Physiological studies on the oxidation of 3-chlorobenzoate by Acinetobacter calcoaceticus strain Bs 5

Summary Acinetobacter calcoaceticus, strain Bs 5, oxidized 3-chlorobenzoate only in the presence of a readily available energy source such as succinate or pyruvate. Cultures of the organism growing in the presence of 3-chlorobenzoate at concentrations greater than 250 M turned darkbrown on prolonged incubation. After centrifugation and acidificition of the supernatants to pH 2, a dark pigment could be precipitated. It was shown to contain bound chlorine and probably originated from 3-chlorocatechol and 4-chlorocatechol, which accumulated in cultures growing in the presence of 3-chlorobenzoate.3-Chlorobenzoate induced the ability to oxidize benzoate and catechol in the bacteria, the latter by orthofission. In the presence of an energy source, 3-chlorobenzoate-induced cells oxidized 3-chlorobenzoate at a rate, which was about 25% of the turnover rate for benzoate.In a continuous culture of the organism, growing in the presence of 1 mM 3-chlorobenzoate at a dilution rat of 0.025 h^–1, all culture parameters including the ability of the cells to oxidize benzoate, were oscillating. This oscillation was attributed to the transient build-up of toxic concentrations of chlorocatechols. 4-chlorocatechol was shown to be about six times more toxic than 3-chlorobenzoate. In another series of continuous culture experiments, 3-chlorobenzoate induced the synthesis of the benzoate oxidizing enzyme system of A. calcoaceticus strain Bs 5 at a concentration of 2.5 M, but appeared to lose its inducing potential towards this enzyme system at about 0.5 M.     

Microbial sensors for determination of aromatics and their chloroderivatives I. Determination of 3-chlorobenzoate using a Pseudomonas-containing biosensor

Summary An amperometric biosensor for the determination of benzoate and 3-chlorobenzoate using Pseudomonas has been developed. The influence of preincubation of the biosensor with desired substrates on sensitivity and specificity was investigated. The Pseudomonas sensor was more sensitive to benzoate and 3-chlorobenzoate than to 2- and 4-chloro-, 2,4-dichlorobenzoate and 2,4-dichlorophenol. Incubation of the sensor with benzoate and 3-chlorobenzoate enhanced the activity of the microbial sensor. Other chlorobenzoates tested caused a decrease of sensitivity. A linear relationship between the current range and the concentration of benzoate was observed up to 160 mol/l. In the case of 3-chlorobenzoate a linear relationship was observed for concentrations up to 200 mol/l. The signal is reproducible within 5.5% when the test solution contains 40 mol/l of 3-chlorobenzoate. Offprint requests to: K. Riedel     

The metabolism of halogen-substituted benzoic acids by Pseudomonas fluorescens

1. Washed suspensions of Pseudomonas fluorescens, grown with benzoate as sole carbon source, oxidize monohalogenobenzoates in the following descending order of effectiveness: benzoate, fluorobenzoates, chlorobenzoates, bromobenzoates, iodobenzoates. 2. Cells grown on asparagine oxidize benzoate after an adaptive period of 90–120min. This adaptive period is increased by halogenobenzoates in the following approximate descending order of effectiveness: chlorobenzoates, fluorobenzoates (=bromobenzoates), iodobenzoates. This inhibition of adaptation by halogeno analogues depends on the concentration of benzoate and is thus apparently competitive. 3. Cells do not adapt to oxidize the halobenzoates when the halogeno analogues are inducers. However, the fluorobenzoates reduce the lag period taken to form the benzoate-oxidizing system. 4. The halogenobenzoates inhibit adaptation to citrate and nicotinate but not so effectively as benzoate itself. This is presumably a `diauxic' effect. The analogues do not inhibit adaptation to catechol. 5. The halogenobenzoates are not used as sole carbon source for growth nor do they increase growth when cells grow with asparagine as the main carbon source. 6. It is suggested that this inability to use the analogues for growth is due partly to inability of the cells to liberate the halogen and to carry the oxidation to a stage at which carbon may be assimilated and partly to the inhibition of the induction of the oxidizing enzymes.     

