Influence of chroline substitution pattern on the degradation of polychlorinated biphenyls by eight bacterial strains

We compared the metabolism of eight di- and trichlorobiphenyls by eight bacterial strains chosen to represent a broad range of degradative activity against polychlorinated biphenyls (PCBs). The PCB congeners used were 2,3-, 2,3′-, 2,4′-, 3,3′-, 2,3,3′-, 2,4,4′-, 2,5,3′-, and 3,4,2′-chlorobiphenyl. The bacterial strains used wereCorynebacterium sp. MB1,Alcaligenes strainsA. eutrophus H850 andA. faecalis Pi434, andPseudomonas strains LB400 and H1130,P. testosteroni H430 and H336, andP. cepacia H201. The results indicated that both the relative rates of primary degradation of PCBs and the choice of the ring attacked were dependent on the bacterial strain used. The bacterial strains exhibited considerable differences in their relative reactivity preferences for attack on mono- and dichlorophenyl groups and in the degree to which the attack was affected by the chlorine substitution pattern on the nonreacting ring. For MB1 the reactivity pattern was 3-≥4-≫2-chlorophenyl with no attack on 2,4- or 2,5-chlorophenyl groups. This strain was relatively insensitive to the chlorine substitution pattern on the nonreacting ring. Strains H1130, H430, H201, and Pi434 exhibited the same reactivity preferences as MB1, but for these strains (and for all others tested) the chlorination pattern on the nonreacting ring had a strong effect. For strain H336 the reactivity preference was 4-≥2->2,4-≥3-chlorophenyl, with no evidence of attack on 2,5-chlorophenyl rings. For strains H850 and LB400 the relative reactivity was 2->2,5->3-≫2,4->4-chlorophenyl. On this basis we propose that the eight bacterial strains represent four distinct classes of biphenyl/PCB-dioxygenase activity. The types of products formed were largely strain-independent and were determined primarily by the chlorine substitution pattern on the reacting ring. When the reacting ring was an unsubstituted phenyl or a 2-chlorophenyl group, the products were chlorobenzoic acids in high yields; for a 3-chlorophenyl ring, both chlorobenzoic acids and chloroacetophenones in moderate yields; and for a 4- or 2,4-chlorophenyl group, chlorobenzoic acids in low yields with an apparent accumulation ofmeta ring-fission product. Strains H850 and LB400 were able to degrade the 3-chlorobenzoic acid that they produced from the degradation of 2,3′-chlorobiphenyl. We conclude that despite differences among strains in the specificity of the initial dioxygenase, the specificities of the enzymes responsible for the subsequent degradation to chlorobenzoic acid and/or chloroacetophenone are quite similar for all strains.     

Growth on dichlorobiphenyls with chlorine substitution on each ring by bacteria isolated from contaminated African soils

Until recently, it was generally believed that the presence of more than one chlorine substituent prevented chlorinated biphenyls from serving as a sole source of carbon and energy for aerobic bacteria. In this study, we report the isolation of three aerobic strains, identified as Enterobacter sp. SA-2, Ralstonia sp. SA-4, and Pseudomonas sp. SA-6 from Nigerian polluted soils, that were able to grow on a wide range of dichlorobiphenyls (diCBs). In addition to growing on all monochlorobiphenyls (monoCBs), the strains were all able to utilize 2,2′-, 2,4′-, and 2,3-diCB as a sole source of carbon and energy. With the exception of strain SA-2, growth was also sustainable on 3,3′-, and 3,5-diCB. Washed benzoate-grown cells were typically able to degrade 68 to 100% of the diCB (100 ppm) within 188 h, concomitant with a cell number increase of up to three orders-of-magnitude and elimination of varying amounts of chloride. In many cases, stoichiometric production of a chlorobenzoate (CBA) as a product was observed. During growth on 2,2′-, and 2,4′-diCB, organisms exclusively attacked an o-chlorinated ring resulting in the production of 2-CBA and 4-CBA, respectively. A gradual decline in the concentration of the latter was observed, which suggested that the product was being degraded further. In the case of 2,3-diCB, the unsubstituted ring was preferentially metabolized. Initial diCB degradation rates were greatest for 2,4′-diCB (11.2 ± 0.91 to 30.3 ± 7.8 nmol/min per 10⁹ cells) and lowest for 2,2′-diCB (0.37 ± 0.12 to 2.7 ± 1.2 nmol/min per 10⁹ cells).     

