOH), a Riesketype ferredoxin (T4MOC), an effector protein (T4MOD), and an NADH oxidoreductase (T4MOF). The T4MOH component is composed of the tmoA, tmoB, and tmoE gene products [quaternary structure (alpha beta epsilon)2, Mr approximately 220 kDa]. The T4MOA polypeptide contains two copies of the amino acid sequence motif (D/E)X(28-37)DEXRH; the same motif provides all of the protein-derived ligands to the diiron centers of ribonucleotide reductase, the soluble methane monooxygenase, and the stearoyl-ACP delta 9 desaturase. Mössbauer, optical, and EPR measurements show that the T4MOH contains diiron centers and suggest that the diiron center contains hydroxo bridge(s) in the diferric state, as observed for methane monooxygenase. Mössbauer and EPR measurements also show that the T4MOC contains a Rieske-type iron-sulfur center. This assignment is in accord with the presence of the amino acid sequence motif CPHX(15-17)CX2H, which has also been found in the bacterial, chloroplastic, and mitochondrial Rieske proteins as well as the bacterial NADH-dependent cis-dihydrodiol-forming aromatic dioxygenases. While single-turnover catalytic studies confirm the function of the T4MOH as the hydroxylase, the NADH-dependent multiple-turnover hydroxylation activity is increased by more than 100-fold in the presence of the T4MOC, which mediates highly specific electron transfer between the T4MOF and the T4MOH. The T4MOD can be purified as an 11.6 kDa monomeric protein devoid of cofactors or redox-active metal ions; this component is also detected as a substoichiometric consitutent of the purified T4MOH. The rate of the hydroxylation reaction can be mildly stimulated by the further addition of separately purified T4MOD to the T4MOH, implying the formation of a high affinity, catalytically competent complex between these two components. These characterizations define a novel, four-component oxygenase combining elements from the soluble methane oxidation complex of the methanotrophic bacteria and the aromatic hydroxylation complexes of the soil pseudomonads.

Experiments were performed to evaluate the effectiveness of two different methodological approaches for recovering DNA from soil and sediment bacterial communities: cell extraction followed by lysis and DNA recovery (cell extraction method) versus direct cell lysis and alkaline extraction to recover DNA (direct lysis method). Efficiency of DNA recovery by each method was determined by spectrophotometric absorbance and using a tritiated thymidine tracer. With both procedures, the use of polyvinylpolypyrrolidone was important for the removal of humic compounds to improve the purity of the recovered DNA; without extensive purification, various restriction enzymes failed to cut added target DNA. Milligram quantities of high-purity DNA were recovered from 100-g samples of both soils and sediments by the direct lysis method, which was a > 1-order-of-magnitude-higher yield than by the cell extraction method. The ratio of labeled thymidine to total DNA, however, was higher in the DNA recovered by the cell extraction method than by the direct lysis method, suggesting that the DNA recovered by the cell extraction method came primarily from active bacterial cells, whereas that recovered by the direct lysis method may have contained DNA from other sources.

A bacterium designated Pseudonocardia sp. strain ENV478 was isolated by enrichment culturing on tetrahydrofuran (THF) and was screened to determine its ability to degrade a range of ether pollutants. After growth on THF, strain ENV478 degraded THF (63 mg/h/g total suspended solids [TSS]), 1,4-dioxane (21 mg/h/g TSS), 1,3-dioxolane (19 mg/h/g TSS), bis-2-chloroethylether (BCEE) (12 mg/h/g TSS), and methyl tert-butyl ether (MTBE) (9.1 mg/h/g TSS). Although the highest rates of 1,4-dioxane degradation occurred after growth on THF, strain ENV478 also degraded 1,4-dioxane after growth on sucrose, lactate, yeast extract, 2-propanol, and propane, indicating that there was some level of constitutive degradative activity. The BCEE degradation rates were about threefold higher after growth on propane (32 mg/h/g TSS) than after growth on THF, and MTBE degradation resulted in accumulation of tert-butyl alcohol. Degradation of 1,4-dioxane resulted in accumulation of 2-hydroxyethoxyacetic acid (2HEAA). Despite its inability to grow on 1,4-dioxane, strain ENV478 degraded this compound for >80 days in aquifer microcosms. Our results suggest that the inability of strain ENV478 and possibly other THF-degrading bacteria to grow on 1,4-dioxane is related to their inability to efficiently metabolize the 1,4-dioxane degradation product 2HEAA but that strain ENV478 may nonetheless be useful as a biocatalyst for remediating 1,4-dioxane-contaminated aquifers.

Several propane-oxidizing bacteria were tested for their ability to degrade gasoline oxygenates, including methyl tert-butyl ether (MTBE), ethyl tert-butyl ether (ETBE), and tert-amyl methyl ether (TAME). Both a laboratory strain and natural isolates were able to degrade each compound after growth on propane. When propane-grown strain ENV425 was incubated with 20 mg of uniformly labeled [ 14 C]MTBE per liter, the strain converted >60% of the added MTBE to 14 CO 2 in <30 h. The initial oxidation of MTBE and ETBE resulted in the production of nearly stoichiometric amounts of tert-butyl alcohol (TBA), while the initial oxidation of TAME resulted in the production of tert-amyl alcohol. The methoxy methyl group of MTBE was oxidized to formaldehyde and ultimately to CO 2. TBA was further oxidized to 2-methyl-2-hydroxy-1-propanol and then 2-hydroxy isobutyric acid; however, neither of these degradation products was an effective growth substrate for the propane oxidizers. Analysis of cell extracts of ENV425 and experiments with enzyme inhibitors implicated a soluble P-450 enzyme in the oxidation of both MTBE and TBA. MTBE was oxidized to TBA by camphorgrown Pseudomonas putida CAM, which produces the well-characterized P-450cam, but not by Rhodococcus rhodochrous 116, which produces two P-450 enzymes. Rates of MTBE degradation by propane-oxidizing strains ranged from 3.9 to 9.2 nmol/min/mg of cell protein at 28°C, whereas TBA was oxidized at a rate of only 1.8 to 2.4 nmol/min/mg of cell protein at the same temperature.