Metabolism of pentachlorophenol in vivo and in vitro

An unexpected antioxidant and redox activity for the classic copper-chelating drug penicillamine

Penicillamine has been widely-used clinically as a copper-chelating drug for the treatment of copper-overload in Wilson's disease. In this study, we found that penicillamine provided marked protection against cytotoxicity induced by tetrachlorohydroquinone (TCHQ), a major toxic metabolite of the well-known wood preservative pentachlorophenol, while other classic copper-chelating agents do not. We found, unexpectedly, that both TCHQ autooxidation and tetrachlorosemiquinone radical (TCSQ^•-) formation were remarkably delayed by penicillamine. Further investigation showed that TCSQ^•- was reduced back to TCHQ by penicillamine, with the concurrent formation of its corresponding disulfide. These data demonstrated that the protection by penicillamine against TCHQ-induced toxicity was not due to its classic Cu-chelating property, but rather to its reduction of the reactive TCSQ^•- to the much less-reactive TCHQ. This is the first report of an unexpected antioxidant and redox activity for penicillamine, which might prove highly relevant to its biological activities.

Characterization of TCHQ-induced genotoxicity and mutagenesis using the pSP189 shuttle vector in mammalian cells

Tetrachlorohydroquinone (TCHQ) is a major toxic metabolite of the widely used wood preservative, pentachlorophenol (PCP), and it has also been implicated in PCP genotoxicity. However, the underlying mechanisms of genotoxicity and mutagenesis induced by TCHQ remain unclear. In this study, we examined the genotoxicity of TCHQ by using comet assays to detect DNA breakage and formation of TCHQ-DNA adducts. Then, we further verified the levels of mutagenesis by using the pSP189 shuttle vector in A549 human lung carcinoma cells. We demonstrated that TCHQ causes significant genotoxicity by inducing DNA breakage and forming DNA adducts. Additionally, DNA sequence analysis of the TCHQ-induced mutations revealed that 85.36% were single base substitutions, 9.76% were single base insertions, and 4.88% were large fragment deletions. More than 80% of the base substitutions occurred at G:C base pairs, and the mutations were G:C to C:G, G:C to T:A or G:C to A:T transversions and transitions. The most common types of mutations in A549 cells were G:C to A:T (37.14%) and A:T to C:G transitions (14.29%) and G:C to C:G (34.29%) and G:C to T:A (11.43%) transversions. We identified hotspots at nucleotides 129, 141, and 155 in the supF gene of plasmid pSP189. These mutation hotspots accounted for 63% of all single base substitutions. We conclude that TCHQ induces sequence-specific DNA mutations at high frequencies. Therefore, the safety of using this product would be carefully examined.

Pentachlorophenol and other chlorinated phenols are substrates for human hydroxysteroid sulfotransferase hSULT2A1

Pentachlorophenol (PCP) is a persistent chemical contaminant that has been extensively investigated in terms of its toxicology and metabolism. Similar to PCP, other chlorinated phenol derivatives are also widely present in the environment from various sources. Even though some of the chlorine-substituted phenols, and particularly PCP, are well-known inhibitors of phenol sulfotransferases (SULTs), these compounds have been shown to undergo sulfation in humans. To investigate the enzymatic basis for sulfation of PCP in humans, we have studied the potential for PCP as well as the mono-, di-, tri-, and tetra-chlorinated phenols to serve as substrates for human hydroxysteroid sulfotransferase, hSULT2A1. Our results show that all of these compounds are substrates for this isoform of sulfotransferase, and the highest rates of sulfation are obtained with PCP, trichlorophenols, and tetrachlorophenols. Much lower rates of sulfation were obtained with isomers of monochlorophenol and dichlorophenol as substrates for hSULT2A1. Thus, the sulfation of polychlorinated phenols catalyzed by hSULT2A1 may be a significant component of their metabolism in humans.

Ambident reactivity of phenoxyl radicals in DNA adduction

Phenols are a class of compounds that can create beneficial effects in vivo owing to their antioxidant properties (through radical scavenging), or they can display hazardous effects owing to their pro-oxidant properties. The mechanism by which phenols act as pro-oxidants stems from their one-electron oxidation into reactive phenoxyl radicals by peroxidase enzymes or redox-active transition metals. In the presence of thiols and molecular oxygen, these reactive phenoxyl radicals stimulate an oxidative stress and cause oxidative damage to biomolecules, which is proposed to contribute to the occurrence of cancer in peroxidase rich tissues. Recent results from our laboratory show that certain phenoxyl radicals can also react directly with the C-8 site of deoxyguanosine to afford oxygen and carbon bonded adducts. This reactivity is consistent with the ambident (oxygen vs. C attachment) electrophilicity of phenoxyl radicals coupled with the susceptibility of the C-8 site of deoxyguanosine to radical attachment. Given that formation of covalent DNA adducts is regarded as the initiation event in the carcinogenic process, C-8 deoxyguanosine adducts of phenolic toxins are expected to contribute greatly to peroxidase driven toxic effects of phenolic xenobiotics. The focus of this review is the role of phenoxyl radicals in direct reactions with DNA and the use of Brown σ+ values to predict their reactivity.Key words: DNA adduction, phenoxyl radicals, chlorophenols, ochratoxin A, deoxyguanosine.

