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Proteomic analysis of the benzoate degradation pathway in Acinetobacter sp. KS-1.

The purpose of this study was to perform proteome analysis of Acinetobacter sp. KS-1, a bacterium capable of degrading benzoate as a sole carbon source. In order to understand the benzoate degradation pathway used by strain KS-1, proteomes of benzoate-cultured and succinate-cultured KS-1 were comparatively analyzed by two dimensional gel electrophoresis (2-DE). Eighteen protein spots proteins were exclusively induced from the benzoate-cultured strain KS-1. Of these 18 spots, two benzoate-degrading enzymes (catechol 1,2-dioxygenase and beta-ketoadipate succinyl-CoA transferase) were identified by MS/MS analysis by MALDI-TOF/TOF mass spectrometry, which suggests that strain KS-1 degrades benzoate by the beta-ketoadipate pathway. DEAE-chromatography suggested that strain KS-1 induced only one type of catechol 1,2-dioxygenase during benzoate degradation. The catechol 1,2-dioxygenase was purified using three steps of ammonium sulfate precipitation, DEAE-sepharose, and Mono-Q chromatography. The purified catechol 1,2-dioxygenase of strain KS-1 had strong dioxygenase activity for 4-methylcatechol as well as catechol. Sequencing analysis using N-terminal and internal amino acid sequences showed that this catechol 1,2-dioxygenase is highly homologous with catechol 1,2-dioxygenase of Acinetobacter radioresistens. These results suggest that comparative proteomic analysis of biodegrading bacteria cultured under different conditions may be a useful initial step toward the elucidation of the aromatic compound degradation pathway.

Acinetobacter↗

Evidence for anaerobic syntrophic benzoate degradation threshold and isolation of the syntrophic benzoate degrader.

An anaerobic, motile, gram-negative, rod-shaped, syntrophic, benzoate-degrading bacterium, strain SB, was isolated in pure culture with crotonate as the energy source. Benzoate was degraded only in association with an H2-using bacterium. The kinetics of benzoate degradation by cell suspensions of strain SB in coculture with Desulfovibrio strain G-11 was studied by using progress curve analysis. The coculture degraded benzoate to a threshold concentration of 214 nM to 6.5 microM, with no further benzoate degradation observed even after extended incubation times. The value of the threshold depended on the amount of benzoate added and, consequently, the amount of acetate produced. The addition of sodium acetate, but not that of sodium chloride, affected the threshold value; higher acetate concentrations resulted in higher threshold values for benzoate. When a cell suspension that had reached a threshold benzoate concentration was reamended with benzoate, benzoate was used without a lag. The hydrogen partial pressure was very low and formate was not detected in cell suspensions that had degraded benzoate to a threshold value. The Gibbs free energy change calculations showed that the degradation of benzoate was favorable when the threshold was reached. These studies showed that the threshold for benzoate degradation was not caused by nutritional limitations, the loss of metabolic activity, or inhibition by hydrogen or formate. The data are consistent with a thermodynamic explanation for the existence of a threshold, but a kinetic explanation based on acetate inhibition may also account for the existence of a threshold.

Acetates↗

BadR, a new MarR family member, regulates anaerobic benzoate degradation by Rhodopseudomonas palustris in concert with AadR, an Fnr family member.