Degradation of mono-, di-, and trihalogenated benzoic acids by Pseudomonas aeruginosa JB2

Pseudomonas aeruginosa JB2 was isolated from a polychlorinated biphenyl-contaminated soil by enrichment culture containing 2-chlorobenzoate as the sole carbon source. Strain JB2 was subsequently found also to grow on 3-chlorobenzoate, 2,3- and 2,5-dichlorobenzoates, 2,3,5-trichlorobenzoate, and a wide range of other mono- and dihalogenated benzoic acids. Cometabolism of 2,4-dichlorobenzoate was also observed. Chlorocatechols were the central intermediates of all chlorobenzoate catabolic pathways. Degradation of 2-chlorobenzoate was routed through 3-chlorocatechol, whereas 4-chlorocatechol was identified from the metabolism of both 2,3- and 2,5-dichlorobenzoate. The initial attack on chlorobenzoates was oxygen dependent and most likely mediated by dioxygenases. Although plasmids were not detected in strain JB2, spontaneous mutants were detected in 70% of glycerol-grown colonies. The mutants were all of the following phenotype: benzoate+, 3-chlorobenzoate+, 2-chlorobenzoate-, 2,3-dichlorobenzoate-, 2,5-dichlorobenzoate-. While chlorocatechols were oxidized by the mutants at wild-type levels, oxidation of 2-chloro- and 2,3- and 2,5-dichlorobenzoates was substantially diminished. These findings suggested that strain JB2 possessed, in addition to the benzoate dioxygenase, a halobenzoate dioxygenase that was necessary for the degradation of chlorobenzoates substituted in the ortho position.     

Degradation of mono-, di-, and trihalogenated benzoic acids by Pseudomonas aeruginosa JB2.

Pseudomonas aeruginosa JB2 was isolated from a polychlorinated biphenyl-contaminated soil by enrichment culture containing 2-chlorobenzoate as the sole carbon source. Strain JB2 was subsequently found also to grow on 3-chlorobenzoate, 2,3- and 2,5-dichlorobenzoates, 2,3,5-trichlorobenzoate, and a wide range of other mono- and dihalogenated benzoic acids. Cometabolism of 2,4-dichlorobenzoate was also observed. Chlorocatechols were the central intermediates of all chlorobenzoate catabolic pathways. Degradation of 2-chlorobenzoate was routed through 3-chlorocatechol, whereas 4-chlorocatechol was identified from the metabolism of both 2,3- and 2,5-dichlorobenzoate. The initial attack on chlorobenzoates was oxygen dependent and most likely mediated by dioxygenases. Although plasmids were not detected in strain JB2, spontaneous mutants were detected in 70% of glycerol-grown colonies. The mutants were all of the following phenotype: benzoate+, 3-chlorobenzoate+, 2-chlorobenzoate-, 2,3-dichlorobenzoate-, 2,5-dichlorobenzoate-. While chlorocatechols were oxidized by the mutants at wild-type levels, oxidation of 2-chloro- and 2,3- and 2,5-dichlorobenzoates was substantially diminished. These findings suggested that strain JB2 possessed, in addition to the benzoate dioxygenase, a halobenzoate dioxygenase that was necessary for the degradation of chlorobenzoates substituted in the ortho position.     

Diversity of anaerobic microbial processes in chlorobenzoate degradation: Nitrate,iron, sulfate and carbonate as electron acceptors

 The utilization of monochlorobenzoate isomers (2-, 3- and 4-chlorobenzoate) by anaerobic microbial consortia in River Nile sediments was systematically evaluated under denitrifying, Fe-reducing, sulfidogenic and methanogenic conditions. Loss of all three chlorobenzoates was noted in denitrifying cultures; furthermore, the initial utilization of chlorobenzoates was fastest under denitrifying conditions. Loss of 3-chlorobenzoate was seen under all four reducing conditions and the degradation of chlorobenzoates was coupled stoichiometrically to NO^- ₃ loss, Fe²⁺ production, SO^2- ₄ loss or CH₄ production, indicating that the chlorobenzoates were oxidized to CO₂. To our knowledge, this is the first observation of halogenated aromatic degradation coupled to Fe reduction. Received: 29 July 1994/Received revision: 22 November 1994/Accepted 16 December 1994     

Biodegradation and chemotaxis of polychlorinated biphenyls,biphenyls, and their metabolites by <Emphasis Type="Italic">Rhodococcus</Emphasis> spp.