Characterization of metabolic activation of pentachlorophenol to quinones and semiquinones in rodent liver

Pentachlorophenol (PCP), a widely used biocide, induces liver tumors in mice but not in rats. Metabolic activation of PCP to chlorinated quinones and semiquinones in liver cytosol from Sprague-Dawley rats and B6C3F1 mice was investigated in vitro (1) with microsomes in the presence of either beta-nicotinamide adenine dinucleotide phosphate (NADPH) or cumene hydroperoxide (CHP), (2) with CHP in the absence of microsomes, and (3) with horseradish peroxidase (HRP) and H2O2. Mono-S- and multi-S-substituted adducts of tetrachloro-1,4-benzoquinone (Cl4-1,4-BQ) and Cl4-1,2-BQ and their corresponding semiquinones [i.e. tetrachloro-1,4-benzosemiquinone (Cl4-1,4-SQ) and tetrachloro-1,2-benzosemiquinone (Cl4-1,2-SQ)] were measured by gas chromatography-mass spectrometry (GC-MS). Qualitatively, the metabolites of PCP were the same in both rats and mice for all activation systems. Induction of PCP metabolism by either 3MC or PB-treated microsomes was observed in NADPH- but not in CHP-supported systems. In rats, the amount of induction was comparable with either 3MC or PB. 3MC was a stronger inducer than PB in mice and also induced a greater amount of metabolism than in rats. This suggests that induction of specific P450 isozymes may play a role in the toxicity of PCP to mice. Both HRP/H2O2 and CHP led to production of the full spectrum of chlorinated quinones and semiquinones, confirming the direct oxidation of PCP. CHP (with or without microsomes) converted PCP into much greater quantities of quinones and semiquinones than did microsomal P450/NADPH or HRP/H2O2 in both species. This implies that, under conditions of oxidative stress, endogenous lipid hydroperoxides may increase PCP metabolism sufficiently to enhance the toxicity and carcinogenicity of PCP.

Protection by desferrioxamine and other hydroxamic acids against tetrachlorohydroquinone-induced cyto- and genotoxicity in human fibroblasts

Tetrachlorohydroquinone (TCHQ) has been identified as a major toxic metabolite of the widely used wood preservative pentachlorophenol and has also been implicated in its genotoxicity. We have recently demonstrated that protection by the trihydroxamate iron chelator desferrioxamine (DFO) on TCHQ-induced single-strand breaks in isolated DNA was not the result of its chelation of iron but rather of its efficient scavenging of the reactive tetrachlorosemiquinone (TCSQ) radical. In this study, we extended our research from isolated DNA to human fibroblasts. We found that DFO provided marked protection against both the cyto- and genotoxicity induced by TCHQ in human fibroblasts when it was incubated simultaneously with TCHQ. Pretreatment of the cells with DFO followed by washing also provided marked protection, although less efficiently compared with the simultaneous treatment. Similar patterns of protection were also observed for three other hydroxamic acids (HAs): aceto-, benzo-, and salicylhydroxamic acid. Dimethyl sulfoxide, an efficient hydroxyl radical scavenger, provided only partial protection even at high concentrations. In vitro studies showed that the HAs tested effectively scavenged the reactive TCSQ radical and enhanced the formation of the less reactive and less toxic 2,5-dichloro-3, 6-dihydroxy-1,4-benzoquinone (chloranilic acid). The results of this study demonstrated that the protection provided by DFO and other HAs against TCHQ-induced cyto- and genotoxicity in human fibroblasts is mainly through scavenging of the observed reactive TCSQ radical and not through prevention of the Fenton reaction by the binding of iron in a redox-inactive form.

Comparative biotransformation of hexachlorobenzene and hexafluorobenzene in relation to the induction of porphyria

The porphyrinogenic action of hexafluorobenzene was investigated and compared to that of hexachlorobenzene. Metabolite patterns in the urine of exposed rats were determined to quantify the extent of metabolism through cytochrome P450 catalysed oxidation and glutathione conjugation. Results obtained demonstrate an almost similar extent of formation of phenolic metabolites. However, in the urine of hexachlorobenzene exposed rats significantly higher levels of the N-acetyl-S-(pentahalophenyl)cysteine were observed than in the urine of hexafluorobenzene exposed rats. Hexafluorobenzene exposure did not result in induction of porphyria, whereas exposure to hexachlorobenzene did result in significantly elevated levels of urinary as well as liver porphyrins. Together these results indicate that if the reactive intermediate is indeed formed in the cytochrome P450 catalysed initial oxidative dehalogenation, the extent of its formation as well as its subsequent reactivity and reaction pathways vary with the type of the halogen substituents. Furthermore, the results seem to indicate that the extent of metabolism of hexahalogenated benzenes into urinary metabolites resulting from glutathione conjugation is a better indication of their porphyrinogenic action than their extent of metabolism to phenolic metabolites. Two explanations for this observation are presented.