A cluster of genes for the anaerobic degradation of benzoate has been described for the phototrophic bacterium Rhodopseudomonas palustris. Here we provide an initial analysis of the regulation of anaerobic benzoate degradation by examining the contributions of two regulators: a new regulator, BadR, encoded by the benzoate degradation gene cluster, and a previously described regulator, AadR, whose gene lies outside the cluster. Strains with single mutations in either badR or aadR grew slowly on benzoate but were relatively unimpaired in growth on succinate and several intermediates of benzoate degradation. A badR aadR double mutant was completely defective in anaerobic growth on benzoate. Effects of the regulators on transcriptional activation were monitored with an R. palustris strain carrying a chromosomal fusion of 'lacZ to the badE gene of the badDEFG operon. This operon encodes benzoyl-coenzyme A (benzoyl-CoA) reductase, an unusual oxygen-sensitive enzyme that catalyzes the benzene ring reduction reaction that is the rate-limiting step in anaerobic benzoate degradation. Expression of badE::'lacZ was induced 100-fold when cells grown aerobically on succinate were shifted to anaerobic growth on succinate plus benzoate. The aadR gene was required for a 20-fold increase in expression that occurred in response to anaerobiosis, and badR was responsible for a further 5-fold increase in expression that occurred in response to benzoate. Further studies with the badE::'lacZ fusion strain grown with various kinds of aromatic acids indicated that BadR probably responds to benzoyl-CoA acting as an effector molecule. Sequence information indicates that BadR is a member of the MarR family of transcriptional regulators. These studies expand the range of functions regulated by MarR family members to include anaerobic aromatic acid degradation and provide an example of a MarR-type protein that acts as a positive regulator rather than as a negative regulator, as do most MarR family members. AadR resembles the Escherichia coli Fnr regulator in sequence and contains cysteine residues that are spaced appropriately to serve in the capacity of a redox-sensing protein.

Anaerobiosis↗

Interspecies acetate transfer influences the extent of anaerobic benzoate degradation by syntrophic consortia.

Benzoate degradation by an anaerobic, syntrophic bacterium, strain SB, in coculture with Desulfovibrio sp. strain G-11 reached a threshold value which depended on the amount of acetate added and ranged from about 2.5 to 29.9 (mu)M. Increasing acetate concentrations also uncompetitively inhibited benzoate degradation. The apparent V(infmax) and apparent K(infm) for benzoate degradation decreased with increasing acetate concentration, but the benzoate degradation capacities (V(infmax)/K(infm)) of cell suspensions remained comparable. The addition of an acetate-using bacterium to cocultures after the threshold was reached resulted in the degradation of benzoate to below the detection limit. Mathematical simulations showed that the benzoate threshold was not predicted by the inhibitory effect of acetate on benzoate degradation kinetics. With nitrate instead of sulfate as the terminal electron acceptor, no benzoate threshold was observed in the presence of 20 mM acetate even though the kinetics of benzoate degradation were slower with nitrate rather than sulfate as the electron acceptor. When strain SB was grown with Desulfovibrio sp. strain DG2 that had a fourfold-lower V(infmax) for hydrogen use than strain G-11, the V(infmax) for benzoate degradation was 37-fold lower than that of strain SB-G-11 cocultures. The Gibb's free energy for benzoate degradation was less negative in cell suspensions with a threshold than in suspensions without a threshold. These studies showed that the threshold was not a function of the inhibition of benzoate degradation by acetate or the toxicity of the undissociated form of acetate. Rather, a critical or minimal Gibb's free energy may exist where thermodynamic constraints preclude further benzoate degradation.

Journal Article↗

Acetate inhibition of methanogenic, syntrophic benzoate degradation.

Acetate inhibited benzoate degradation by a syntrophic coculture of an anaerobic benzoate degrader (strain BZ-2) and Methanospirillum strain PM-1; the apparent K(i) for acetate was approximately 40 mM. The addition of acetate resulted in a decrease in the hydrogen concentration in the coculture, indicating that phenomena related to interspecies hydrogen transfer affected this value and that the effect of acetate on the benzoate-degrading partner was probably greater than the apparent K(i) for the coculture suggests.

Journal Article↗

Anaerobic degradation of 2-fluorobenzoate by benzoate-degrading, denitrifying bacteria.

