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Chlorobenzene-impaired lindane metabolism and the effect of pretreatment with chlorobenzene, lindane, or chlorobenzene plus lindane.

The storage and metabolism of lindane (gamma-HCH) was studied in the female rat after the administration of a hepatotoxic dose of chlorobenzene. Impaired lindane metabolism was observed following a challenge dose of 1.12 g chlorobenzene/kg. The data indicated that a hepatotoxic dose of chlorobenzene (CB) selectively impaired certain pathways, such as dehydrochlorination and the direct hydroxylation of lindane, to a greater extent than others, such as the dehydrogenation and dechlorination of lindane. Pretreatment with a subtoxic level of chlorobenzene produced: (1) significant increases in the dehydrogenation of lindane, (2) significant increase in the excretion of conjugated metabolites, (3) significant increases in the excretion of metabolites derived from the dehydrogenation of lindane through hexachlorocylohexene, gamma-HCCH, (4) significant improvement in the excretion of metabolites derived from CB-impaired dehydrochlorination of lindane as well as from the CB-impaired hydroxylation of lindane, and (5) significant reduction in the level of unaltered lindane stored in the adipose tissue. Repeated pretreatment with a subtoxic level of chlorobenzene offered significant protection against the reduction in lindane metabolism produced by the single hepatotoxic dose of chlorobenzene. Pretreatment with gamma-HCH alone was not as effective against the hepatotoxic effect of CB on lindane metabolism.

Animals↗

Toxicity of chlorobenzene on Pseudomonas sp. strain RHO1, a chlorobenzene-degrading strain.

Pseudomonas sp. strain RHO1 able to use chloro- and 1,4-dichlorobenzene as growth substrates was tested towards sensitivity against chlorobenzene. Concentrations of chlorobenzene higher than 3.5 mM were found to be toxic to cells independent of pregrowth with chlorobenzene or nutrient broth. Below this concentration, sensitivity towards chlorobenzene depended on the precultivation of the cells, i.e. type of growth substrate (chlorobenzene or nutrient broth) and the concentration of chlorobenzene as the growth substrate. Cells grown in continuous culture were especially sensitive with a threshold concentration of 2.5 mM chlorobenzene. In addition to chlorobenzene, metabolites also seem to function as toxic compounds. 2-Chlorophenol and 3-chlorocatechol were isolated from cell extracts. Cleavage of 3-chlorocatechol by catechol 1,2-dioxygenase seems to be the critical step in the metabolism of chlorobenzene.

Biodegradation, Environmental↗

Quantitation of urinary chlorobenzene metabolites by HPLC: concentrations of 4-chlorocatechol and chlorophenols in urine and of chlorobenzene in biological specimens of subjects exposed to chlorobenzene.

A simple method for the determination of 4-chlorocatechol (ClCh, 4-chloro-1,2-benzenediol) and chlorophenols (ClPh), metabolites of monochlorobenzene (ClBz), in urine by high performance liquid chromatography (HPLC) is described. Enzymatic hydrolysates of urine were applied to a stainless-steel column packed with octadecyl-silanized silica gel, and a mixed solution of 20 mM potassium phosphate monobasic: acetonitryl (75:25, v/v) was used as a mobile phase. The procedures for ether extraction and evaporation of extract could be omitted. The accuracy and precision of the present HPLC method were satisfactory. The excretion kinetics of ClCh and p-ClPh were investigated over 35 h after cessation of ClBz inhalation. Proportional relationships between concentrations of ClBz in air and of its metabolites in urine were observed. The slopes of regression lines predicting the levels of ClCh, p-ClPh and total ClPh in urine taken during the last 2 h of exposure to ClBz in air were 6.56, 1.13 and 2.83 mg/g creatinine for 1 ppm ClBz, respectively. ClBz in the blood and the end exhaled air of subjects at the end of exposure were identified by gas chromatography (GC) and mass spectrometry. A proportional relationship was observed between the concentration of ClBz in air and that in blood. The validity of the threshold limit value (TLV) for ClBz as evaluated from the subjective and objective symptoms is discussed.