The pentachlorophenol metabolite tetrachloro-p-hydroquinone induces the formation of 8-hydroxy-2-deoxyguanosine in liver DNA of male B6C3F1 mice

Tetrachloro-p-hydroquinone (TCHQ), the major metabolite of pentachlorophenol (PCP) in mammalian systems, is known to autoxidize to its semiquinone radical under physiological conditions. In this way, PCP could present a potent source of reactive oxygen species (ROS) during metabolization. ROS contribute to numerous modifications of DNA. Formation of 8-hydroxy-2'-deoxyguanosine (8-OH-dG), a product of hydroxyl radical attack on DNA, is monitored as a marker of a major genetic lesion induced by agents which produce oxygen radicals. We studied the properties of TCHQ for the induction of oxidative DNA damage in vivo. Male B6C3F1 mice were fed a diet containing TCHQ for 2 and 4 weeks. These experiments resulted in an enhancement of about 50% of the 8-OH-dG portion in liver DNA after administration of 300 mg TCHQ/kg body wt./day for 2 weeks. Control levels did not change over the periods of 2 and 4 weeks, respectively. In contrast to these results, a single i.p. injection of 20 or 50 mg/kg body wt. did not affect the 8-OH-dG content after 6 and 24 h, respectively. These data may support a possible contribution of ROS to the carcinogenicity of PCP.

Role of active oxygen species in DNA damage by pentachlorophenol metabolites

Pentachlorophenol (PCP) has been shown to be carcinogenic for mice, although it does not seem to be mutagenic in bacterial test systems. In this study, the mechanism of DNA damage by PCP metabolites in the presence of metals was investigated with a DNA sequencing technique using 32P-labeled DNA fragments and with an electrochemical detector coupled to an HPLC. The metabolite tetrachlorohydroquinone (TCHQ) caused DNA damage in the presence of Cu(II) but not in the presence of either Mn(II) or Fe(III). TCHQ plus Cu(II) frequently induced piperidine-labile sites at thymine residues and guanine residues. The most preferred sites were the thymine residues of the 5'-GTC-3' sequence. TCHQ increased 8-oxo-7,8-dihydro-2'-deoxyguanosine in calf thymus DNA in the presence of Cu(II). Typical OH scavengers showed no inhibitory effects on TCHQ- plus Cu(II)-induced DNA damage. Bathocuproine and catalase inhibited DNA damage, suggesting that Cu(I) and H2O2 have important roles in the production of active species causing DNA damage. Tetrachloro-p-benzoquinone (TCBQ) alone did not induce DNA damage in the presence of Cu(II), but addition of NADH induced DNA cleavage even in the absence of NADH-FMN oxidoreductase. UV-visible and ESR spectroscopies have demonstrated that TCHQ is rapidly autoxidized into semiquinone even in the absence of metal ions, indicating that the semiquinone radical itself is not the main active species inducing DNA damage. These results suggest that the semiquinone radical produced by the autoxidation of TCHQ and/or the reduction of TCBQ by NADH reacts with dioxygen to form superoxide and subsequently H2O2, which is activated by transition metals to cause DNA damage.

Toxicokinetics and biotransformation of pentachlorophenol in the sea urchin (Strongylocentrotus purpuratus)

1. The toxicokinetics and biotransformation of pentachlorophenol (PCP) were determined in the purple sea urchin (Strongylocentrotus purpuratus). 2. In a static chamber, urchins (n = 9) were individually exposed to 50 micrograms/l of [U-14C]PCP for 24 h to determine bioconcentration and the absorption rate constant (Ka), elimination rate constant (Ke), and elimination half-life (t1/2). Determination was by direct quantitation of radioactivity in the exposure water. 3. After exposure, urchins were placed in a flow-through chamber for 24 h to allow depuration of retained residues, which were identified by hplc and quantified by lsc. The Ka and Ke, calculated using a simplified model, were 0.12 +/- 0.06 h and 0.43 +/- 0.22 h, respectively, whilst the 24-h total concentration factor was 316.3 +/- 209.7, and the t1/2 was 1.6 +/- 0.8 h. 4. Whereas urchins depurated 40.6% of retained residues, only a small amount of PCP was excreted unchanged (17.0%), as the more polar conjugates pentachlorophenyl-beta-D-glucoside (72.4%) and pentachlorophenylsulphate (10.6%) were also formed.