Effect of surfactant solubilization on biodegradation of polychlorinated biphenyl congeners by Pseudomonas LB400

A variety of commercial surfactants were tested to determine their effect on polychlorinated biphenyl (PCB) transformation by Pseudomonas LB400. Initial tests determined that most surfactants were fully or partially able to solubilize the PCB congeners 2,5,2′-chlorobiphenyl (CBP), 2,4,2′,4′-CBP, 2,3,5,2′,5′-CBP and 2,4,5,2′,4′,5′-CBP, at concentrations above the surfactants' critical micelle concentration (CMC). Surfactants were also found to have no negative effect on bacterial survival, as cell numbers were the same or higher after incubation in the presence of surfactants than after incubation without surfactants. A comparison of the extent of biotransformation of single PCB congeners by the bacterium revealed that, at surfactant concentrations above the CMC, the presence of an anionic surfactant promoted while nonionic surfactants inhibited PCB transformation, compared to a control with no surfactant. The rates of transformation of PCB congeners were also higher in the presence of the anionic surfactant compared to the control. The inhibitory effects of a nonionic surfactant, Igepal CO-630 at a concentration above its CMC, on transformation of 2,4,5,2′,5′-CBP could be eliminated by diluting the surfactant/PCB solution to a concentration close to the surfactant CMC. Received: 26 October 1998 / Received revision: 5 March 1999 / Accepted: 14 March 1999     

Mineralization of PCBs by the genetically modified strain Cupriavidus necator JMS34 and its application for bioremediation of PCBs in soil

Polychlorobiphenyls (PCBs) are classified as “high-priority pollutants.” Diverse microorganisms are able to degrade PCBs. However, bacterial degradation of PCBs is generally incomplete, leading to the accumulation of chlorobenzoates (CBAs) as dead-end metabolites. To obtain a microorganism able to mineralize PCB congeners, the bph locus of Burkholderia xenovorans LB400, which encodes one of the most effective PCB degradation pathways, was incorporated into the genome of the CBA-degrading bacterium Cupriavidus necator JMP134-X3. The bph genes were transferred into strain JMP134-X3, using the mini-Tn5 transposon system and biparental mating. The genetically modified derivative, C. necator strain JMS34, had only one chromosomal insertion of bph locus, which was stable under nonselective conditions. This modified bacterium was able to grow on biphenyl, 3-CBA and 4-CBA, and degraded 3,5-CBA in the presence of m-toluate. The strain JMS34 mineralized 3-CB, 4-CB, 2,4′-CB, and 3,5-CB, without accumulation of CBAs. Bioaugmentation of PCB-polluted soils with C. necator strain JMS34 and with the native B. xenovorans LB400 was monitored. It is noteworthy that strain JMS34 degraded, in 1 week, 99% of 3-CB and 4-CB and approximately 80% of 2,4′-CB in nonsterile soil, as well as in sterile soil. Additionally, the bacterial count of strain JMS34 increased by almost two orders of magnitude in PCB-polluted nonsterile soil. In contrast, the presence of native microflora reduced the degradation of these PCBs by strain LB400 from 73% (sterile soil) to approximately 50% (nonsterile soil). This study contributes to the development of improved biocatalysts for remediation of PCB-contaminated environments.     

Simultaneous degradation of chloro- and methyl-substituted aromatic compounds: competition between Pseudomonas strains using the ortho and meta pathway or the ortho pathway exclusively

Pseudomonas sp. D7-4 and Pseudomonas sp. B13 FR1(pFRC20P) degraded mixtures of chloro- and methyl-substituted benzoates exclusively via an extended ortho pathway, whereas in Pseudomonas putida WR201 both ortho and meta fission were induced by mixtures of 3-chloro- and 3-methylbenzoate or even by 3-chlorobenzoate alone. The competition behaviour of these strains was compared in batch and in chemostat cultures. Despite misrouting of metabolites, strain WR201 was competitive, in a lot of the competition experiments, with mixtures of these substrates. Only in a narrow range of the mixing ratio of chloro- and methylbenzoate was the presence of both the meta and ortho pathways a disadvantage for competitiveness. Outside these ranges other attributes, such as high growth rates or short lag periods, of a respective strain were even more essential for one strain to outcompete another. Received: 13 February 1998 / Received revision: 28 April 1998 / Accepted: 30 April 1998     

Microbial Growth on Dichlorobiphenyls Chlorinated on Both Rings as a Sole Carbon and Energy Source

We have isolated bacterial strains capable of aerobic growth on ortho-substituted dichlorobiphenyls as sole carbon and energy sources. During growth on 2,2′-dichlorobiphenyl and 2,4′-dichlorobiphenyl strain SK-4 produced stoichiometric amounts of 2-chlorobenzoate and 4-chlorobenzoate, respectively. Chlorobenzoates were not produced when strain SK-3 was grown on 2,4′-dichlorobiphenyl.     