Three strains of anaerobically benzoate-degrading, denitrifying bacteria of the genus Pseudomonas were able to grow on 2-fluorobenzoate as the sole carbon and energy source. Fluoride ion release was stoichiometric, and the reduction of dissolved organic carbon indicated total degradation. Cells grown anaerobically with benzoate were adapted for immediate growth with 2-fluorobenzoate, and both compounds were substrates for an inducible benzoyl-coenzyme A synthetase, the initial enzyme of anaerobic degradation. It is proposed that fluoride is eliminated gratuitously by a regioselective reaction in a sequence common to both carbon sources. Benzoate, but not 2-fluorobenzoate, was oxidized by aerobically grown cells.

Acetate-CoA Ligase↗

Anaerobic Metabolism of Cyclohex-1-Ene-1-Carboxylate, a Proposed Intermediate of Benzoate Degradation, by Rhodopseudomonas palustris.

Anaerobic benzoate degradation by the phototrophic bacterium Rhodopseudomonas palustris has been proposed to proceed via aromatic ring reduction reactions leading to cyclohex-1-ene-1-carboxyl-coenzyme A (CoA) formation. The alicyclic product is then proposed to undergo three beta-oxidation-like modifications resulting in ring cleavage. Illuminated suspensions of benzoate-grown cells converted [7-C]cyclohex-1-ene-1-carboxylate to intermediates that comigrated with cyclohex-1-ene-1-carboxyl-CoA, 2-hydroxycyclohexanecar-boxyl-CoA, 2-ketocyclohexanecarboxyl-CoA, and pimelyl-CoA by thin-layer chromatography. This set of intermediates was also formed by cells grown anaerobically or aerobically on cyclohex-1-ene-1-carboxylate, indicating that benzoate-grown and cyclohex-1-ene-1-carboxylate-grown cells degrade this alicyclic acid by the same catabolic route. Four enzymatic activities proposed to be required for conversion of cyclohex-1-ene-1-carboxylate to pimelyl-CoA were detected at 3- to 10-fold-higher levels in benzoate-grown cells than in succinate-grown cells. These were cyclohex-1-ene-1-carboxylate-CoA ligase, cyclohex-1-ene-1-carboxyl-CoA hydratase, 2-hydroxycyclohexanecarboxyl-CoA dehydrogenase, and 2-ketocyclohexanecarboxyl-CoA hydrolase (ring cleaving). Pimelyl-CoA was identified in hydrolase reaction mixtures as the product of alicyclic ring cleavage. The results provide a first demonstration of an alicyclic ring cleavage activity.

Journal Article↗

2-Hydroxycyclohexanecarboxyl coenzyme A dehydrogenase, an enzyme characteristic of the anaerobic benzoate degradation pathway used by Rhodopseudomonas palustris.

A gene, badH, whose predicted product is a member of the short-chain dehydrogenase/reductase family of enzymes, was recently discovered during studies of anaerobic benzoate degradation by the photoheterotrophic bacterium Rhodopseudomonas palustris. Purified histidine-tagged BadH protein catalyzed the oxidation of 2-hydroxycyclohexanecarboxyl coenzyme A (2-hydroxychc-CoA) to 2-ketocyclohexanecarboxyl-CoA. These compounds are proposed intermediates of a series of three reactions that are shared by the pathways of cyclohexanecarboxylate and benzoate degradation used by R. palustris. The 2-hydroxychc-CoA dehydrogenase activity encoded by badH was dependent on the presence of NAD(+); no activity was detected with NADP(+) as a cofactor. The dehydrogenase activity was not sensitive to oxygen. The enzyme has apparent K(m) values of 10 and 200 microM for 2-hydroxychc-CoA and NAD(+), respectively. Western blot analysis with antisera raised against purified His-BadH identified a 27-kDa protein that was present in benzoate- and cyclohexanecarboxylate-grown but not in succinate-grown R. palustris cell extracts. The active form of the enzyme is a homotetramer. badH was determined to be the first gene in an operon, termed the cyclohexanecarboxylate degradation operon, containing genes required for both benzoate and cyclohexanecarboxylate degradation. A nonpolar R. palustris badH mutant was unable to grow on benzoate or cyclohexanecarboxylate but had wild-type growth rates on succinate. Cells blocked in expression of the entire cyclohexanecarboxylate degradation operon excreted cyclohex-1-ene-1-carboxylate into the growth medium when given benzoate. This confirms that cyclohex-1-ene-1-carboxyl-CoA is an intermediate of anaerobic benzoate degradation by R. palustris. This compound had previously been shown not to be formed by Thauera aromatica, a denitrifying bacterium that degrades benzoate by a pathway that is slightly different from the R. palustris pathway. 2-Hydroxychc-CoA dehydrogenase does not participate in anaerobic benzoate degradation by T. aromatica and thus may serve as a useful indicator of an R. palustris-type benzoate degradation pathway.