Comparison of the urinary metabolite profiles of hexachlorobenzene and pentachlorobenzene in the rat

The urinary metabolite profile of hexachlorobenzene (HCB) and pentachlorobenzene (PCBz) in the rat is compared after dietary exposure for 13 weeks. Both HCB and PCBz are oxidized to pentachlorophenol (PCP) and tetrachlorohydroquinone (TCHQ), which were the only two mutual metabolites formed. Additional urinary metabolites of HCB are N-acetyl-S(pentachlorophenyl)cysteine (PCTP-NAC), which appeared to be quantitatively the most important product, and mercaptotetrachlorothioanisole (MTCTA), which was excreted as a glucuronide. PCBz is more extensively metabolized to the major metabolites 2,3,4,5-tetrachlorophenol (TCP), mercaptotetrachlorophenol (MTCP) and the glucuronide of pentachlorothiophenol (PCTP), and the minor metabolites methylthiotetrachlorophenol (MeTTCP), hydroxytetrachlorophenyl sulphoxide (HTCPS), and bis(methylthio)-trichlorophenol (bis-MeTTriCP). The biotransformation of HCB and PCBz was modulated by selective inhibition of cytochrome P450IIIA in rats which received combined treatment of HCB or PCBz with triacetyloleandomycin (TAO). Rats receiving this diet had a strongly diminished excretion of both PCP and TCHQ, as compared to rats fed HCB or PCBz alone, indicating the involvement of P450IIIA in the oxidation of both compounds. However, the excretion of 2,3,4,5-TCP was not diminished by co-treatment of rats with PCBz and TAO, indicating that: (i) the oxidation of PCBz to PCP and 2,3,4,5-TCP does not proceed via a common intermediate; and (ii) oxidation of PCBz to 2,3,4,5-TCP is not mediated by P450IIIA. Co-treatment of rats with PCBz and TAO had a differential effect on the excretion of sulphur-containing metabolites, resulting in a decrease in the excretion of PCTP glucuronide, whereas no change was observed in the excretion of MTCP, as compared to rats receiving PCBz alone. The observed differences in HCB and PCBz metabolites clearly deserve further in vitro studies to elucidate their origin.

Toxicokinetics and biotransformation of pentachlorophenol in the topsmelt (Atherinops affinis)

The toxicokinetics and biotransformation of pentachlorophenol (PCP) were determined in the topsmelt (Atherinops affinis). In a static system, topsmelt (n = 9) were exposed to 50 micrograms/L of [U-14C]PCP for 24 hours to determine the absorption rate constant (Ka), the whole-body bioconcentration (at steady-state conditions), the elimination rate constant (Ke), and the elimination half-life (t1/2). Kinetics were determined by direct quantitation of radioactivity in the exposure water. Following exposure, fish were placed in a flow-through metabolism chamber for 24 hours to allow depuration of retained residues, which were collected on XAD-4 resin. Excreted residues were identified and quantified by high-pressure liquid co-chromatography, fraction collection, and liquid scintillation counting. The Ka and Ke, calculated using a simplified model, were 0.012 +/- 0.005/h and 0.014 +/- 0.003/h, respectively, while the 24 hour total concentration factor was 278.0 +/- 182.0 and the t1/2 was 52.7 +/- 11.2. During 24 hours of exposure to clean seawater, topsmelt depurated 32.9% of retained residues, and while PCP was primarily excreted unchanged (64.9%), significant amounts of both pentachlorophenylsulfate (18.9%) and pentachloro-beta-D-glucuronide (16.2%) were also formed.

Induction of micronuclei in V79 Chinese hamster cells by tetrachlorohydroquinone, a metabolite of pentachlorophenol

Tetrachlorohydroquinone, a metabolite of the fungicide pentachlorophenol, induced significant dose-related increases in micronuclei in V79 Chinese hamster cells without exogenous metabolic activation. The lowest observed effective dose was 10 microM, where the relative survival was about 62%. At the highest dose tested, 20 microM, the relative survival was about 8% and the frequency of cells with micronuclei was about 6 times the solvent control frequency. The induction of micronuclei by tetrachlorohydroquinone was significantly inhibited by the hydroxyl radical scavenger dimethyl sulfoxide at 5% (v/v).

Disposition and biotransformation of pentachlorophenol in the red abalone (Haliotis rufescens)

1. The disposition and biotransformation of pentachlorophenol (PCP) in the red abalone (Haliotis rufescens) have been determined. 2. In a flow-through system, three abalones were exposed to 1.2 mg/l of [U-14C]PCP for 5 h to determine bioconcentration and tissue distribution. Retained residues were quantified from radioactivity, while excreted residues were identified and quantified by h.p.l.c. and determination of radioactivity. 3. The 5-h total concentration factor ranged from 16.0 to 21.5; individual tissue concentrations ranged from 133.4 nmol/g in gill to 17.5 nmol/g in gonad. Due to its large size, the foot muscle received the largest amount of total retained residue (47.4%). 4. During a 13-h recovery period the abalones depurated 72.2% of retained residues; however, residue concentration in gonad increased over 100%. PCP was primarily excreted unchanged (89.3%), but small amounts of pentachloro-beta-D-glucoside (7.9%), pentachloroanisole (1.3%), pentachlorophenylsulphate (0.9%), and tetrachloro-p-hydroquinone (0.6%) were also formed.