Two biphenyl-degrading bacterial strains, SS1 and SS2, were isolated from polychlorinated biphenyl (PCB)-contaminated soil. They were identified as Rhodococcus ruber and Rhodococcus pyridinivorans based on the 16S rRNA gene sequence, as well as morphological, physiological and biochemical characteristics. SS1 and SS2 exhibited tolerance to 2000 and 3000 mg/L of biphenyl. And they could degrade 83.2 and 71.5% of 1300 mg/L biphenyl within 84 h, respectively. In the case of low-chlorinated PCB congeners, benzoate and 3-chlorobenzoate, the degradation activities of SS1 and SS2 were also significant. In addition, these two strains exhibited chemotactic response toward TCA-cycle intermediates, benzoate, biphenyl and 2-chlorobenzoate. This study indicated that, like the flagellated bacteria, non-flagellated Rhodococcus spp. might actively seek substrates through the process of chemotaxis once the substrates are depleted in their surroundings. Together, these data provide supporting evidence that SS1 and SS2 might be good candidates for restoring biphenyl/PCB-polluted environments.     

Isolation and characterization of a 3-chlorobenzoate degrading pseudomonad

A pseudomonad has been isolated from sewage, which can utilize 3-chlorobenzoic acid as a sole carbon source. In cells grown on benzoate the enzymes of the -ketoadipic acid pathway are present. Considerable enzymic activities for chlorinated substrates were found in benzoate grown cells only for the oxygenation of 3-chlorobenzoate and the dehydrogenation of 3- and 5-chloro-3,5-cyclohexadiene-1,2-diol-1-carboxylic acid. 3-Chlorobenzoate grown cells show additional high activities for the turnover of 3- and 4-chlorocatechols and chloromuconic acids.Abbreviations Used DHB (-)-3,5-cyclohexadiene-1,2-diol-1-carboxylic acid (derived from the trivial name, dihydrodihydroxybenzoate) - 3- and 5-Cl-DHB correspondingly 3- and 5-chloro-3,5-cyclohexadiene-1,2-diol-1-carboxylic acid     

Chlorobenzoate catabolism and interactions between Alcaligenes and Pseudomonas species from Bloody Run Creek

A mixed community of bacteria from surface runoff waters of the Hyde Park industrial landfill was enriched on 3-chlorobenzoate. Alcaligenes and Pseudomonas species were dominant in the community. Alcaligenes sp. BR60 carried an unstable plasmid specifying 3-chlorobenzoate catabolism. Metabolites detected in culture supernatants included chlorocatechol and chloro-cis,cis-muconic acid. Oxygen uptake in the presence of 3- and 4-substituted methyl-catechols revealed a catechol-1,2-oxygenase activity specific for substituted catechols with very limited activity for catechol. The isolate grew very slowly on benzoate. Alcaligenes sp. BR60 was isolated in co-culture with Pseudomonas fluorescens NR52. The latter contained no detectable plasmids and did not grow on benzoate or any of the chlorobenzoates in pure culture. Growth of the co-culture in Bloody Run Creek water supplemented with 3-chlorobenzoate indicated that phosphate concentrations in the water severely limited biodegradation. Under phosphate limited conditions in continuous culture, Pseudomonas fluorescens NR52 effectively scavenged available phosphate when it was present at a ratio of 1 cell to 20 of Alcaligenes sp. BR60. Under these conditions the growth of Alcaligenes sp. BR60 on 3-chlorobenzoate was reduced 5 fold, the frequency of plasmid deletion mutants increased, and 96% of the contaminant remained in the outflow in the form of the starting material or metabolites. No evidence was found for conjugation of the plasmid determining chlorobenzoate catabolism in Alcaligenes sp. BR60 to P. fluorescens NR52.Abbreviations 3 and 4 Cba chlorobenzoic acid isomers and growth phenotypes - Ba benzoic acid     

Erythematous Reaction to Ultraviolet Radiation and its Dynamics in Treatment Of Patients with Various Forms of Depression

We know that biological reactions depend not only upon the nature of the stimulus inducing them, but also upon the functional state of the organism as a whole and of the nervous system in particular. Therefore, in mental diseases a change occurs in a number of biological reactions, particularly white blood cell reactions, in response to antigenic stimuli (1) and to acupuncture. (2) Plesso (3) established the fact of considerable reduction of erythematous reaction to ultraviolet irradiation in schizophrenics, while Strakhov (4) studied photoerythema in a group of manic depressives and found that their's was a distinctive reaction.     