Adult↗

The broad substrate chlorobenzene dioxygenase and cis-chlorobenzene dihydrodiol dehydrogenase of Pseudomonas sp. strain P51 are linked evolutionarily to the enzymes for benzene and toluene degradation.

The chlorobenzene degradation pathway of Pseudomonas sp. strain P51 is an evolutionary novelty. The first enzymes of the pathway, the chlorobenzene dioxygenase and the cis-chlorobenzene dihydrodiol dehydrogenase, are encoded on a plasmid-located transposon Tn5280. Chlorobenzene dioxygenase is a four-protein complex, formed by the gene products of tcbAa for the large subunit of the terminal oxygenase, tcbAb for the small subunit, tcbAc for the ferredoxin, and tcbAd for the NADH reductase. Directly downstream of tcbAd is the gene for the cis-chlorobenzene dihydrodiol dehydrogenase, tcbB. Homology comparisons indicated that these genes and gene products are most closely related to those for toluene (todC1C2BAD) and benzene degradation (bedC1C2BA and bnzABCD) and distantly to those for biphenyl, naphthalene, and benzoate degradation. Similar to the tod-encoded enzymes, chlorobenzene dioxygenase and cis-chlorobenzene dihydrodiol dehydrogenase were capable of oxidizing 1,2-dichlorobenzene, toluene, naphthalene, and biphenyl, but not benzoate, to the corresponding dihydrodiol and dihydroxy intermediates. These data strongly suggest that the chlorobenzene dioxygenase and dehydrogenase originated from a toluene or benzene degradation pathway, probably by horizontal gene transfer. This evolutionary event left its traces as short gene fragments directly outside the tcbAB coding regions.

Amino Acid Sequence↗

[Experimental study on the treatment of organic wastewater containing chlorobenzene by using an EGSB reactor].

In this paper, the study on the inhibition and recovery of the methanogenic activity of the granular sludge which uncontacted and contacted with chlorobenzene caused by chlorobenzene, and the study of the treatment of organic wastewater containing chlorobenzene by using an EGSB reactor were conducted. The results showed that the activity of the granular sludge which had not contacted with chlorobenzene would be inhibited by different concentrations chlorobenzene; but for the granular sludge which had contacted with chlorobenzene, its activity would be inhibited only by higher concentration (100 mg/L) chlorobenzene. Using EGSB reactor to treat organic wastewater containing chlorobenzene, when the influent chlorobenzene concentration was about 10-50 mg/L, the effluent concentration was lower than 7 mg/L before 65 days, but after the 66th day, the effluent concentration suddenly reached above 25 mg/L, and after stopping adding chlorobenzene, the effluent chlorobenzene concentration was between 3.4-38.32 mg/L, this showed that the high chlorobenzene removal efficiency was mainly due to the strong adsorption by granular sludge, and the biological degradation of chlorobenzene was not obvious.

Biodegradation, Environmental↗

NTP Toxicology and Carcinogenesis Studies of Chlorobenzene (CAS No. 108-90-7) in F344/N Rats and B6C3F1 Mice (Gavage Studies).

