Separation of pure polychlorinated biphenyl isomers into two types of inducers on the basis of induction of cytochrome P-450 or P-448.

A number of isomerically pure polychlorinated biphenyls (PCBs) were tested as inducers of hepatic drug-metabolizing enzymes in the rat. The chlorinated biphenyl isomers can be categorized into two distinct groups of inducers, while commercial PCB mixtures have characteristics of both groups. Biphenyls chlorinated symmetrically in both the meta and para positions (3,4,3′,4′- and 3,4,5,3′,4′,5′-) increase the formation of cytochrome P-448, the ratio of the 455 to 430 peaks of the ethyl isocyanide difference spectrum, and aryl hydrocarbon hydroxylase and glucuronyl transferase activities, but decrease aminopyrine N-demethylase activity. These isomers are also the most toxic, as measured by weight loss. Biphenyl isomers chlorinated in both the para and ortho positions induce the formation of cytochrome P-450 rather than P-448, regardless of the chlorination of the meta position. These isomers, which include 2,4,2′,4′-tetra- and 2,4,5,2′,4′,5′-, 2,3,4,2′,3′,4′- and 2,4,6,2′,4′,6′-hexachlorobiphenyls, increase cytochrome P-450 and N-demethylase activity, but produce only a slight increase in aryl hydrocarbon hydroxylase activity, and do not alter the peak of the CO-difference spectrum or the ratio of the 455/430 peaks of the ethyl isocyanide difference spectrum. Isomers which are chlorinated in only one ring, or are chlorinated in both rings but not in the para positions, have very little activity as inducers of liver enzymes. Of the dichlorobiphenyls tested, 3,3′- and 4,4′-dichlorobiphenyls have very slight activity at extremely high doses.     

Enhancement of microsomal drug oxidation and glucuronidation in rat liver by an environmental chemical, polychlorinated biphenyl

A polychlorinated biphenyl (PCB) compound, Clophen A 50, enhanced both hepatic aryl hydrocarbon hydroxylase and p-nitroanisole O-demethylase activities (7.5-fold and 16-fold, respectively), after treating the rats for 6 days with consecutive daily injections of Clophen A 50 (15 mg/kg i.p.). The treatment increased 3-fold the content of the carbon monoxide binding hemoprotein in liver microsomes, causing a concomitant shift in its reduced carbon monoxide absorbance peak to 448 nm. NADPH cytochrome c reductase, another component reaction of the microsomal mixed-function oxidase, was enhanced 1.5-fold in 6 days. A slight enhancement in the overall hydroxylation reactions was already observable 24 h after a single injection of Clophen A 50.The UDPglucuronosyltransferase activity of native liver microsomes was enhanced 3-fold in 6 days by the Clophen A 50 treatment of rats. The enhancement was, however, more pronounced, if the microsomes were treated in vitro with membrane-perturbing agents to activate the latent UDPglucuronosyltransferase before measuring its activity. After treatment for 6 days, the enhancement was about 6-fold in digitonin-treated, 5-fold in phospholipase C-treated and about 10-fold in trypsin-digested microsomes. No enhancement could be detected 24 h after a single Clophen A 50 injection.Aryl hydrocarbon hydroxylase activity was also enhanced in lung (5-fold), and kidney (8-fold) microsomes, whereas the microsomes from the duodenal mucosa exhibited no enhancement by a Clophen A 50 treatment of rats for 3 days.The data obtained support the assumption that PCBs form a new type of inducer group in enhancing the microsomal drug biotransformation. Both the monooxygenase complex and UDPglucuronosyltransferase differ in their properties from those after enhancement with the known types of inducers, exemplified by phenobarbital and 3-methylcholanthrene, respectively.     

On the inhibition of microsomal drug metabolism by polychlorinated biphenyls (PCB) and related phenolic compounds.