Gratuitous dechlorination of chloroethanes by methanogenic granular sludge

The dechlorinating activity of a methanogenic granular sludge from a methanol-fed upflow anaerobic sludge blanket reactor was investigated with chlorinated ethanes. This unadapted methanogenic consortium degraded all chloroethanes tested. The product formation rates decreased with the number of chlorine substituents. The more highly chlorinated ethanes were also converted, although at a lower rate, in the presence of autoclaved (dead) sludge, indicating the involvement of reduced heat-stable cofactors like vitamin B₁₂ and F₄₃₀. Direct chemical dechlorination of hexa-, penta- and tetrachloroethanes was also observed in medium without sludge, although at a much lower rate. The results show the importance of cometabolic and abiotic (chemical) conversions for the transformation of chlorinated ethanes by the methanogenic consortium. The types of reaction and the products formed were correlated with the Gibbs free-energy change (ΔG ^0′). Reductive hydrogenolysis and dichloroelimination were important dechlorinating mechanisms. Generally, these reactions have a higher ΔG ^0′ value than dehydrochlorination reactions, which occurred less frequently during the transformation of chloroethanes by the methanogenic granular sludge. Received: 8 June 1998 / Received revision: 7 September 1998 / Accepted: 13 September 1998     

Active-site engineering of biphenyl dioxygenase: effect of substituted amino acids on substrate specificity and regiospecificity

Biphenyl dioxygenase (Bph Dox) catalyzes the initial dioxygenation step in the metabolism of biphenyl. The large subunit (BphA1) of Bph Dox plays a crucial role in the determination of the substrate specificity of biphenyl-related compounds including polychlorinated biphenyls (PCBs). Previously, the substitution of Asn at Thr-376 near the active-site iron in the BphA1 of Pseudomonas pseudoalcaligenes KF707 expanded the oxidation range and altered the regiospecificity of Bph Dox for PCBs. In this study, we replaced Thr-376 with Gly, Ser, Gln, Tyr, Val, Phe, Asp, and Lys and expressed these enzymes in Escherichia coli. Bph Dox mutants of Thr376Asn, Thr376Val, Thr376Phe, and Thr376Lys showed novel degradation activity for dibenzofuran, which is a poor substrate for KF707 Bph Dox. All active Bph Dox mutants showed altered regiospecificity with 2,2′-dichlorobiphenyl and 2,5,4′-trichlorobiphenyl. The Thr376Gly, Thr376Val, Thr376Phe, and Thr376Asp Bph Dox mutants introduced molecular oxygen at the 2,3 position of 2,2′-dichlorobiphenyl, forming 2-chloro-2′,3′-dihydroxybiphenyl with concomitant dechlorination. The Bph Dox mutants of Thr376Gly, Thr376Ser, Thr376Asp, and Thr376Lys attacked 2,5,4′-trichlorobiphenyl via both 2′,3′- and 3,4-dioxygenation activities. In particular, the Thr376Phe Bph Dox mutant exhibited enhanced and expanded degradation activities toward all of the compounds tested. Further site-directed mutation was induced to change the oxidizing character of KF707 Bph Dox to that of the Bph Dox of Burkholderia xenovorans LB400 by the substitution of two amino acids, Ile335Phe and Thr376Asn, near the active-site.Electronic supplementary material Supplementary material is available in the online version of this article at .     