Chlorobenzene is a colorless, volatile liquid under standard environmental conditions (vapor pressure=11.8 mm Hg at 25 degrees C, 760 mm Hg). It is used primarily as a solvent (e.g. resins, dyes, pesticides, and perfumes), a degreasing agent, and a chemical intermediate, particularly in the synthesis of nitrobenzenes. Although still considerable, estimates of the yearly production volume of chlorobenzene in the United States indicate declining use in recent years, due to the reduced demand for organochlorine pesticides utilizing chlorobenzene as an intermediate. Toxicology and carcinogenesis studies of chlorobenzene (<99% pure) were conducted by administering the test chemical in corn oil by gavage to groups of 50 male and 50 female F344/N rats and 50 female B6C3F1 mice at doses of 60 or 120 mg/kg. Groups of 50 male B6C3F1 mice received 30 or 60 mg/kg. Chlorobenzene was administered five times per week for 103 weeks. Groups of 50 rats and 50 mice of each sex received corn oil by gavage on the same schedule and served as vehicle controls, and additional groups of 50 rats and 50 mice of each sex served as untreated controls. The chlorobenzene doses were chosen on the basis of 90-day studies, in which doses 2-fold or greater in excess of the doses used in the 2-year study caused death, hepatocellular necrosis, renal tubular injury, thymic necrosis, or lymphoid or myeloid depletion of bone marrow, spleen or thymus. Mean body weights of dosed rats and mice were essentially the same or greater than those of the controls during the 2-year studies. Survivals of low dose male rats, dosed female rats, dosed male mice, and dosed female mice were not adversely affected by administration of chlorobenzene. Survival of high dose male rats in the 2-year study was significantly (P=0.033) lower than that of the vehicle controls. No chlorobenzene-induced toxic lesions responsible for this reduction in survival were observed. Based on the prechronic results and on the above data, the doses used in the 2-year study were considered to be adequate for carcinogenicity testing. Male rats dosed with chlorobenzene exhibited a significant (P<0.05) increase in the incidence of animals with neoplastic nodules of the liver (overall incidences: untreated control, 4/50 (8%); vehicle control, 2/50 (4%); low dose, 4/49 (8%); high dose, 8/49 (16)). Increased incidences of hepatocellular carcinomas in male rats or of neoplastic nodules or hepatocellular carcinomas in female rats were not observed. No increased tumor incidences were observed in female rats or in male or female mice. Under the conditions of these studies, chlorobenzene administration increased the occurrence of neoplastic nodules of the liver in high dose (120 mg/kg/day) male F344/N rats, providing some but not clear evidence of carcinogenicity of chlorobenzene in male rats. Carcinogenic effects of chlorobenzene were not observed in female F344/N rats or in male or female B6C3F1 mice. Levels of Evidence of Carcinogenicity: Male Rats: Equivocal Female Rats: Negative Male Mice: Negative Female Mice: Negative Synonyms: monochlorobenzene; chlorobenzol; phenyl chloride; benzene monochloride

Journal Article↗

Variation of cysteine level by chlorobenzene-induced pertubation of glutathione metabolism in rat liver.

Effects of chlorobenzene-induced alteration in glutathione levels on cysteine metabolism in rat liver were investigated. Male Wistar rats were intraperitoneally injected with chlorobenzene (0.2, 0.5, 1.0 or 2.0 mmol/kg body weight). Both hepatic glutathione and cysteine levels were dose-dependently decreased by the chlorobenzene 6 h after the injection. However, at 24 h, the glutathione in the rats with chlorobenzene increased significantly as compared to that in the rats without chlorobenzene. Concomitant to the elevation in glutathione levels, hepatic glutathione synthesis activities were increased by the chlorobenzene by 68-111%. On the other hand, no significant difference between the rats with and without chlorobenzene was observed as regards cysteine levels at 24 h. Hepatic glutamate, glycine, methionine and serine levels were unaltered but hepatic taurine levels were significantly decreased by the chlorobenzene at both 6 and 24 h. Chlorobenzene administration had no effect on hepatic cystathionine synthase and cystathionase activities. These results indicate that a transient loss of hepatic glutathione, caused by the administration of chlorobenzene, resulted in an acceleration of glutathione synthesis and an increase of cysteine demand in the liver.

Amino Acids↗

Effect of variation of exposure to airborne chlorobenzene on internal exposure and concentrations of urinary metabolite.