The in vitro metabolism of p-nitroanisole, aminopyrine, and aniline by rat liver microsomal monoxygenases were studied in the presence of different polychlorinated biphenyl (PCB) mixtures and some related hydroxybiphenyls. The tested PCB mixtures contained preferably dichloro- (di-CB), tetrachloro- (tetra-CB), or hexachlorobiphenyls (hexa-CB). All PCB were competitive inhibitors of only aminopyrine demethylation by normal microsomes (Ki 22-39 micron). In microsomes of PCB-pretreated rats the aminopyrine demethylation was inhibited noncompetitively by di-CB and hexa-CB whereas tetra-CB remained a competitive inhibitor (Ki 12 micron). Moreover, after PCB pretreatment all PCB were competitive inhibitors of p-nitroanisole demethylation. 2-OH-biphenyl and 4-OH-biphenyl caused competitive inhibition of aminopyrine demethylation and aniline hydroxylation but failed to inhibit p-nitroanisole metabolism by normal microsomes. Chlorinated 4-hydroxybiphenyls inhibited competitively the metabolism of both type I and type II substrates. However, after PCB pretreatment all phenolic compounds caused uncompetitive inhibition of aniline hydroxylation.     

Crystallization and preliminary crystallographic analysis of a 2,3-dihydroxybiphenyl dioxygenase from Pseudomonas sp. strain KKS102 having polychlorinated biphenyl (PCB)-degrading activity

Crystals have been obtained for a 2,3-dihydroxybiphenyl dioxygenase (conventionally called BphC) from a polychlorinated biphenyl (PCB)-degrader, Pseudomonas sp. strain KKS1O2. The crystals were grown using both ammonium sulfate and MPD as the precipitating agents. The crystals belonged to a tetragonal space group (I422) and diffracted to 2.5 Å. © 1995 Wiley-Liss, Inc.     

Studies on metabolic activation of vinyl chloride in Drosophila melanogaster after pretreatment with phenobarbital and polychlorinated biphenyls.

It is known that vinyl chloride is metabolized by the mixed function oxygenase system in the liver to reactive mutagenic and carcinogenic metabolites. This metabolic activation was studied in Drosophila melanogaster by measuring the uptake of 14C from labelled vinyl chloride in different strains and with different pretreatments with phenobarbital and polychlorinated biphenyl (PCB) Clophen A50), well known inducers of cytochrome P-450. In accordance with previously obtained data on vinyl chloride induced sex linked recessive lethals, it was shown that pretreatment with inducers increased the uptake of labelled compound up to ten times. There was, however, a marked difference in response between the five strains used. In particular, the strain Hikone, known to be resistant to insecticides, had a comparatively high initial radioactivity from vinyl chloride without any pretreatment, but it was not or insignificantly inducible with phenobarbital or PCB. Crosses between Hikone and an inducible strain indicated essentially a dominance for the Hikone genotype. Tests on inducible strains showed the same response to phenobarbital by 2 h old larvae and adult male and females. Dimethylsulphoxide (DMSO) used as a solvent decreased both the initial uptake of 14C and particularly the induction by PCB. The use of Tween 80 as an emulsifier did not have such an effect. It is emphasized that the interstrain variation in metabolic activation and inducability has to be taken into consideration in order to optimize the use of Drosophila for mutagenicity testing. This variation also opens up new possibilities of analyzing the mixed function oxygenase system biochemically and genetically.     

Enantioseparation and identification for the rationalization of the environmental impact of 4 polychlorinated biphenyls

Polychlorinated biphenyls (PCBs) are harmful and persistent organic pollutants that have long been used in industrial manufacturing. Their persistence leads to accumulation in the food chain causing potential toxic effects. As 19 out of 78 of the chiral congeners have stable atropisomers at ambient temperature, we studied some typical enantiomers: PCB45, PCB95, PCB136, and PCB149. The chiral stationary phases OD‐H and OJ‐H were used for separation in analytic high‐performance liquid chromatography (HPLC), as well as for collection in semi‐preparative HPLC. The resolution was optimized with respect to n‐hexane–based mobile phases, temperature, and flow rate. All pure enantiomers were recovered from semi‐preparative HPLC within 15 minutes for practical purpose. Characterization of the absolute configurations were conducted with a combination of theoretical and experimental electronic circular dichroism measurements. The enantiomers of PCB45, PCB95, PCB136, and PCB149 proved to be eluted as R > S, S > R, R > S, and S > R, respectively. Molecular structures (eg, substituent groups) and properties (eg, bond lengths, bond angles, and dipole moments) were quantitatively analyzed to understand the toxicity effect of PCBs. In summary, we have developed a well‐established methodology of collection and configuration identification for analogous PCB derivatives.     