Pentachlorophenol toxicokinetics after intravenous and oral administration to rat

1. The toxicokinetics of pentachlorophenol (PCP) were studied in rats. Doses of 2.5 mg/kg were given i.v. (bolus, five rats) and orally (gastric intubation, five rats). Concentrations in plasma, urine and faeces were measured by capillary g.l.c. with electron-capture detection. 2. After i.v. administration, the clearance and volume of distribution at steady state were 0.026 +/- 0.003 l/h per kg and 0.25 +/- 0.02 l/kg, respectively. These two parameters exhibit low inter-rat variability (coefficients of variation less than 15%). The half-life of the initial decline of PCP plasma concn. was less than 1.3 h, while the second phase half-life was 7.11 +/- 0.87 h. 3. After oral administration the peak plasma concn. (7.3 +/- 2.8 micrograms/ml) occurred between 1.5 and 2 h and absorption was complete (bioavailability = 0.91-0.97). No distinct distribution phase was observed and the elimination half-life was 7.54 +/- 0.44 h. 4. PCP clearance is essentially metabolic since only 5.3 +/- 0.2% dose is eliminated unchanged by the kidney. About 60% dose was recovered in urine, mainly as conjugated PCP and conjugated tetrachlorohydroquinone (TCHQ). 5. For both routes of administration, about 10% dose was recovered in faeces as PCP and/or metabolites, which indicates that biliary excretion contributes to total elimination.

Induction of mutation in V79 Chinese hamster cells by tetrachlorohydroquinone, a metabolite of pentachlorophenol

Tetrachlorohydroquinone (TCHQ) and tetrachlorocatechol (TCC), two metabolites of the environmental mutagen and carcinogen pentachlorophenol, were tested without exogenous activation in V79 Chinese hamster cells for the induction of mutation at the hypoxanthine phosphoribosyl transferase (HPRT) locus to 6-thioguanine resistance (TGr) and at the Na/K-ATPase locus to ouabain resistance (OuaR). Treatment was for 24 h at 37 degrees C. TCHQ produced statistically significant increases in the frequency of TGr mutants. The lowest observed effective dose (LOED) was 20 microM, where the relative cloning efficiency was 63%. The relationship between the dose of TCHQ and the frequency of TGr mutants was approximately linear over the range of 0-60 microM with an estimated slope (+/- 95% confidence limits) of 1.1 +/- 0.3 mutants per 10(6) clonable cells per microM. At the highest tested dose of TCHQ, 60 microM, the relative cloning efficiency was reduced to 7%. In contrast to TCHQ, TCC was unable to induce TGr mutants at doses up to 120 microM. The relative cloning efficiency at this dose was 5%. Both TCHQ and TCC were unable to induce OuaR mutants. The results suggest that TCHQ is at least partly responsible for the genotoxic activity of pentachlorophenol. TCHQ can produce reactive oxygen species, which may cause large genetic damage such as deletions, resulting in mutation to TGr but not to OuaR.

Effects of hexachlorobenzene and its metabolites pentachlorophenol and tetrachlorohydroquinone on serum thyroid hormone levels in rats

Effects of administration of equimolar doses of hexachlorobenzene (HCB) and its metabolites pentachlorophenol (PCP) and tetrachlorohydroquinone (TCHQ) on serum thyroxine (TT4) and triiodothyronine (TT3) levels in rats were studied. Furthermore, it was investigated whether the observed effects were related to the serum levels of HCB or PCP. Rats received either corn oil (controls) or HCB, PCP or TCHQ in a single equimolar intraperitoneal dose of 0.056 mmol/kg. Results indicated that HCB did not alter serum TT4 and TT3 levels for a period up to 96 h after dosing. In contrast, PCP and TCHQ were both capable of reducing serum TT4 levels with a maximum effect between 6 and 24 h after exposure. TCHQ was more effective in repressing TT3 than TT4 blood levels. Dose-response experiments were carried out in order to obtain insight into the sensitivity of the observed effects. Rats received different doses of PCP or TCHQ intraperitoneally. The reductions of TT4 levels by PCP were inversely related to serum PCP levels in exposed animals, based on the toxicokinetics and dose-response profiles. Furthermore, PCP serum levels after HCB administration appeared too low to cause an effect. The results of this study indicate that not HCB itself, but rather its metabolites PCP and TCHQ may be involved in reduced serum thyroid hormone levels after HCB administration.

Interactions of halogenated industrial chemicals with transthyretin and effects on thyroid hormone levels in vivo

Previous results in experimental systems have suggested that hydroxylated PCBs may decrease thyroid hormone levels through associative interaction with transthyretin. In the present paper it was investigated whether this property was also shared by various industrial chemicals, mainly pesticides. In total, 65 compounds from 12 chemical groups were analyzed for direct interference with the T4 binding site of transthyretin using a competitive binding assay. Sixty per cent of the compounds were competitive at a concentration level of 100 microM. Relatively strong interactions were observed by several chlorophenols, chlorophenoxy acids and nitrophenols, as well as by individual compounds such as hexachlorobenzene, dicofol, bromoxynil and tetrachlorohydroquinone. Examples from these chemical groups, e.g. pentachlorophenol, 2,4-dichlorophenoxybutyric acid, dinoseb and bromoxynil, also reduced plasma TT4 levels in rats. In addition, bromoxynil decreased plasma TT3 levels. The results suggest the existence of a number of halogenated industrial chemicals with a potential for lowering plasma thyroid hormone levels through interference with hormone transport carriers.