OBJECTIVES: This study aimed to develop a physiologically based pharmacokinetic model for chlorobenzene and to investigate the effect of variation in exposure to chlorobenzene on the chlorobenzene concentration in blood and the urinary concentration of 4-chlorocatechol. METHODS: A physiologically based pharmacokinetic model was developed and the simulated results of urinary 4-chlorocatechol concentrations were compared with the values found in experiments and field surveys. The area under the chlorobenzene concentration-time curve in blood (CBBauc) was selected as the measure of internal exposure related to the chronic effect of chlorobenzene. The maximum one-hour time weighted average value of chlorobenzene concentration in blood (CBBmax) was chosen as the measure of internal exposure related to the acute effect of chlorobenzene. The total amount of urinary 4-chlorocatechol (TOTCC) and that excreted during the last four hours (CC(4-8)) or two hours (CC(6-8)) of exposure as well as that excreted during two hours on the next morning (CC(22-24)) were used to represent concentrations of urinary metabolites. The effects of variation of the one-hour time weighted averages of airborne chlorobenzene exposure (CBAs) on the internal exposures and the concentrations of urinary metabolites were investigated with the pharmacokinetic model. RESULTS: The comparison of the simulated results with the observed data showed that the pharmacokinetic model can be used to estimate the urinary concentrations of 4-chlorocatechol. The CBBauc and TOTCC were not affected by changes in both the geometric SD (GSD) of CBAs or the variations in CBAs. The CBBmax varied with changes in both the GSD and CBAs. The CC(4-8) and CC(6-8) did not vary with the GSD, but these concentrations were affected by the change in the CBAs. Although there was little effect of the GSD and CBAs on the CC(22-24), this value highly reflected the exposure over the preceding days. CONCLUSION: To protect workers from the chronic effect of chlorobenzene, it may be sufficient to control the daily average exposure. To protect from the acute effect, however, the short term exposure must be controlled as well. The values of CC(4-8) and CC(6-8) were acceptable for estimating daily average exposure, but the CC(22-24) was not.

Adipose Tissue↗

Enzymology of the degradation of (di)chlorobenzenes by Xanthobacter flavus 14p1.

Xanthobacter flavus 14p1 used 1,4-dichlorobenzene as the sole source of carbon and energy but did not grow on other (chloro)aromatic compounds. 1,4-Dichlorobenzene was attacked by a chlorobenzene dioxygenase, and the intermediate chlorocatechol was metabolized by the modified ortho pathway. All enzymes necessary to convert 1, 4-dichlorobenzene to 3-oxoadipate showed a low substrate specificity and also accepted the respective intermediates of chlorobenzene or 1, 3-dichlorobenzene degradation. Of the three compounds chlorobenzene, 1,4-dichlorobenzene, and 1,3-dichlorobenzene, the latter was the most toxic for X. flavus 14p1. Furthermore, 1,3-dichlorobenzene did not induce chlorocatechol 1,2-dioxygenase activity of the organism. Chlorobenzene, however, induced chlorocatechol 1,2-dioxygenase, dienelactone hydrolase, and maleylacetate reductase activities. As demonstrated by chloride release, also chlorobenzene dioxygenase, chlorobenzene cis-dihydrodiol dehydrogenase, and chloromuconate cycloisomerase activities were present in chlorobenzene-induced cells, but chlorobenzene failed to support growth. Presumably a toxic compound was formed from one of the intermediates.

Biodegradation, Environmental↗

Chlorobenzenes in rivers draining industrial catchments

Eleven chlorobenzenes (out of a total of 12 in the congener series) were monitored weekly on four industrialized rivers (Aire, Calder, Don and Trent) of the Southern Humber Catchment in whole water samples. 1,2- and 1,4-dichlorobenzene were present at relatively high levels on both the Aire and Calder, having mean concentrations of approximately 30 ng/l. They were both at lower concentrations on the Don and Trent, although the 1,4-isomer dominated. All other chlorobenzenes monitored were routinely found on all the rivers, with the exception of hexachlorobenzene, which was only regularly detected on the Trent. Again, the rivers fell into two classes with respect to their total chlorobenzene concentrations, with the Aire and Calder being more polluted. The higher levels of chlorobenzenes (excluding hexachlorobenzene which was used widely as a agricultural pesticide) on the Aire and Calder, and the dominance of the 1,4-dichlorobenzene congener (accounting for 60-70% of sigma chlorobenzenes) on the Don and Trent, indicated that the Aire and Calder were predominately contaminated with chlorobenzenes through industrial sources, while the Don and Trent were mainly contaminated through domestic sources (1,4-dichlorobenzene is widely used as a toilet deodorant). 1,4-Dichlorobenzene dominated flux, with the Aire, Don and Trent exporting 52.5 kg/year into the Humber estuary, followed by the 1,2-dichlorobenzene at 38.8 kg/year. Sigma chlorobenzenes exported to the Humber was 133 kg/year. This is the first study to calculate chlorobenzene fluxes to the North Sea from a UK catchment.

Journal Article↗

An experimental and numerical study of the thermal oxidation of chlorobenzene.