Alcohol Oxidoreductases↗

The pimFABCDE operon from Rhodopseudomonas palustris mediates dicarboxylic acid degradation and participates in anaerobic benzoate degradation.

Bacteria in anoxic environments typically convert aromatic compounds derived from pollutants or green plants to benzoyl-CoA, and then to the C7 dicarboxylic acid derivative 3-hydroxypimelyl-CoA. Inspection of the recently completed genome sequence of the purple nonsulfur phototroph Rhodopseudomonas palustris revealed one predicted cluster of genes for the beta-oxidation of dicarboxylic acids. These genes, annotated as pimFABCDE, are predicted to encode acyl-CoA ligase, enoyl-CoA hydratase, acyl-CoA dehydrogenase and acyl-CoA transferase enzymes, which should allow the conversion of odd-chain dicarboxylic acids to glutaryl-CoA, and even-chain dicarboxylic acids to succinyl-CoA. A mutant strain that was deleted in the pim gene cluster grew at about half the rate of the wild-type parent when benzoate or pimelate was supplied as the sole carbon source. The mutant grew five times more slowly than the wild-type on the C14 dicarboxylic acid tetradecanedioate. The mutant was unimpaired in growth on the C8-fatty acid caprylate. The acyl-CoA ligase predicted to be encoded by the pimA gene was purified, and found to be active with C7-C14 dicarboxylic and fatty acids. The expression of a pimA-lacZ chromosomal gene fusion increased twofold when cells were grown in the presence of straight-chain C7-C14 dicarboxylic and fatty acids. These results suggest that the beta-oxidation enzymes encoded by the pim gene cluster are active with medium-chain-length dicarboxylic acids, including pimelate. However, the finding that the pim operon deletion mutant is still able to grow on dicarboxylic acids, albeit at a slower rate, indicates that R. palustris has additional genes that can also specify the degradation of these compounds.

Anaerobiosis↗

Roles of CatR and cis,cis-muconate in activation of the catBC operon, which is involved in benzoate degradation in Pseudomonas putida.

In Pseudomonas putida, the catBC operon encodes enzymes involved in benzoate degradation. Previous studies have determined that these enzymes are induced when P. putida is grown in the presence of benzoate. Induction of the enzymes of the catBC operon requires an intermediate of benzoate degradation, cis,cis-muconate, and a regulatory protein, CatR. It has been determined that CatR binds to a 27-bp region of the catBC promoter in the presence or absence of inducer. We have called this the repression binding site. In this study, we used a gel shift assay to demonstrate that the inducer, cis,cis-muconate, increases the affinity of CatR for the catBC promoter region by 20-fold. Furthermore, in the absence of cis,cis-muconate, CatR forms two complexes in the gel shift assay. The inducer cis,cis-muconate confers specificity primarily for the formation of complex 2. DNase I footprinting showed that an additional 27 bp of the catBC promoter region is protected by CatR in the presence of cis,cis-muconate. We have named this second binding site the activation binding site. Methylation interference footprinting determined that in the presence or absence of inducer, five G nucleotides of the catBC promoter region were necessary for CatR interaction with the repression binding site, while a single G residue was important for CatR interaction with the activation binding site in the presence of cis,cis-muconate. Using polymerase chain reaction-generated constructs, we found that the binding of CatR to the repression binding site is independent of the activation binding site. However, binding of CatR to the activation binding site required an intact repression binding site.