Terpene-utilizing isolates and their relevance to enhanced biotransformation of polychlorinated biphenyls in soil

Orange peels, eucalyptus leaves, pine needles and ivy leaves were addedseparately to soil spiked with Aroclor 1242 (100 mgkg^-1.Polychorinated biphenyls (PCBs) disappeared after six months in all theamended soils, but not in unamended soils. Although biphenyl was not addedto any of the soils, all four amended soils had much higher levels(10⁸/g) of biphenyl-utilizing bacteria than the unamendedcontrol (10³/g). Ten random isolates obtained from these soilswere identified as coryneform bacteria. Five isolates, that were distinctlydifferent, were studied further with respect to growth on pure terpenes andmetabolism of PCBs. The most effective strains were Cellulomonas sp. T109and R. rhodochrous T100, which metabolized 83% and 80% ofAroclor 1242, respectively, during a six day period of growth on cymene andlimonene, respectively. The bphA gene, cloned as a 2.8 Kb Sa/I fragment ofpAW6194 from cbpA (Walia et al. 1990) hybridized to total DNA of allcoryneform isolates, and to the well-established PCB degrader Rhodococcusgloberulus. In contrast, a 5 Kb XhoI-SmaI fragment of the bphA gene(Furukawa & Miyazaki 1986) did not show any homology to the genomic DNAof any of the isolates or to R. globerulus, but did hybridize to two otherwell-known PCB degraders Pseudomonas sp. LB400, and Alcaligenes eutrophusH850. The data presented herein indicate that terpenes may be naturalsubstrates for biphenyl-degrading bacteria and may enhance substantialtransformation of Aroclor 1242.     

Covalent binding of polychlorinated biphenyls to proteins by reconstituted monooxygenase system containing cytochrome P-450

Incubation in the presence of NADPH and molecular oxygen of ¹⁴C-labeled polychlorinated biphenyls (PCBs) and two tetrachlorobiphenyl (TCB) isomers with a reconstituted system containing NADPH-cytochrome P-450 reductase and cytochrome P-450, both purified from liver microsomes of phenobarbital(PB)-pretreated rabbits, led to covalent binding of radioactive metabolites of PCBs and TCBs to the protein components of the system. A rabbit liver cytosol fraction added to the system provided more binding sites for the activated metabolites and thus increased the extent of binding markedly. The binding reaction depended absolutely on the reductase, cytochrome P-450 and NADPH, and required dilauroyl phosphatidylcholine and sodium cholate for maximal activity. A further stimulation of the binding was attained by including cytochrome b₅ in the reconstituted system. Four forms of cytochrome P-450, purified from liver microsomes of PB- and 3-methylcholanthrene(MC)-treated rabbits and rats, were used to reconstitute the PCB- and TCB-metabolizing systems, and it was found that PB-inducible forms of the cytochrome from both animals were more active than those inducible by MC in catalyzing the PCB- and TCB-binding reaction. Sodium dodecyl sulfate(SDS)-polyacrylamide gel electrophoresis indicated that, in the system containing the reductase, cytochrome P-450 and cytochrome b₅, PCB metabolites bound to the reductase and cytochrome P-450, but not to cytochrome b₅. In the presence of the liver cytosol fraction, the binding took place to many cytosolic proteins in addition to the reductase and cytochrome P-450.     

Effect of nutrient enrichment on the distribution and sedimentation of polychlorinated biphenyls (PCBs) in seawater