A combustion-driven flow reactor was used to examine the formation of chlorinated and non-chlorinated species from the thermal oxidation of chlorobenzene under post-flame conditions. Temperature varied from 725 to 1000 K, while the equivalence ratio was held constant at 0.5. Significant quantities of chlorinated intermediates, vinyl chloride and chlorophenol, were measured. A dominant C-Cl scission destruction pathway seen in pyrolytic studies was not observed. Instead, hydrogen-abstraction reactions prevailed, leading to high concentrations of chlorinated byproducts. The thermal oxidation of benzene was also investigated for comparison. Chemical kinetic modeling of benzene and chlorobenzene was used to explore reaction pathways. Two chlorobenzene models were developed to test the hypothesis that chlorobenzene oxidation follows a CO-expulsion breakdown pathway similar to that of benzene. For the temperatures and equivalence ratio studied, hydrogen abstraction by hydroxyl radicals dominates the initial destruction of both benzene and chlorobenzene. Chlorinated byproducts (i.e., chlorophenol and vinyl chloride) were formed from chlorobenzene oxidation in similar quantities and at similar temperatures to their respective analogue formed during benzene oxidation (i.e., phenol and ethylene).

Journal Article↗

Mechanisms for modification of bromobenzene hepatotoxicity by coadministered toluene and chlorobenzene.

Hepatotoxicity of bromobenzene (2 mmole/kg) in combination with toluene or chlorobenzene (4 mmole/kg each) were studied in vivo on the basis of GPT elevation and histological examinations. Both toluene and chlorobenzene suppressed bromobenzene hepatotoxicity 24 hr after the treatment, and chlorobenzene dramatically potentiated the toxicity at 48 hr. The glutathione level became lower at 12 hr and recovered at 24 hr when bromobenzene was given alone. The recovery delayed until 48 hr when chlorobenzene was coadministered. In experiments in vitro with microsomes from phenobarbital-pretreated rats, both toluene and chlorobenzene at 0.6 mM inhibited p-bromophenol formation noncompetitively but had no effect on o-isomer formation. Multiple factors may determine overall hepatotoxicity in combined exposure; bromobenzene hepatotoxicity will be suppressed in the early phase owing to metabolic inhibition of 3,4-epoxidation, but potentiated later because of delayed recovery in the glutathione level. A time-saving yet reliable assay system with an ECD-gas chromatograph was developed for bromobenzene metabolism study.

Animals↗

Microorganisms degrading chlorobenzene via a meta-cleavage pathway harbor highly similar chlorocatechol 2,3-dioxygenase-encoding gene clusters.

Pseudomonas putida GJ31 harbors a degradative pathway for chlorobenzene via meta-cleavage of 3-chlorocatechol. Pseudomonads using this route for chlorobenzene degradation, which was previously thought to be generally unproductive, were isolated from various contaminated environments of distant locations. The new isolates, Pseudomonas fluorescens SK1 (DSM16274), Pseudomonas veronii 16-6A (DSM16273), Pseudomonas sp. strain MG61 (DSM16272), harbor a chlorocatechol 2,3-dioxygenase (CbzE). The cbzE-like genes were cloned, sequenced, and expressed from the isolates and a mixed culture. The chlorocatechol 2,3-dioxygenases shared 97% identical amino acids with CbzE from strain GJ31, forming a distinct family of catechol 2,3-dioxygenases. The chlorocatechol 2,3-dioxygenase, purified from chlorobenzene-grown cells of strain SK1, showed an identical N-terminal sequence with the amino acid sequence deduced from cloned cbzE. In all investigated chlorobenzene-degrading strains, cbzT-like genes encoding ferredoxins are located upstream of cbzE. The sequence data indicate that the ferredoxins are identical (one amino acid difference in CbzT of strain 16-6A compared to the others). In addition, the structure of the operon downstream of cbzE is identical in strains GJ31, 16-6A, and SK1 with genes cbzX (unknown function) and the known part of cbzG (2-hydroxymuconic semialdehyde dehydrogenase) and share 100% nucleotide sequence identity with the entire downstream region. The current study suggests that meta-cleavage of 3-chlorocatechol is not an atypical pathway for the degradation of chlorobenzene.