Bacterial Proteins↗

Sporotomaculum syntrophicum sp. nov., a novel anaerobic, syntrophic benzoate-degrading bacterium isolated from methanogenic sludge treating wastewater from terephthalate manufacturing.

An anaerobic, mesophilic, syntrophic benzoate-degrading bacterium, designated strain FB(T), was isolated from methanogenic sludge which had been used to treat wastewater from the manufacture of terephthalic acid. Cells were non-motile gram-positive rods that formed spores. The optimum temperature for growth was 35-40 degrees C, and the optimum pH was 7.0-7.2. A co-culture with the hydrogenotrophic methanogen Methanospirillum hungatei converted benzoate to acetate, carbon dioxide, and methane. Butyrate transiently accumulated at a high concentration of 2.5 mM during degradation. Besides benzoate, no other compound tested supported growth of the co-culture. Crotonate supported growth of strain FB(T) in pure culture. Furthermore, the strain degraded benzoate in pure culture with crotonate as co-substrate to produce acetate and butyrate. The strain was not able to utilize sulfate, sulfite, thiosulfate, nitrate, fumarate, or Fe(III) as electron acceptor. The G+C content of the DNA was 46.8 mol%. Strain FB(T) contained MK-7 as the major quinone and C(16:1) as the major fatty acid. 16S rDNA sequence analysis revealed that the strain was a member of the genus Sporotomaculum, even though it exhibited significant differences, such as the capacity for syntrophic growth, to the known member of the genus. Hence, we propose the name Sporotomaculum syntrophicum sp. nov. for strain FB(T). The type strain is strain FB(T) (DSM 14795, JCM 11475).

Bacteria, Anaerobic↗

A catabolic gene cluster for anaerobic benzoate degradation in methanotrophic microbial Black Sea mats.

A microbial mat from the Black Sea shelf was analyzed by a metagenomic approach. While the habitat and its microbial community are characterized by anaerobic methane oxidation, a 79 kb contiguous DNA sequence obtained from the same mat provided first evidence for the concomitant presence of the capacity for anaerobic benzoate degradation. Benzoyl-CoA is one central intermediate of anaerobic aromatic degradation, among others. Within a stretch of 31 kb, all genes required for the complete pathway of anaerobic benzoate degradation (catabolic island) were identified, including the four subunits of the key enzyme benzoyl-CoA reductase (bcrCBAD), which catalyzes the ATP-driven 2-electron reduction of the aromatic ring. Genes for a ketoacid:acceptor oxidoreductase (korABC) and a ferredoxin (fdx), which are required for generation of a suitable electron donor, were also detected. The majority of the identified catabolic gene products are most similar to their respective orthologs from the denitrifying freshwater bacterium Azoarcus evansii, and the genes are also similarly organized. Due to the lack of established markers, the phylogenetic affiliation of the source organism remains unclear. The presented findings indicate that the metabolic diversity of the Black Sea mat is wider than currently known and that probably other bacteria than those of the methane-oxidizing consortia contribute to aromatic degradation in this anoxic habitat.

Anaerobiosis↗

Regulation of benzoate degradation in Acinetobacter sp. strain ADP1 by BenM, a LysR-type transcriptional activator.