Strain DCB-1 conserves energy for growth from reductive dechlorination coupled to formate oxidation

Strain DCB-1 is a strict anaerobe capable of the reductive dechlorination of chlorobenzoates. The effect of dechlorination on the yield of pure cultures of DCB-1 was tested. Cultures were incubated with formate or H₂ as electron donors and CO₂ as a putative carbon source. Relative to control cultures with benzoate, cultures which dechlorinated 3-chlorobenzoate and 3,5-dichlorobenzoate had higher yields measured both as protein and cell density. On the media tested the apparent growth yield was 1.7 to 3.4 g cell protein per mole Cl^- removed. Dechlorination also stimulated formate oxidation by growing cultures. Resuspended cells required an electron donor for dechlorination activity, with either formate or elemental iron serving this function. Resuspended cells did not require an electron acceptor for formate consumption, but reductive dechlorination of 3CB to benzoate stoichiometrically stimulated oxidation of formate to CO₂. These results indicate that DCB-1 conserves energy for growth by coupling formate, and probably, H₂ oxidation to reductive dechlorination.Non-standard abbreviations 3CB 3-chlorobenzoate - 35DCB 3,5-dichlorobenzoate - PCF Propionibacterium sp. culture fluid     

Growth yield increase linked to reductive dechlorination in a defined 3-chlorobenzoate degrading methanogenic coculture

The microbially mediated reductive dehalogenation of aromatic compounds is potentially important in removal of chlorinated aromatic compounds from the environment. Thermodynamic data are presented which show that the reductive dechlorination of 3-chlorobenzoate to benzoate is exergonic, which led to the hypothesis that reductive elimination of chlorine from 3-chlorobenzoate yields biologically useful energy. In the present paper this hypothesis is tested. Experimental data were obtained with a defined 3-chlorobenzoate degrading methanogenic consortium. These data showed that (i) the molar growth yield of a defined 3-chlorobenzoate degrading consortium increased from 4.9 g protein per mol benzoate metabolized to 6.8 g protein per mol 3-chlorobenzoate when 3-chlorobenzoate replaced benzoate as energy source, and that (ii) the ATP level in starved consortium cells was twice as high when the cells were fed 3-chlorobenzoate than when fed benzoate. These observations show that the electrochemical potential between the redox partners of the H⁺/H₂ (electron-donating) and 3-chlorobenzoate/benzoate (electron-accepting) couples is a potential source of energy and are consistent with the hypothesis that reductive dechlorination of aromatic compounds is coupled to a novel type of microbial chemotrophy.     

Induction of enzymes of phytoalexin synthesis in cultured soybean cells by an elicitor from Phytophthora megasperma f. sp. glycinea

The glucan elicitor from cell walls of the fungal pathogen, Phytophthora megasperma f. sp. glycinea, induced rapid but transient increases in enzyme activities of general phenylpropanoid metabolism (phenylalanine ammonia-lyase and 4-coumarate: CoA ligase) and of the flavonoid pathway (chalcone synthase) in cell suspension cultures of soybean (Glycine max). After transferring cells into fresh medium, two peaks of inducibility for the enzymes by elicitor were observed, one shortly after transfer (stage I), and one at the end of the linear growth phase (stage II). Only one of the two isoenzymes of 4-coumarate: CoA ligase (isoenzyme 2), for which a specific involvement in flavonoid biosynthesis has been postulated, was affected by the elicitor. For two of the induced enzymes, phenylalanine ammonia-lyase and chalcone synthase, the changes in activity at stage I were shown to be preceded by large changes in their rates of synthesis, as determined by in vivo labelling with [³⁵S] methionine and immunoprecipitation.Abbreviations Pmg Phytophthora megasperma f. sp. glycinea - glyceollin is a term used to designate the 3 isomers which accumulate in challenged soybean tissue (Moesta and Grisebach 1981b)     

Anaerobic degradation of halogenated benzoic acids by photoheterotrophic bacteria

Abstract From light-exposed enrichment cultures containing benzoate and a mixture of chlorobenzoates, a pure culture was obtained able to grow with 3-chlorobenzoate (3-CBA) or 3-bromobenzoate (3-BrBA) as the sole growth substrate anaerobically in the light. The thus isolated organism is a photoheterotroph, designated isolate DCP3. It is preliminarily identified as a Rhodopseudomonas palustris strain. It differs from Rhodopseudomonas palustris WS17, the only other known photoheterotroph capable of using 3-CBA for growth, in its independence of benzoate for growth with 3-CBA and in its wider substrate range: if grown on 3-CBA, it can also use 2-CBA, 4-CBA or 3,5-CBA.     