The induction of DNA strand breaks and formation of semiquinone radicals by metabolites of 2,4,5-trichlorophenol

The industrial pollutant 2,4,5-trichlorophenol (2,4,5-TCP) was metabolized with postmitochondrial liver fraction from Aroclor-1254 induced rats. The generated metabolites induced single strand breaks in PM2 DNA. Among the metabolites produced are the 3,4,6-trichlorocatechol (TCC) and the 2,5-dichlorohydro-quinone (DCH), whereby the induction of DNA scission by DCH was approximately one hundred times greater than that of TCC. In the 2,4,5-TCP metabolization mixture radicals were observed by ESR. They were identified as the semiquinones of TCC and DCH. ESR studies confirmed that both TCC and DCH autoxidize in aqueous solution to their semiquinone radicals. The involvement of reactive oxygen species in the DNA strand scission was demonstrated by using DMSO, SOD, and catalase as scavengers. Inhibition of strand breaks with the scavenger enzymes did not give homogeneous results for DCH and TCC. This indicated that the directly damaging species might be different for DCH and TCC.

The effect of pentachlorophenol and its metabolite tetrachlorohydroquinone on cell growth and the induction of DNA damage in Chinese hamster ovary cells

It is shown that p-tetrachlorohydroquinone (TCH), the metabolite of the environmental chemical pentachlorophenol (PCP), is more toxic to cultured CHO cells than PCP, and that it causes DNA single-strand breaks and/or alkali-labile sites at concentrations of 2-10 microgram/ml as demonstrated by the alkaline elution technique.

Short-term effects of chlorophenols on the function and viability of primary cultured rat hepatocytes

Primary cultured rat hepatocytes were used as an experimental model to detect adverse effects of five chlorophenols (CP) in vitro (penta-CP, 2,3,4,5-tetra-CP, 2,4,5,-tri-CP, 2,4-di-CP, and 4-mono-CP). Monolayer cultures were exposed to the test compounds for 1 h, and concentration-response curves were established with respect to the effects on phase I and phase II metabolism of 7-ethoxycoumarin (7-EC) and on cellular ATP content. All CP tested inhibited the O-dealkylation of 7-EC, with half-maximum effective concentrations (EC50) ranging from about 36 microM for the three highest chlorinated phenols to 215 microM for 4-mono-CP, which proved to be least effective. The subsequent conjugation of the primary metabolite 7-hydroxycoumarin was even more sensitive towards CP exposure than the O-deethylation process. The concentrations which reduced the percentage of conjugated metabolite to 50% of the respective control cultures ranged from 7 microM for penta-CP to 48 microM for 4-mono-CP. Treatment of cultured hepatocytes with CP additionally resulted in a depletion of cellular ATP at EC50 concentrations ranging from 6 microM for penta-CP to 1330 microM for 4-mono-CP. Cellular viability, as measured by the leakage of lactate dehydrogenase from the cells, was not affected by any of the CP within the 1-h exposure period.

The in vitro metabolites of 2,4,6-trichlorophenol and their DNA strand breaking properties

The carcinogenic compound 2,4,6-trichlorophenol (2,4,6-TCP) was incubated with rat liver S-9 fraction. Three metabolites were identified: 2,6-dichloro-1,4-hydroquinone (DHQ), and two isomers of hydroxypentachlorodiphenyl ether (OH-Cl5-DPE). The latter are probably products of microsomal .OH radical attack on the trichlorophenol molecule forming phenoxy free radicals. These would undergo dimerizations with other molecules present in solution. The 2,6-dichloro-1,4-semiquinone free radical was identified by ESR spectroscopy. It is formed at physiological conditions in phosphate buffer at pH 7.2 and 7.8, with a more intensive signal at the more alkaline pH. The formation is probably due to the autoxidation of the corresponding hydroquinone. Incubation of a mixture of metabolites with PM2 DNA at pH 7.2 resulted in single strand breaks. Addition of catalase and dimethylsulfoxide (DMSO) inhibited the DNA strand scission. It was concluded that reactive oxygen species (ROS), produced during the formation of the semiquinone radical, were responsible for the observed DNA damage. The significance of the ROS and the semiquinone free radical is discussed in view of the reported tumorgenicity of 2,4,6-TCP in rats and mice.