In Acinetobacter sp. strain ADP1, benzoate degradation requires the ben genes for converting benzoate to catechol and the cat genes for degrading catechol. Here we describe a novel transcriptional activator, BenM, that regulates the chromosomal ben and cat genes. BenM is homologous to CatM, a LysR-type transcriptional activator of the cat genes. Unusual regulatory features of this system include the abilities of both BenM and CatM to recognize the same inducer, cis,cis-muconate, and to regulate some of the same genes, such as catA and catB. Unlike CatM, BenM responded to benzoate. Benzoate together with cis,cis-muconate increased the BenM-dependent expression of the benABCDE operon synergistically. CatM was not required for this synergism, nor did CatM regulate the expression of a chromosomal benA::lacZ transcriptional fusion. BenM-mediated regulation differs significantly from that of the TOL plasmid-encoded conversion of benzoate to catechol in pseudomonads. The benM gene is immediately upstream of, and divergently transcribed from, benA, and a possible DNA binding site for BenM was identified between the two coding regions. Two mutations in the predicted operator/promoter region rendered ben gene expression either constitutive or inducible by cis,cis-muconate but not benzoate. Mutants lacking BenM, CatM, or both of these regulators degraded aromatic compounds at different rates, and the levels of intermediary metabolites that accumulated depended on the genetic background. These studies indicated that BenM is necessary for ben gene expression but not for expression of the cat genes, which can be regulated by CatM. In a catM-disrupted strain, BenM was able to induce higher levels of catA expression than catB expression.

Acinetobacter↗

benK encodes a hydrophobic permease-like protein involved in benzoate degradation by Acinetobacter sp. strain ADP1.

The chromosomal benK gene was identified within a supraoperonic gene cluster involved in benzoate degradation by Acinetobacter sp. strain ADP1, and benK was expressed in response to a benzoate metabolite, cis,cis-muconate. The disruption of benK reduced benzoate uptake and impaired the use of benzoate or benzaldehyde as the carbon source. BenK was homologous to several aromatic compound transporters.

Acinetobacter↗

Isotopic composition of inorganic carbon as an indicator of benzoate degradation by pseudomonas putida: temperature, growth rate and pH effects.

Degradation experiments of benzoate by Pseudomonas putida resulted in enzymatic carbon isotope fractionations. However, isotopic temperature effects between experiments at 20 and 30 degrees C were minor. Averages of the last three values of the CO(2) isotopic composition (delta(13)C(CO2(g))) were more negative than the initial benzoate delta(13)C value (-26.2 per thousand Vienna Pee Dee Belenite (VPDB)) by 3.8, 3.4 and 3.2 per thousand at 20, 25 and 30 degrees C, respectively. Although the maximum isotopic temperature difference found was only 0.6 per thousand, more extreme temperature variations may cause larger isotope effects. In order to understand the isotope effects on the total inorganic carbon (TIC), a better measure is to calculate the proportions of the inorganic carbon species (CO(2)(g), CO(2)(aq) and HCO(3)(-)) and to determine their cumulative delta(13)C(TIC). In all three experiments delta(13)C(TIC) was more positive than the initial isotopic composition of the benzoate at a pH of 7. This suggests an uptake of (12)C in the biomass in order to match the carbon balance of these closed system experiments.

Benzoates↗

2-Ketocyclohexanecarboxyl coenzyme A hydrolase, the ring cleavage enzyme required for anaerobic benzoate degradation by Rhodopseudomonas palustris.

2-Ketocyclohexanecarboxyl coenzyme A (2-ketochc-CoA) hydrolase has been proposed to catalyze an unusual hydrolytic ring cleavage reaction as the last unique step in the pathway of anaerobic benzoate degradation by bacteria. This enzyme was purified from the phototrophic bacterium Rhodopseudomonas palustris by sequential Q-Sepharose, phenyl-Sepharose, gel filtration, and hydroxyapatite chromatography. The sequence of the 25 N-terminal amino acids of the purified hydrolase was identical to the deduced amino acid sequence of the badI gene, which is located in a cluster of genes involved in anaerobic degradation of aromatic acids. The deduced amino acid sequence of badI indicates that 2-ketochc-CoA hydrolase is a member of the crotonase superfamily of proteins. Purified BadI had a molecular mass of 35 kDa as determined by sodium dodecyl sulfate-polyacrylamide gel electrophoresis and a native molecular mass of 134 kDa as determined by gel filtration. This indicates that the native form of the enzyme is a homotetramer. The purified enzyme was insensitive to oxygen and catalyzed the hydration of 2-ketochc-CoA to yield pimelyl-CoA with a specific activity of 9.7 micromol min(-1) mg of protein(-1). Immunoblot analysis using polyclonal antiserum raised against the purified hydrolase showed that the synthesis of BadI is induced by growth on benzoate and other proposed benzoate pathway intermediates but not by growth on pimelate or succinate. An R. palustris mutant, carrying a chromosomal disruption of badI, did not grow with benzoate and other proposed benzoate pathway intermediates but had wild-type doubling times on pimelate and succinate. These data demonstrate that BadI, the 2-ketochc-CoA hydrolase, is essential for anaerobic benzoate metabolism by R. palustris.