Synthesis of Brunfelsamidine Ribonucleoside and Certain Related Compounds by the Stereospecific Sodium Salt Glycosylation Procedure

Abstract

A synthesis of 2,4-dideazaribavirin ( 2 ), brunfelsamidine ribonucleoside ( 8c ) and certain related derivatives are described for the first time using the stereospecific sodium salt glycosylation procedure. Glycosylation of the sodium salt of pyrrole-3-carbonitrile ( 4 ) with 1-chloro-2, 3-O-t-isopropylidene-5-O-t-butyldimethylsilyl-α-D-ribofuranose ( 5 ) gave exclusively the corresponding blocked nucleoside ( 6 ) with β-anomeric configuration, which on deprotection provided 1-β-D-ribofuranosylpyrrole-3-carbonitrile ( 7 ). Functional group tranformation of 7 gave 2 , 8c and related 3-substituted pyrrole ribonucleosides. These compounds are devoid of any significant antiviral/antitumor activity invitro.     

The Clinical Characteristics,Carbapenem Resistance,and Outcome of Acinetobacter Bacteremia According to Genospecies

Background

Few clinical data are available on the relationship between genospecies and outcome of Acinetobacter bacteremia, and the results are inconsistent. We performed this study to evaluate the relationship between genospecies and the outcome of Acinetobacter bacteremia.

Methods

Clinical data from 180 patients who had Acinetobacter bacteremia from 2003 to 2010 were reviewed retrospectively. The genospecies were identified by rpoB gene sequence analysis. The clinical features and outcomes of 90 patients with A. baumannii bacteremia were compared to those of 90 patients with non-baumannii Acinetobacter bacteremia (60 with A. nosocomialis, 17 with Acinetobacter species “close to 13 TU”, 11 with A. pittii, and two with A. calcoaceticus).

Results

A. baumannii bacteremia was associated with intensive care unit-onset, mechanical ventilation, pneumonia, carbapenem resistance, and higher APACHE II scores, compared to non-baumannii Acinetobacter bacteremia (P<0.05). In univariate analyses, age, pneumonia, multidrug resistance, carbapenem resistance, inappropriate empirical antibiotics, higher APACHE II scores, and A. baumannii genospecies were risk factors for mortality (P<0.05). Multivariate analysis revealed A. baumannii genospecies (OR, 3.60; 95% CI, 1.56–8.33), age, pneumonia, and higher APACHE II scores to be independent risk factors for mortality (P<0.05).

Conclusion

A. baumannii genospecies was an independent risk factor for mortality in patients with Acinetobacter bacteremia. Our results emphasize the importance of correct species identification of Acinetobacter blood isolates.     

Synthesis of Certain 4-Substituted-1-β-D-Ribofuranosyl-3-Hydroxypyrazoles Structurally Related to the Antibiotic Pyrazofurin

Abstract

Several 4-substituted-1-β-D-ribofuranosyl-3-hydroxypyrazoles were prepared as structural analogs of pyrazofurin. Glycosylation of the TMS derivative of ethyl 3(5)-hydroxypyrazole-4-carboxylate (3) with 1-0-acetyl-2,3,5-tri-0-benzoyl-D-ribofuranose in the presence of TMS-triflate gave predominantly ethyl 3-hydroxy-1-(2,3,5-tri-0-benzoyl-β-D-ribofuranosyl)pyrazole-4-carboxylate (4a), which on subsequent ammonolysis furnished 3-hydroxy-1-β-D-ribofuranosylpyrazole-4-carboxamide (5). Benzylation of 4a with benzyl bromide and further ammonolysis gave 3-benzyloxy-1-β-D-ribofuranosylpyrazole-4-carboxamide (8a). Catalytic (Pd/C) hydrogenation of 8a afforded yet another high yield route to 5. Saponification of the ester function of ethyl 3-benzyloxy-1-β-D-ribofuranosylpyrazole-4-carboxylate (7b) gave the corresponding 4-carboxylic acid (6a). Phosphorylation of 8a and subsequent debenzylation of the intermediate 11a gave 3-hydroxy-1-β-D-ribofuranosylpyrazole-4-carboxamide 5′-phosphate (11b). Dehydration of 3-benzyloxy-1-(2,3,5-tri-0-acetyl-β-D-ribofuranosyl)pyrazole-4-carboxamide (8b) with POCl₃ provided the corresponding 4-carbonitrile derivative (10a), which on debenzylation with Cl₃SiI gave 3-hydroxy-1-(2,3,5-tri-0-acetyl-β-D-ribofuranosyl)pyrazole-4-carbonitrile (13). Reaction of 13 with H₂S/pyridine and subsequent deacetylation gave 3-hydroxy-1-β-D-ribofuranosylpyrazole-4-thiocarboxamide (12b). Similarly, treatment of 13 with NH₂OH afforded 3-hydroxy-1-β-D-ribofuranosylpyrazole-4-carboxamidoxime (14a), which on catalytic (Pd/C) hydrogenation gave the corresponding 4-carboxamidine derivative (14b). The structural assignment of these pyrazole ribonucleosides was made by single-crystal X-ray analysis of 6a. None of these compounds exhibited any significant antitumor or antiviral activity in cell culture.     