Aerobic mineralization of 4,4′-dichlorobiphenyl and 4-chlorobenzoic acid by a novel natural bacterial strain that grows poorly on benzoate and biphenyl

Achromobacter xylosoxidans strain IR08 was isolated from soil contaminated with electrical transformer fluid by enrichment culture containing Aroclor 1221 as the sole carbon source. This strain was found to grow on all monochlorobiphenyls, 4,4′-dichlorobiphenyl (4,4′-diCB) and a wide range of other xenobiotic compounds. During growth on 4,4′-diCB, a near-stoichiometric amount of chloride was excreted into the culture fluid in less than 5 days and growth yield was more than twice that achieved on biphenyl. The production of 4-CBA or chlorocatechol as a metabolite was not observed. Quite unusually, coincubation of strain IR08 with 4,4′-diCB and biphenyl at relatively equal concentrations showed preferential utilization of the chlorobiphenyl: 4,4′-diCB was mineralized in less than 5 days concomitant with stoichiometric release of chloride, while biphenyl was poorly degraded. Growth on 2.5 mM CBA also resulted in complete disappearance of the substrate, however, inorganic chloride recovered from the culture broth was less than 65%. The isolation of a dichlorobiphenyl-mineralizing rather than transformation strain such as IR08 is an important advance in an effort to develop effective bioremediation strategy for polychlorinated biphenyl-contaminated soil.     

Cometabolic Degradation of Polychlorinated Biphenyls at Low Temperature by Psychrotolerant Bacterium Hydrogenophaga sp. IA3-A

A biphenyl-utilizing bacterium isolated from polychlorinated biphenyls (PCBs)-contaminated soils grew on tryptic soy at temperatures between 4 and 40°C. The Gram-negative rod bacterium formed yellow colonies on nutrient agar and it denitrified nitrate to nitrogen. Analysis of cellular fatty acids showed that it was most closely related to Hydrogenophaga taeniospiralis. At 5°C, biphenyl-grown cells cometabolically degraded di- and trichlorinated isomers of PCBs in 10 ppm of Aroclor 1248. At 30°C, PCBs that were removed included a congener with four chlorine substituents. At 5°C, cells transformed 2,4′-dichlorobiphenyl (2,4′-DCB) and accumulated ortho-chlorinated meta-cleavage product as a stable metabolite. Analysis of extracts of culture supernatant by gas chromatography–mass spectrometry indicated that products of transformation of 2,4′-DCB included 2- and 4-chlorobenzoic acid (2- and 4-CBA), suggesting that (chloro)biphenyl-degrading upper-pathway enzymes of the bacterium are active at low temperature. The bacterium Hydrogenophaga sp. IA3-A is a PCB-degrading psychrotolerant strain.     

Metabolism of Doubly para-Substituted Hydroxychlorobiphenyls by Bacterial Biphenyl Dioxygenases

In this work, we examined the profile of metabolites produced from the doubly para-substituted biphenyl analogs 4,4′-dihydroxybiphenyl, 4-hydroxy-4′-chlorobiphenyl, 3-hydroxy-4,4′-dichlorobiphenyl, and 3,3′-dihydroxy-4,4′-chlorobiphenyl by biphenyl-induced Pandoraea pnomenusa B356 and by its biphenyl dioxygenase (BPDO). 4-Hydroxy-4′-chlorobiphenyl was hydroxylated principally through a 2,3-dioxygenation of the hydroxylated ring to generate 2,3-dihydro-2,3,4-trihydroxy-4′-chlorobiphenyl and 3,4-dihydroxy-4′-chlorobiphenyl after the removal of water. The former was further oxidized by the biphenyl dioxygenase to produce ultimately 3,4,5-trihydroxy-4′-chlorobiphenyl, a dead-end metabolite. 3-Hydroxy-4,4′-dichlorobiphenyl was oxygenated on both rings. Hydroxylation of the nonhydroxylated ring generated 2,3,3′-trihydroxy-4′-chlorobiphenyl with concomitant dechlorination, and 2,3,3′-trihydroxy-4′-chlorobiphenyl was ultimately metabolized to 2-hydroxy-4-chlorobenzoate, but hydroxylation of the hydroxylated ring generated dead-end metabolites. 3,3′-Dihydroxy-4,4′-dichlorobiphenyl was principally metabolized through a 2,3-dioxygenation to generate 2,3-dihydro-2,3,3′-trihydroxy-4,4′-dichlorobiphenyl, which was ultimately converted to 3-hydroxy-4-chlorobenzoate. Similar metabolites were produced when the biphenyl dioxygenase of Burkholderia xenovorans LB400 was used to catalyze the reactions, except that for the three substrates used, the BPDO of LB400 was less efficient than that of B356, and unlike that of B356, it was unable to further oxidize the initial reaction products. Together the data show that BPDO oxidation of doubly para-substituted hydroxychlorobiphenyls may generate nonnegligible amounts of dead-end metabolites. Therefore, biphenyl dioxygenase could produce metabolites other than those expected, corresponding to dihydrodihydroxy metabolites from initial doubly para-substituted substrates. This finding shows that a clear picture of the fate of polychlorinated biphenyls in contaminated sites will require more insights into the bacterial metabolism of hydroxychlorobiphenyls and the chemistry of the dihydrodihydroxylated metabolites derived from them.     