The effect of nutrient enrichment on the distribution of polychlorinated biphenyl's (PCBs) in the microbial food web and the residence time of PCBs in seawater was studied in an experimental mesocosm system. Two 5 m high temperature and light controlled mesocosm tubes (⊘ = 0,5 m) were filled with seawater from the northern Baltic Sea. Inorganic phosphorus and nitrogen were added daily to one mesocosm, while the other served as a control. Experiments were conducted at 5, 10 and 20°>C. Three ¹⁴C-labelled PCBs of different degree of chlorination were added to subsamples of the mesocosms: 4 chlorobiphenyl (MCB), IUPAC # 3; 2,2′,5,5′-tetrachlorobiphenyl (TCB), IUPAC # 52 and 2,2′, 4,4′,5,5′-hexachlorobiphenyl (HCB) IUPAC # 153. The biomasses and growth rates of the microorganisms as well as the sedimentation rate of particulate organic material increased with nutrient enrichment. The size distribution of the microorganisms changed with nutrient status, from dominance of picoplankton (< 2 μm) in the control towards increased importance of micro (> 10 μm) and nanoplankton (2– 10 μm) in nutrient enrichment. The specific growth rate of the bacterial community was found to be more temperature dependent than that of the phytoplankton community. The relative proportion of PCBs in the >2 μm fraction was observed to be in the order MCB < TCB < HCB, while the opposite distribution prevailed in the < 2 μm fraction. We hypothesize that this is due to the combined effect of the different Kow values of the PCBs and a different composition of the particulate organic carbon in the > 2 μm and < 2 μm fractions (e.g. different lipid composition). The residence time of the PCBs in the mesocosm generally decreased with nutrient enrichment, but was dependent on the degree of chlorination of the PCB. Our results indicate that the transport of organic pollutants up through the food web is more important in nutrient poor than in nutrient rich waters and that the importance of sedimentation is higher in eutrophic ecosystems. This revised version was published online in July 2006 with corrections to the Cover Date.     

Methyl-beta-cyclodextrin-enhanced solubilization and aerobic biodegradation of polychlorinated biphenyls in two aged-contaminated soils

The bioremediation of aged polychlorinated biphenyl (PCB)-contaminated soils is adversely affected by the low bioavailability of the pollutants. Randomly methylated-beta-cyclodextrins (RAMEB) were tested as a potential PCB-bioavailability-enhancing agent in the aerobic treatment of two aged-contaminated soils. The soils, contaminated by about 890 and 8500 mg/kg of Aroclor 1260 PCBs, were amended with biphenyl (4 g/kg), inorganic nutrients (to adjust their C:N ratio to 20:1), and variable amounts of RAMEB (0%, 0.5%, or 1.0% [w/w]) and treated in both aerobic 3-L solid-phase reactors and 1.5-L packed-bed loop reactors for 6 months. Notably, significant enhancement of the PCB biodegradation and dechlorination, along with a detectable depletion of the initial soil ecotoxicity, were generally observed in the RAMEB-treated reactors of both soils. RAMEB effects were different in the two soils, depending upon the treatment conditions employed, and generally increased proportionally with the concentration at which RAMEB was applied. RAMEB, which was slowly metabolized by the soil's aerobic microorganisms, was found to markedly enhance the occurrence of the indigenous aerobic, cultivable biphenyl-growing bacteria harboring genes homologous to those of two highly specialized PCB degraders (i.e., bphABC genes of Pseudomonas pseudoalcaligenes KF707 and bphA1A2A3A4BC1 genes of Rhodococcus globerulus P6) and chlorobenzoic acid-degrading bacteria as well as the occurrence of PCBs in the water phase of the soil reactors. These findings indicate that RAMEB enhanced the aerobic bioremediation of the two soils by increasing the bioavailability of PCBs and the occurrence of specialized bacteria in the soil reactors.     

Effects of humic substances on the bioavailability and aerobic biodegradation of polychlorinated biphenyls in a model soil.