6,7-Dimethyl-3-β-D-Erythrofuranosyl-1-Phenyl- and 1-p-Fluorophenyl-Pyrazolo[3,4-b]QUINOXALINE∗

Abstract

The C-nucleoside analogs 6,7-dimethyl-3-β-D-erythrofuranosyl-1-phenylpyrazolo[3,4-b]quinoxaline 4 and 3-β- D -erythrofuranosyl-1-p-fluorophenylpyrazolo[3,4-b]quinoxaline 8 were prepared by dehydration of the polyhydroxyalkyl chain of 6,7-dimethyl-1-phenyl-3-( D -arabino-tetritol-1-yl)-pyrazolo[3,4-b]quinoxaline 3 and 1-p-fluorophenyl-3-( D -arabino-tetritol-1-yl)-pyrazolo[3,4-b]quinoxaline 7, respectively. The structure and anomeric configuration of the products were determined by n.m.r. spectroscopy. The mass spectra and biological activities in connection with chemical constitution are discussed.     

Synthesis and Biological Evaluation of some Acyclic Nucleoside Cyclic Phosphoramidate Derivatives

Abstract

The acyclic nucleosides 2 were treated with 2-chloro-3-methyl-1-oxa-3-aza-2-phosphacyclopentane (3) in the presence of diisopropylethylamine to give the corresponding phosphoramidite derivatives (4). The phosphoramidite intermediates (4) were oxidized with m-chloroperbenzoic acid to the phosphoramidate derivatives (5). Treatment of 5a,b with ZnBr₂ in CH₃NO₂ gave the corresponding acyclic nucleoside cyclic phosphoramidates (6a,b). Attempts to desilylation of 5c by tetrabutylammonium fluoride (TBAF) resulted in opening of the phosphoramidate ring. The newly synthesized compounds were evaluated for antiviral and antitumor cell activity.     

Aerobic degradation of polychlorinated biphenyls by Alcaligenes sp. JB1: metabolites and enzymes

In contrast to the degradation of penta-and hexachlorobiphenyls in chemostat cultures, the metabolism of PCBs by Alcaligenes sp. JB1 was shown to be restricted to PCBs with up to four chlorine substituents in resting-cell assays. Among these, the PCB congeners containing ortho chlorine substituents on both phenyl rings were found to be least degraded. Monochloro-benzoates and dichlorobenzoates were detected as metabolites. Resting cell assays with chlorobenzoates showed that JB1 could metabolize all three monochlorobenzoates and dichlorobenzoates containing only meta and para chlorine substituents, but not dichlorobenzoates possessing an ortho chlorine substituent. In enzyme activity assays, meta cleaving 2,3-dihydroxybiphenyl 1,2-dioxygenase and catechol 2,3-dioxygenase activities were constitutive, whereas benzoate dioxygenase and ortho cleaving catechol 1,2-dioxygenase activities were induced by their substrates. No activity was found for pyrocatechase II, the enzyme that is specific for chlorocatechols. The data suggest that complete mineralization of PCBs with three or more chlorine substituents by Alcaligenes sp. JB1 is unlikely.Abbreviations PCB polychlorinated biphenyls - CBA chlorobenzoate - D di - Tr tri - Te tetra - Pe penta- - H hexa