Degradation of 2-chlorobenzoic and 2,5-dichlorobenzoic acids in pure culture byPseudomonas stutzeri

A strain ofPseudomonas stutzeri KS25 utilizing 2-chlorobenzoic and 2,5-dichlorobenzoic acids as the sole carbon and energy source was isolated from polychlorophenol-contaminated soil and sewage, using the method of enrichment cultures. This strain was also able to grow on 2-fluoro-, 2-iodo-, 2-bromo- and 2,5-dihydroxybenzoate, but did not utilize 3-, 4-chloro-, 2,4- and 2,6-dichlorobenzoates as the sole carbon and energy source, however, it cometabolized 3-chloro-, 2,4-and 2,6-dichlorobenzoates, but not 4-chlorobenzoate. The yield of released chlorine during utilization of 2-chloro- and 2,5-dichlorobenzoates amounted to 100 % of the theoretical. The concentration of 2-chloro- and 2,5-dichlorobenzoates, not substantially inhibiting the isolated microorganism, was within the range 0.25–0.5 and 2.5–3.0 g/L, respectively.     

Analysis of changes in congener selectivity during PCB degradation by Burkholderia sp. strain TSN101 with increasing concentrations of PCB and characterization of the bphBCD genes and gene products

We isolated and characterized a gram-negative bacterium, Burkholderia sp. strain TSN101, that can degrade polychlorinated biphenyls (PCBs) at concentrations as high as 150 μg Kaneclor 300/ml, a PCB mixture equivalent to Aroclor 1242. Growing cells of strain TSN101 degraded most of the tri- and tetrachlorobiphenyls in medium containing 25 μg Kaneclor 300/ml. Using PCB concentrations of 50–150 μg of Kaneclor 300/ml, the congener selectivity pattern was different and the pattern of chlorine substitution strongly affected degradation of some congeners. At 25 μg Kaneclor 300/ml, strain TSN101 degraded di- and trichlorinated congeners with chlorine substitutions at both the ortho and the para positions. At higher concentrations of Kaneclor 300, di- and trichlorobiphenyls with ortho substituents in both phenyl rings were not degraded well. Trichlorobiphenyls with para and meta substitutents were degraded equally well at all concentrations studied. The ability of strain TSN101 to degrade ortho and para-substituted congeners was confirmed using a defined PCB mixture with chlorine substituents at 2′- and 4′-positions. A 5-kb DNA fragment containing the bphBCD genes was cloned and sequenced. Comparison of the deduced amino acid sequences of these genes with related proteins indicated 99 and 98% sequence similarity to the BphB and BphD of Comamonas testosteroni strain B-356, respectively. The bphC gene product showed 74% sequence similarity to the BphC of Burkholderia cepacia strain LB400 and exhibited a narrow substrate specificity with strong affinity for 2,3-dihydroxybiphenyl. A bphC-disrupted mutant of Burkholderia sp. strain TSN101, constructed by gene replacement, lost the ability to utilize biphenyl, thus supporting the role of the cloned bph gene in biphenyl metabolism. Received: 18 February 1997 / Accepted: 19 August 1997     

Solvent production by Clostridium beijerinckii NRRL B592 growing on different potato media

Very good solvent formation rates were observed when Clostridium beijerinckii NRRL B592 was cultivated on different whole potato media. The increase in whole potato concentration contributed to the increased final solvent concentrations, while the addition of yeast extract or mineral salts gave negative effects. To obtain good solvent productivities and high final solvent concentrations during batch fermentation, no enzymatic hydrolysis of the potato starch was necessary, indicating high activity of the clostridial amylases produced by the strain applied. Received: 17 April 1998 / Received revision: 22 June 1998 / Accepted: 27 June 1998     

Screening and characterization of Lactobacillus strains producing large amounts of exopolysaccharides

