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Relative sensitivity of Daphnia magna and Brachionus calyciflorus to five pesticides.

Comparative toxicity of several pesticides, lindane, endosulfan, pentachlorophenol (PCP),3,4-dichloroaniline (DCA) and copper sulphate has been tested to determine their lethality in two species of freshwater invertebrates, Daphnia magna and Brachionus calyciflorus. D. magna was more sensitive than B. calyciflorus to all the toxicants tested except to copper sulphate. DCA was the most toxic compound to D. magna and was followed in order of decreasing toxicity by copper sulphate, PCP, endosulfan and lindane. Copper sulphate was the most toxic chemical tested to the rotifer B. calyciflorus and was followed by PCP, endosulfan, lindane and DCA. The 24 hr LC50 values (mg/L) for D. magna and B. calyciflorus, respectively, were: lindane, 1.64 and 22.5; endosulfan, 0.62 and 5.15; DCA, 0.20 and 61.5; PCP, 0.39 and 2.16; copper sulphate, 0.38 and 0.076.

Aniline Compounds↗

A comparison of two methods for fractionating complex mixtures in preparation for toxicity analysis.

Chemical fractionation is a widely used tool for the chemical and toxicological characterization of complex mixtures. The objective of this research was to compare two frequently employed methods for fractionating a wood preserving waste (WPW) containing polycyclic aromatic hydrocarbons (PAHs) and pentachlorophenol (PCP). The first method involved fractionation of the WPW into acid, base, and neutral fractions using a liquid-liquid acid/base/neutral (A/B/N) technique. The second method utilized alumina column chromatography to produce two fractions, A1 and A2. Gas chromatography and mass spectrometry were used to quantify the chemical components in all fractions. The alumina method recovered 473,338 mg of total PAHs (tPAHs) per kilogram crude, while the A/B/N method yielded only 193,379 mg tPAHs/kg crude. In contrast, the A/B/N method recovered 13.7 mg PCP/kg crude while the alumina method yielded only 0.5 mg PCP/kg crude. Three bioassays were used to determine the toxicity of the crude extract and fractions. The neutral and A1 fractions contained the highest levels of tPAHs and benzo[a]pyrene (BaP) but failed to induce a positive response in the Salmonella/microsome assay with concentrations containing as much as 1800 and 2500 ng BaP/plate, respectively. In the Escherichia coli prophage induction assay, the acid fraction, which contained 472 mg PCP/kg fraction, induced a positive response, as did the base fraction, which did not contain detectable PCP. Significant reduction of gap junctional intercellular communication in hepatic cells occurred with the crude extract and acid, base, and neutral fractions. Overall, the results of these bioassays suggest that PCP genotoxicity was expressed in the acid fraction, whereas the cumulative genotoxicity of genotoxic PAHs appeared to be masked in the isolates from either fractionation method. The optimal fractionation method for a mixture of chlorophenols and PAHs may involve a refined hybrid method.

Animals↗

Effect of hydroxychlorodiphenyl ethers (chlorinated pre-and isopredioxins) on erythrocyte membrane adenosinetriphosphatase activity.

The effect of hydroxychlorodiphenyl ethers (HO-ClX-DPEs; chlorinated pre- and isopredibenzodioxins), contaminants of technical chlorophenol preparations, on human erythrocyte membrane-bound adenosinetriphosphatases (ATPases) has been investigated. Both 2- and 3-HO-Cl9-DPE inhibited the Na+ + K+-activated, Mg2+-dependent ATPase (Na+, K+, Mg2+-ATPase). The Mg2+-dependent ATPase (Mg2+-ATPase) was stimulated at lower concentration of these compounds, but at higher concentrations there was a gradual decrease in the extent of stimulation, 2-Hydroxy-21, 41, 41-trichlorodiphenyl ether (2-HO-Cl3-DPE; Irgasan DP-300; Triclosan) was not as effective as the nonachloro compounds at inhibiting Na+, K+, Mg2+-ATPase and was inactive at stimulating Mg2+-ATPase. Pure pentachlorophenol (PCP) caused both inhibition of Na+, K+, Mg2+-ATPase and stimulation of Mg2+-ATPase, although each effect required a higher concentration of PCP than was needed for the HO-CL9-DPEs. The possible relationship of the effects of HO-CL x-DPEs on human erythrocyte membrane ATPase activities to the potent hemolytic activity of these compounds is discussed.