Acyl Coenzyme A↗

Flux limitations in the ortho pathway of benzoate degradation of Alcaligenes eutrophus: metabolite overflow and induction of the meta pathway at high substrate concentrations.

The growth behaviour of Alcaligenes eutrophus using various concentrations of benzoate was investigated. In batch culture, growth was exponential and growth rate (mu) and yields (Y) were high [mu = 0.51 h-1 and Yx/benzoate = 0.56 mol carbon (mol carbon)-1] when low concentrations of benzoate (< 5 mM) were used. These kinetic parameters were close to the maxima determined in a benzoate-limited chemostat [mu(max) = 0.55 h-1 and YX/benzoatemax = 0.57 mol carbon (mol carbon)-1] and the part of the energy for maintenance was limited (mATP = 4.3 +/- 2.2 mmol ATP g-1 h-1). When higher concentrations of benzoate were used (up to 40 mM), several metabolic limitations appeared. The specific rate of benzoate consumption was not altered, whereas growth was inhibited [Ki(benzoate) approximately 27 mM]. Furthermore, high concentrations of catechol together with some 1,2-dihydro-1,2-dihydroxybenzoate (DHB) transiently accumulated in the medium. The accumulation of catechol was attributed to limiting flux through catechol 1,2-dioxygenase estimated to be 5.2 mmol g-1 h-1, whereas that of DHB was provoked by an imbalance in the NADH/NAD+ intracellular content. The direct consequence of DHB accumulation was the induction of the meta pathway for the degradation of catechol, and this pathway contributed up to 20% of the total flux of catechol to the central metabolism. Finally, when very high concentrations of benzoate were used (55 mM), both growth and the specific rate of benzoate degradation were diminished due to a strong decrease in benzoate 1,2-dioxygenase specific activity.

Adenosine Triphosphate↗

Cloning and expression in Escherichia coli of Acinetobacter calcoaceticus genes for benzoate degradation.

The catabolic genes necessary for the conversion of benzoate to catechol have been cloned from Acinetobacter calcoaceticus into Escherichia coli. The cloned genes, benABCD, encoded both a benzoate 1,2-dioxygenase system, composed of NADH-cytochrome c reductase and terminal oxygenase components, and a cis-diol dehydrogenase. The dioxygenase system appears to be encoded by three genes, benABC, whose products, 53-, 19-, and 38-kilodalton proteins, correspond in size to those of components in other bacterial dioxygenases. The cloned dioxygenase system is expressed at high level in E. coli, enabling the conversion of benzoate to a cis-diol, 2-hydro-1,2-dihydroxybenzoate, at a rate comparable to that of fully induced A. calcoaceticus cultures. A cis-diol dehydrogenase, the product of the A. calcoaceticus benD gene, when present in E. coli enables this organism to convert the cis-diol intermediate to catechol. The dehydrogenase has been partially purified and is a dimer with two identical 31-kilodalton subunits. The ben genes are clustered on the A. calcoaceticus chromosome with independently regulated genes needed for the dissimilation of catechol. In a 16-kilobase-pair region of the chromosome there are 10 genes for benzoate catabolism, organized in no fewer than three transcriptional units. This kind of arrangement, termed supraoperonic clustering, has been observed previously in pseudomonads.

Acinetobacter↗