A total of 182 Lactobacillus strains were screened for production of extracellular polysaccharides (EPS) by a new method: growth in liquid media with high sugar concentrations. Sixty EPS-positive strains were identified; 17 strains produced more than 100 mg/l soluble EPS. Sucrose was an excellent substrate for abundant EPS synthesis. The ability to produce glucans appears to be widespread in the genus Lactobacillus. The monosaccharide composition of EPS produced by Lactobacillus reuteri strain LB 121 varied with the growth conditions (solid compared to liquid medium) and the sugar substrates (sucrose or raffinose) supplied in the medium. Strain LB 121 produced both a glucan and a fructan on sucrose, but only a fructan on raffinose. This is the first report of fructan production by a Lactobacillus species. EPS production increased with increasing sucrose concentrations and involved extracellular sucrase-type enzymes. Received: 20 March 1998 / Received revision: 12 August 1998 / Accepted: 12 August 1998     

Biodegradation of the pesticide 4,6-dinitro-ortho-cresol by microorganisms in batch cultures and in fixed-bed column reactors

A mixed culture of microorganisms able to utilize 4,6-dinitro-ortho-cresol (DNOC) as the sole source of carbon, nitrogen and energy was isolated from soil contaminated with pesticides and from activated sludge. DNOC was decomposed aerobically in batch cultures as well as in fixed-bed column reactors. Between 65% and 84% of the substrate nitrogen was released as nitrate into the medium, and 61% of the carbon from uniformly ¹⁴C-labelled DNOC was recovered as ¹⁴CO₂. The mixed microbial culture also decomposed 4-nitrophenol and 2,4-dinitrophenol but not 2,3-dinitrophenol, 2,6-dinitrophenol, 2,4-dinitrotoluene, 2,4-dinitrobenzoic acid or 2-sec-butyl-4,6-dinitrophenol (Dinoseb). Maximal degradation rates for DNOC by the bacterial biofilm immobilized on glass beads in fixed-bed column reactors were 30 mmol day⁻¹ (l reactor volume)⁻¹, leaving an effluent concentration of less than 5 μg l⁻¹ DNOC in the outflowing medium. The apparent K _s value of the immobilized mixed culture for DNOC was 17 μM. Degradation was inhibited at DNOC concentrations above 30 μM and it ceased at 340 μM, possibly because of the uncoupling action of the nitroaromatic compound on the cellular energy-transducing mechanism. Received: 27 March 1997 / Received revision: 5 June 1997 / Accepted: 7 June 1997     

Involvement of the Terminal Oxygenase β Subunit in the Biphenyl Dioxygenase Reactivity Pattern toward Chlorobiphenyls

Biphenyl dioxygenase (BPH dox) oxidizes biphenyl on adjacent carbons to generate 2,3-dihydro-2,3-dihydroxybiphenyl in Comamonas testosteroni B-356 and in Pseudomonas sp. strain LB400. The enzyme comprises a two-subunit (α and β) iron sulfur protein (ISP_BPH), a ferredoxin (FER_BPH), and a ferredoxin reductase (RED_BPH). B-356 BPH dox preferentially catalyzes the oxidation of the double-meta-substituted congener 3,3′-dichlorobiphenyl over the double-para-substituted congener 4,4′-dichlorobiphenyl or the double-ortho-substituted congener 2,2′-dichlorobiphenyl. LB400 BPH dox shows a preference for 2,2′-dichlorobiphenyl, and in addition, unlike B-356 BPH dox, it can catalyze the oxidation of selected chlorobiphenyls such as 2,2′,5,5′-tetrachlorobiphenyl on adjacent meta-para carbons. In this work, we examine the reactivity pattern of BPH dox toward various chlorobiphenyls and its capacity to catalyze the meta-para dioxygenation of chimeric enzymes obtained by exchanging the ISP_BPH α or β subunit of strain B-356 for the corresponding subunit of strain LB400. These hybrid enzymes were purified by an affinity chromatography system as His-tagged proteins. Both types, the chimera with the α subunit of ISP_BPH of strain LB400 and the β subunit of ISP_BPH of strain B-356 (the α_LB400β_B-356 chimera) and the α_B-356β_LB400 chimera, were functional. Results with purified enzyme preparations showed for the first time that the ISP_BPH β subunit influences BPH dox’s reactivity pattern toward chlorobiphenyls. Thus, if the α subunit were the sole determinant of the enzyme reactivity pattern, the α_B-356β_LB400 chimera should have behaved like B-356 ISP_BPH; instead, its reactivity pattern toward the substrates tested was similar to that of LB400 ISP_BPH. On the other hand, the α_LB400β_B-356 chimera showed features of both B-356 and LB400 ISP_BPH where the enzyme was able to metabolize 2,2′- and 3,3′-dichlorobiphenyl and where it was able to catalyze the meta-para oxygenation of 2,2′,5,5′-tetrachlorobiphenyl.     