Identification of multiple glutathione S-transferases from Daphnia magna

1. Six anionic glutathione S-transferases (GST) were purified from the crustacean, Daphnia magna, by means of affinity chromatography, that are responsible for ca. 40% of cytosolic GST activity. 2. Electrophoresis in the presence of sodium dodecyl sulfate (SDS) revealed the presence of three proteins, with molecular weights of 27,500, 28,000, and 30,200. 3. Separation under nondenaturing conditions revealed six proteins, all of which exhibited GST activity, with molecular weights ranging from 55,000 to 61,700. 4. Ethacrynic acid is a competitive inhibitor of activity towards CDNB of all six GSTs, binding each with similar affinities. 5. Chlorinated phenols are also competitive inhibitors of the enzyme, with the degree of inhibition being directly correlated with the lipophilicity of the compounds. 6. Analysis of inhibition of separated isoforms reveals that form 4 is most strongly inhibited by these chlorinated phenols, with forms 5 and 6 being inhibited to a lesser degree.

The microsomal metabolism of pentachlorophenol and its covalent binding to protein and DNA

The microsomal metabolism of pentachlorophenol (PCP) was investigated, with special attention to the conversion dependent covalent binding to protein and DNA. The two metabolites detected were tetrachloro-1,2- and tetrachloro-1,4-hydroquinone. Microsomes from isosafrole (ISF)-induced rats were by far the most effective in catalyzing the reaction: the rate of conversion was increased 7-fold over control microsomes. All other inducers tested (hexachlorobenzene (HCB), phenobarbital (PB) and 3-methylcholanthrene (3MC) gave 2--3-fold increases over control. There are indications that the 1,2- and 1,4-isomers are produced in different ratio's by various cytochrome P-450 isoenzymes: Microsomes from PB- and HCB-treated rats produced the tetrachloro-1,4- and tetrachloro-1,2-hydroquinone in a ratio of about 2, while microsomes from rats induced with 3 MC and ISF showed a ratio of about 1.3. When PCP was incubated with microsomes from rats treated with HCB, a mixed type inducer of P-450, the ratio between formation of the 1,4- and 1,2-isomers decreased with increasing concentration of PCP, suggesting the involvement of at least two P-450 isoenzymes with different Km-values. The overall apparent Km-value for HCB-microsomes was 13 microM both for the formation of the soluble metabolites and the covalent binding to microsomal protein, suggesting both stem from the same reaction. The covalent binding could be inhibited by ascorbic acid and this inhibition was accompanied by an increase in formation of tetrachlorohydroquinones (TCHQ). Although a large variation was observed in rates of conversion between microsomes treated with different (or no) inducers, the rate of covalent binding to microsomal protein was remarkably constant. A conversion-dependent covalent binding to DNA was observed in incubations with added DNA which was 0.2 times the amount of binding to protein (37 pmol/mg DNA).

The microsomal metabolism of hexachlorobenzene. Origin of the covalent binding to protein

The microsomal metabolism of hexachlorobenzene is studied, with special attention to the covalent binding to protein. The metabolites formed are pentachlorophenol and tetrachlorohydroquinone. In addition, a considerable amount of covalent binding to protein is detected (250 pmoles pentachlorophenol, 17 pmoles tetrachlorohydroquinone and 11 pmoles covalent binding in an incubation containing 50 mumoles of hexachlorobenzene). In order to establish the potential role of reductive dechlorination in the covalent binding, the anaerobic metabolism of hexachlorobenzene was investigated. At low oxygen concentrations no pentachlorobenzene was detected, and only very small amounts of pentachlorophenol as well as covalent binding, indicating a relationship between covalent binding and the microsomal oxidation of hexachlorobenzene. Incubations with 14C-pentachlorophenol at low concentrations showed that a conversion-dependent covalent binding occurs to the extent of 75 pmole binding per nmole pentachlorophenol. This is almost enough to account for the amount of label bound to protein observed in hexachlorobenzene incubations. This indicates that less than 10% of the covalent binding occurs during conversion of hexachlorobenzene to pentachlorophenol, and the remainder is produced during conversion of hexachlorobenzene to pentachlorophenol, and the remainder is produced during conversion of pentachlorophenol. The major product of microsomal oxidation of pentachlorophenol is tetrachlorohydroquinone, which is in redox-equilibrium with the corresponding semiquinone and quinone (chloranil). The covalent binding is inhibited by addition of ascorbic acid or glutathione to the hexachlorobenzene incubations. Ascorbic acid decreases the covalent binding with a simultaneous increase in formation of tetrachlorohydroquinone, probably due to a shift in the redox-equilibrium to the reduced side. Glutathione does not act as a reducing agent, since the inhibition of covalent binding is not accompanied by an increase in tetrachlorohydroquinone formation. Instead, glutathione reacts with chloranil, producing at least three stable products, probably in a Michael-type reaction. These results strongly indicate the involvement of chloranil or the semiquinone radical in the covalent binding during microsomal hexachlorobenzene metabolism.