The very high hydrophobicity of polychlorinated biphenyls (PCBs) strongly reduces their bioavailability in aged contaminated soils, thus limiting their bioremediation. The biodegradability of PCBs in heavily contaminated soils can be significantly enhanced by soil treatment with surface-active agents. In this work, the effects of naturally occurring surfactants such as humic substances (HS) on the aerobic biodegradation of PCBs in a model soil were studied. The soil was amended with biphenyl (4 g/kg), Fenclor 42 (1,000 mg/kg), the aerobic PCB-biodegrading bacterial co-culture ECO3 (inoculum: 10(8)CFU/mL), and treated in aerobic batch slurry-phase conditions (17.5% w/v) with and without the addition of HS at the rates of 1.5 and 3.0% (w/w). Low PCBs biodegradation and dechlorination yields were observed in the HS-free microcosms, probably as a result of the rapid disappearance of inoculated bacteria. The presence of HS influenced significantly the activity of the specialized biomass and the biodegradation of PCBs in the microcosms. The microcosms that received HS at the 1.5% rate showed a higher persistence of the specialized bacteria and yields of PCB biodegradation and dechlorination about 150 and 100%, respectively, larger than those found for the HS-free microcosms. Lower stimulating effects were observed in the microcosms added with the HS at 3.0% rate. These effects were attributed to an increased solubilization of PCBs in the hydrophobic domains of the humic supramolecular associations and to a different accessibility of PCBs by the specialized bacteria at the different rates of HS addition. Although the slurry-phase treatment generally showed a decrease of the original soil ecotoxicity, the addition of the originally non-toxic HS decreased soil ecotoxicity for the Collembola animal biomarker and increased that towards the Lepidium sativum vegetal biomarker.     

Association between exudates of brown algae and polychlorinated biphenyls

Exudates from the brown algaeCaepidium antarcticum andDesmarestia sp. were investigated for their ability to associate with hydrophobic pollutants such as polychlorinated biphenyls (PCB s). The percentage of PCB associated with algal exudates ranged from 79% for decachlorobiphenyl to 23% for the pentachlorobiphenyl congener No. 95. Exudates from the tested brown algae may therefore alter the bioavailability of PCBs in natural or artificial ecosystems.     

Biodegradation and evaporation of polychlorinated biphenyls (PCBs) in liquid media

During microbial degradation of PCBs in a liquid medium, two processes influence the PCB concentration in the medium simultaneously: biodegradation and evaporation. The physical loss of PCB due to evaporation frequently causes false positive results in biodegradation experiments. Therefore, if only PCBs are monitored, the determination of the PCB concentration in both liquid and gaseous phases is necessary for a correct appraisal of biodegradation. The kinetics of PCB evaporation and biodegradation were monitored and described by a simple mathematical model. The evaporation and biodegradation rate constants for individual PCB congeners were determined for PCB degradation in liquid medium byPseudomonas stutzeri andAlcaligenes xylosoxidans, both isolated from a longterm PCB-contaminated soil.Symbols a ₁,b ₁,a ₂,b ₂ fitting parameters - c ₀ initial concentration of PCB congener in liquid medium - c _l concentration of PCB congener in liquid medium - c _ev concentration of PCB congener in sorbent - k _ev rate constant of PCB congener evaporation - k _met rate constant of PCB congener metabolization - n _s amount of PCB congener in sorbent - t _1/2 half-time of evaporation - V _t volume of liquid medium     

Structural basis for preferential binding of non-ortho-substituted polychlorinated biphenyls by the monoclonal antibody S2B1

Polychlorinated biphenyls (PCBs) are a family of 209 isomers (congeners) with a wide range of toxic effects. In structural terms, they are of two types: those with and those without chlorines at the ortho positions (2, 2', 6 and 6'). Only 20 congeners have no ortho chlorines. Three of these are bound by the aryl hydrocarbon receptor and are one to four orders of magnitude more toxic than all others. A monoclonal antibody, S2B1, and its recombinant Fab have high selectivity and nanomolar binding affinities for two of the most toxic non-ortho-chlorinated PCBs, 3,4,3',4'-tetrachlorobiphenyl and 3,4,3',4',5'-pentachlorobiphenyl. To investigate the basis for these properties, we built a three-dimensional structure model of the S2B1 variable fragment (Fv) based on the high-resolution crystallographic structures of antibodies 48G7 and N1G9. Two plausible conformations for the complementarity-determining region (CDR) H3 loop led to two putative PCB-binding pockets with very different shapes (models A and B). Docking studies using molecular mechanics and potentials of mean force (PMF) indicated that model B was most consistent with the selectivity observed for S2B1 in competition ELISAs. The binding site in model B had a deep, narrow pocket between V(L) and V(H), with a slight constriction at the top that opened into a wider pocket between CDRs H1 and H3 on the antibody surface. This binding site resembles those of esterolytic antibodies that bind haptens with phenyl rings. One phenyl ring of the PCB fits into the deep pocket, and the other ring is bound in the shallower one. The bound PCB is surrounded by the side chains of TyrL91, TyrL96 and TrpH98, and it has a pi-cation interaction with ArgL46. The tight fit of the binding pocket around the ortho positions of the bound PCBs indicates that steric hindrance of ortho chlorines in the binding site, rather than induced conformational change of the PCBs, is responsible for the selectivity of S2B1.     