A Pseudomonas aeruginosa biosensor responds to exposure to ultraviolet radiation

We fused the Pseudomonas aeruginosa recA promoter to a promoterless Vibrio fisherilux operon. This recA–lux fusion (pMOE15) was introduced into wild-type P. aeruginosa strain FRD1 and recA expression was monitored by measuring 490-nm light production. The RM4440 strain responded to increasing doses of ultraviolet radiation by an increase in its bioluminescence. RM4440 has the potential to be useful as a biosensor for the presence of DNA-damaging agents in the environment. Received: 18 February 1998 / Received revision: 18 June 1998 / Accepted: 27 June 1998     

Substrate specificities of the chloromuconate cycloisomerases from Pseudomonas sp. B13, Ralstonia eutropha JMP134 and Pseudomonas sp. P51

The chloromuconate cycloisomerase of Pseudomonas sp. B13 was purified from 3-chlorobenzoate-grown wild-type cells while the chloromuconate cycloisomerases of Ralstonia eutropha JMP134 (pJP4) and Pseudomonas sp. P51 (pP51) were purified from Escherichia coli strains expressing the corresponding gene. Kinetic studies were performed with various chloro-, fluoro-, and methylsubstituted cis,cis-muconates. 2,4-Dichloro-cis,cis-muconate proved to be the best substrate for all three chloromuconate cycloisomerases. Of the three enzymes, TfdD of Ralstonia eutropha JMP134 (pJP4) was most specific, since its specificity constant for 2,4-dichloro-cis,cis-muconate was the highest, while the constants for cis,cis-muconate, 2-chloro- and 2,5-dichloro-cis,cis-muconate were especially poor. The sequence of ClcB of the 3-chlorobenzoate-utilizing strain Pseudomonas sp. B13 was determined and turned out to be identical to that of the corresponding enzyme of pAC27 (though slightly different from the published sequences). Corresponding to 2-chloro-cis,cis-muconate being a major metabolite of 3-chlorobenzoate degradation, the k _cat/K _m with 2-chloro-cis,cis-muconate was relatively high, while that with the still preferred substrate 2,4-dichloro-cis,cis-muconate was relatively low. This enzyme was thus the least specific and the least active among the three compared enzymes. TcbD of Pseudomonas sp. P51 (pP51) took an intermediate position with respect to both the degree of specificity and the activity with the preferred substrate. Received: 7 August 1998 / Received revision: 24 November 1998 / Accepted: 29 November 1998     

Investigation of substrate specificity of wildtype and mutant BphK (a glutathione S-transferase) from Burkholderia LB400

The bphK gene located in the bph operon of Burkholderia LB400 encodes a protein, BphK^LB400, with significant sequence similarity to glutathione-S-transferases (GST), a group of enzymes involved in the detoxification of many endobiotic and xenobiotic substances. Comparison of the amino acid sequence of BphK^LB400 with GST from other polychlorinated biphenyl (PCB)-degrading bacteria identified a number of highly conserved amino acids in the C-terminal region of the protein that may be associated with substrate specificity. In this study, two of these conserved amino acids in BphK^LB400 (amino acids 152 and 180) were selected for mutation, using site-directed mutagenesis, and substrate specificity assays. BphK^LB400 (wildtype and mutant) was over-expressed in Escherichia coli where the bphK gene (wildtype and mutant) is under the expression of a lac promoter and is induced by isopropyl thiogalactoside, and bacterial cell extracts were prepared for GST activity assays. Mutations at amino acids 152 and 180 were shown to affect GST activity of BphK^LB400 using 1-chloro-2,4-dinitrobenzene, the model substrate for GST activity assays; 4-chlorobenzoate and 3-chlorobenzoate, intermediates in the polychlorinated biphenyl (PCB) degradation pathway, and 2,4-dichlorophenoxyacetate and atrazine, commonly used herbicides; as substrates. A BphK^LB400 mutant (Ala180Pro) is identified in this study as having increased activity towards all substrates tested. This mutant may have potential in bioremediation.