Aldehyde Oxidoreductases↗

Effects of four chlorobenzenes on serum sex steroids and hepatic microsome enzyme activities in crucian carp, Carassius auratus.

Four chlorobenzenes (chlorobenzene, 1,3-dichlorobenzene, 1,4-dichlorobenzene, p-chloro-methylbenzene) were administrated to the crucian carps (Carassius auratus) by peritoneal injections in the laboratory for 30 days. Serum testosterone and 17 beta-estradiol concentrations were detected using radioimmunology assay (RIA), and the activities of two hepatic microsome enzymes, glutathione s-transferase (GST) and UDP-glucuronosyltransferase (UDPGT), were measured using the modified methods as described by Habig and Owens. Results showed that the four chlorobenzenes caused significant increases in serum testosterone concentration in the crucian carps (P < 0.05) compared to the controls, but they caused no significant effect on 17 beta-estradiol level. All test chemicals caused a change in hepatic GST activity in crucian carps, with significant increases in enzyme activity (P < 0.05). Chlorobenzene, 1,3-dichlorobenzene and p-chloro-methylbenzene resulted in a marked inhibition to UDPGT activity in crucian carp (P < 0.05) except 1,4-dichlorobenzene. The changes in hepatic microsome enzyme activities may have resulted in the alterations of serum sex steroids levels in the crucian carps. The results indicated that these four chlorobenzenes may result in the changes of endocrine functions and may affect the reproductive success of this and other species.

Animals↗

Isotopically labeled chlorobenzenes as probes for the mechanism of cytochrome P-450 catalyzed aromatic hydroxylation.

Noncompetitive and competitive intermolecular deuterium isotope effects were measured for the cytochrome P-450 catalyzed hydroxylation of a series of selectively deuterated chlorobenzenes. An isotope effect of 1.27 accompanied the meta hydroxylation of chlorobenzene-2H5 as determined by two totally independent methods (EC-LC and GC-MS assays). All isotope effects associated with the meta hydroxylation of chlorobenzenes-3,5-2H2 and -2,4,6-2H3 were approximately 1.1. In contrast, competitive isotope studies on the ortho and para hydroxylation of chlorobenzenes-4-2H1, -3,5-2H2, and -2,4,6-2H3 resulted in significant inverse isotope effects (approximately 0.95) when deuterium was substituted at the site of oxidation whereas no isotope effect was observed for the oxidation of protio sites. These results eliminate initial epoxide formation and initial electron abstraction (charge transfer) as viable mechanisms for the cytochrome P-450 catalyzed hydroxylation of chlorobenzene. The results, however, can be explained by a mechanism in which an active triplet-like oxygen atom adds to the pi system in a manner analogous to that for olefin oxidation. The resulting tetrahedral intermediate can then rearrange to phenol directly or via epoxide or ketone intermediates.

Animals↗

Development of a physiologically based pharmacokinetic model for chlorobenzene in F-344 rats.

A physiologically based pharmacokinetic (PBPK) model to describe the absorption, distribution, metabolism, and elimination of chlorobenzene in rats was developed. Partition coefficients were experimentally determined in rat tissues and blood samples using an in vitro vial equilibration technique. These solubility ratios were in agreement with previous reports. The in vivo metabolism of chlorobenzene was evaluated using groups of three F344 male rats exposed to initial chlorobenzene concentrations ranging from 82 to 6750 ppm in a closed, recirculating gas uptake system. An optimal fit of the family of uptake curves was obtained by adjusting Michaelis-Menten metabolic constants, K(m) (affinity) and Vmax (capacity), using the PBPK model. At the highest chamber concentration, the uptake curve could not be modeled without the addition of a first-order (Kfo) metabolic pathway. Pretreatment with pyrazole, an inhibitor of oxidative microsomal metabolism, had no impact on the slope of the uptake curve. The completed PBPK model was evaluated against real-time exhaled breath data collected from rats receiving either an intraperitoneal (i.p.) injection or oral gavage dose of chlorobenzene in corn oil. Exhaled breath profiles were evaluated and absorption rates were determined. Development of the chlorobenzene PBPK model in rats is the first step toward future extrapolations to apply to humans.

Absorption↗