Isolation and characterization of different plant associated bacteria and their potential to degrade polychlorinated biphenyls

In our experiments the effect of different plants on microbial activities resulting in degradation and PCB removal from long-term contaminated soil was evaluated. Total bacteria and bacteria representing the dominating microflora within rhizosphere of individual plant species – tobacco (Nicotiana tabacum), black nightshade (Solanum nigrum), horseradish (Armoracia rusticana) and goat willow (Salix caprea) planted in PCB contaminated soil as well as from the same, but non-vegetated PCBs soil, were isolated and biochemically characterized. PCB bacterial degraders, stimulated by root exudates of individual plants, were detected after isolation from rhizosphere soil and precultivation on minimal medium with biphenyl as the sole carbon source. Detection of BphA1 gene (first gene of bacterial aerobic PCB degradative pathway) in genomes of rhizosphere microorganisms was performed by nested PCR technique using previously designed specific primers. Rhizosphere of individual plants contained different bacterial species, mostly gram-negative non-fermenting bacteria of Pseudomonas, Agrobacterium, Ochrobactrum and other species. Gene BphA1 was identified in genome of only several of them. From tested species, S. caprea and A. rusticana have shown to be promising candidates for rhizoremediation purposes.     

The ability of different plant species to remove polycyclic aromatic hydrocarbons and polychlorinated biphenyls from incubation media

The ability of in vitro cultured cells of black nightshade, wheat, barley, soybean, tomato, mulberry and birch to grow in the presence of polycyclic aromatic hydrocarbons (PAHs) and polychlorinated biphenyls (PCBs) and to metabolise them was compared. No correlation was found between the resistance of the plants and removal of xenobiotics. Up to 20% of PCBs and over 90% of PAHs were removed by wheat cells from nutrient media in two weeks.     

Isolation and characterization of a thermophilic Bacillus sp. JF8 capable of degrading polychlorinated biphenyls and naphthalene

Bacillus sp. strain JF8, which was isolated from compost, utilizes naphthalene and biphenyl as carbon sources at 60 degrees C. Biphenyl grown cells of strain JF8 barely degraded naphthalene while naphthalene grown cells did not degrade p-chlorobiphenyl, suggesting the existince of two independent degradation pathways. Isolation of JF8N, a mutant strain which can not utilize biphenyl as a carbon source while retaining the ability to utilize naphthalene, supports this hypothesis. Biphenyl grown cells of strain JF8 can degrade several polychlorinated biphenyl congeners including tetra- and pentachlorobiphenyl. bph and nah probes from mesophilic organisms failed to hybridize to strain JF8 DNA.     

Distribution and biochemical effects of pentylenetetrazol in brains of swine treated with a polychlorinated biphenyl

In order to detect an effect on the CNS following treatment with polychlorinated biphenyls (PCB), pentylenetetrazol (PTZ) was administered to two groups of miniature swine. One group was a control and the other had been treated for 30 days with Aroclor 1254 (PCB) at a dose of 25 μg/kg in ground laboratory chow. No statistical difference was seen between the amount of PTZ administered or the time required to convulse for either group of animals. The total amount of PTZ found in brains of PCB-treated swine was less than from brains of control swine. Less PTZ was found in medulla and cerebellum from PCB-treated animals. The amount of PTZ found in motor cortex and in caudate nucleus from brains of PCB-treated swine was equal to the amounts found in similar structures of control brains. A 2–3-fold increase in dihydroxyphenylalanine (DOPA) levels was detected in motor cortex and medulla from PCB-treated animals, although levels of norepinephrine (NE) and gamma- aminobutyric acid (GABA) were unchanged from controls. It is concluded that PCB treatment had no effect on altering convulsive threshold of PTZ in swine, although PCB treatment does decrease the amount of PTZ in swine brains. Non-specific alterations in brain amine levels were also seen in PCB-treated swine.     

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