Formation of pentachlorophenol as the major product of microsomal oxidation of hexachlorobenzene

On incubation of [14C]-hexachlorobenzene with microsomes from livers of rats induced with hexachlorobenzene, the major product (80-90%) was pentachlorophenol. The only other detectable metabolite, tetrachlorohydroquinone (4-15%), was presumably formed from pentachlorophenol. A considerable amount of radioactivity (5-10% of the amount of extracted metabolites) was covalently bound to protein. Microsomes derived from male hexachlorobenzene--induced rats gave by far the highest conversion (approx. 1% of substrate). Microsomes from female hexachlorobenzene--induced rats were 3 times less efficient. Microsomes from untreated and 3-methyl-cholanthrene--treated animals gave less than 5% of the amount of pentachlorophenol formed by microsomes from hexachlorobenzene--induced male rats, while phenobarbital and aroclor 1254-induction resulted in formation of 51% and 34% respectively.

DNA-damaging properties and cytotoxicity in human fibroblasts of tetrachlorohydroquinone, a pentachlorophenol metabolite

The DNA-damaging potential of pentachlorophenol (PCP) and its metabolite tetrachlorohydroquinone (TCH) was investigated. TCH was found to bind covalently to calf-thymus DNA and to cause single-strand breaks in PM2 DNA. No DNA-damaging effects were observed for PCP. Exposure of human fibroblasts to PCP and TCH showed that TCH is more toxic, when colony-forming ability after exposure to the agent is used as a measure of toxicity. In the evaluation of the mutagenic and carcinogenic potential of PCP the metabolite TCH should be taken into consideration.

A simple liquid chromatographic method for the analysis of penta- and tetrachlorophenols in urine of exposed workers

A liquid chromatographic method was developed for the simultaneous determination of penta- and tetrachlorophenols in urine. The method is more rapid than gas chromatographic methods and does not involve the use of such potentially dangerous compounds as benzene, diazomethane or pyridine, which have been used in several methods described previously.

Chlorinated phenols: occurrence, toxicity, metabolism, and environmental impact

Pentachlorophenol and the lower chlorinated phenols, tetra- and trichlorophenols, have gained an increasing use as fungicides, herbicides, insecticides, and precursors in the synthesis of other pesticides since the early 1930s. World-wide production totals about 200,000 tons. Production and use of chlorinated phenols have caused industrial hygiene problems but, otherwise, have not been recognized to create more than limited environmental problems. The introduction of modern analytical techniques, however, has revealed the ubiquitous occurrence of chlorophenols in the environment, and the discovery of chlorinated dimers, such as dibenzo-p-dioxins and dibenzofurans, as impurities in commercial chlorophenol formulations, has made a reevaluation of the chlorinated phenols necessary. The present article reviews recent studies on the toxicity and metabolism in mammals and aquatic organisms and the degradation of the chlorophenols under various conditions in the environment. Finally, the hazards of burning of chlorophenol wastes are discussed, as well as health considerations with regard to humans and the environment.

Effects of pentachlorophenol and 2,4,6-trichlorophenol on the disposition of sulfobromophthalein and respiration of isolated liver cells

The effect of pentachlorophenol (PCP) and 2,4,6-tricholorphenol (2,4,6-T) on the disposition of the hepatodiagnostic dye, sulfobromophthalein (BSP) has been studied in isolated liver cells. PCP (4-6 microM) as well as 2,4,6-T (50-100 microM) interferes with the disposition of BSP. The main effect apparently occurs at the secretion step as both drugs severely impair the release of the glutathione conjugate of BSP into the medium. As a consequence, BSP and its conjugate accumulate in the cell. High doses of PCP did not increase the release of lactate dehydrogenase from the hepatocytes. Concentrations of the two phenols which interfere with the secretion of BSP also completely uncouple the oxidative phosphorylation of hepatocellular mitochondria. The dysfunction of liver cells described here may therefore be explained by the effect of PCP and 2,4,6-T on the energy production of the cells. The higher toxicity of PCP as compared to 2,4,6-T observed in our system corresponds well with the higher LD50 of the latter compound.

Effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin on the in vivo and in vitro dechlorination of pentachlorophenol

The metabolism of pentachlorophenol has been studied in the rat after pretreatments with phenobarbital, 3-methyl cholanthrene or 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). In addition to the previously identified metabolite, tetrachloro-p-hydroquinone, trichloro-p-hydroquinone has been identified in urine as a metabolite. The formation of the latter represents a type dechlorination different from that of the formation of tetrachlorohydroquinone. The inducing agents, 3-methylcholanthrene and TCDD have similar effects on the dechlorination and increase the formation of tetrachloro-p-hydroquinone more pronounced than does phenobarbital. In contrast to phenobarbital they also increase the formation of trichloro-p-hydroquinone and the total elimination of pentachlorophenol and its metabolites. The in vivo findings are supported by in vitro studies with microsomes from rats pretreated with phenobarbital or TCDD. Use of the inhibitor beta-diethylaminoethyl-diphenyl propylacetate (SKF 525-A) in vitro showed a more pronounced inhibition on microsomes from phenobarbital-treated rats than on microsomes from untreated or TCDD-treated rats. Gas chromatography-mass spectrometry have been used for the identification and quantification of pentachlorophenol and its metabolites.