Adenosine Triphosphatases↗

The acute toxicity of nonachloropredioxin and 3- and 4-hydroxynonachlorodiphenyl ether in mice.

The acute intraperitoneal LD50 values of hydroxynonachlorodiphenyl ethers (HO-Cl9-DPEs) in mice have been determined. The acute toxicity of each of these compounds is compared with that of pentachlorophenol (PCP) and 2-hydroxy-2',4,4'-trichlorodiphenyl ether (2-HO-Cl3-DPE; Irgasan DP-300; Triclosan), a commonly used bactericide. The order of acute toxicity observed was: 2-HO-Cl9-DPE greater than technical PCP approximately equal to pure PCP greater than 3-HO-Cl9-DPE greater than 4-HO-Cl9-DPE greater than 2-HO-Cl3-DPE. Symptomatology following exposure to the HO-Cl9-DPEs was similar to that observed for PCP, a known uncoupler of oxidative phosphorylation. 2-HO-Cl3-DPE, however, produced clinical signs suggestive of a suppressive effect on the central nervous system. Data on time response following a lethal dose of each of these compounds was also obtained.

Animals↗

Selected pesticide residues and metabolites in urine from a survey of the U.S. general population.

Residues of toxic chemicals in human tissues and fluids can be important indicators of exposure. Urine collected from a subsample of the second National Health and Nutrition Examination Survey was analyzed for organochlorine, organophosphorus, and chlorophenoxy pesticides or their metabolites. Urine concentration was also measured. The most frequently occurring residue in urine was pentachlorophenol (PCP), found in quantifiable concentrations in 71.6% of the general population with an estimated geometric mean level of 6.3 ng/ml. Percent quantifiable levels of PCP were found to be highest among males. Quantifiable concentrations of 3,5,6-trichloro-2-pyridinol (5.8%), 2,4,5-trichlorophenol (3.4%), para-nitrophenol (2.4%), dicamba (1.4%), malathion dicarboxylic acid (0.5%), malathion alpha-monocarboxylic acid (1.1%), and 2,4-D (0.3%) were found, but at much lower frequencies. No quantifiable levels of 2,4,5-T or silvex were found. Preliminary analyses showed an apparent relationship between residue concentration and two measures of urine concentration (osmolality and creatinine). A large segment of the general population of the United States experienced exposure to certain pesticides, including some considered biodegradable, during the years 1976-1980.

2,4-Dichlorophenoxyacetic Acid↗

Effects on thyroid hormone metabolism and depletion of lung vitamin A in rats by airborne particulate matter.

Thyroxine (T4) and vitamin A are important regulators of normal epithelial differentiation and proliferation and might act in the promotion phase of carcinogenesis. Thyroid hormone and vitamin A metabolism are linked by a common plasma carrier protein, transthyretin (TTR). Polychlorinated biphenyls (PCBs) and related organochlorine compounds deplete vitamin A and thyroxine by interaction with TTR and alteration of their metabolism in hepatic and other organs. In the present report an outdoor airborne particulate matter (APM) extract was tested for both interaction with thyroid hormone and vitamin A metabolism, in order to address the question of whether APM has the potency to deplete vitamin A and thyroid hormones. Furthermore, studies were performed to characterize compounds present in APM that interact with TTR. A third aim was to compare the interaction of APM extracts with TTR and thyroxine-binding globulin (TBG), the major carrier protein for thyroxine in humans. Results showed that a single treatment of rats with an outdoor APM extract depleted plasma thyroxine and triiodothyronine levels and increased plasma retinol levels gradually over the time period studied, while liver retinol, lung retinol, and retinyl palmitate levels were depleted by 30-50%. As outdoor APM was able to inhibit T4-TTR binding in vitro, this suggests that the reduction in thyroxine levels in vivo is caused by the same phenomenon. Experiments showed that the neutral fraction of the APM extract accounted for most of the inhibitory activity on T4-TTR binding. Polycyclic aromatic hydrocarbons and nitrated derivatives are not likely to be responsible for the activity of the neutral fraction, because several representatives of these compounds showed no or very little interaction with TTR. Pentachlorophenol, a compound with known inhibitory activity on T4-TTR binding, was detected in the organic acid fraction of both a cigarette smoke sample and an outdoor APM sample. Finally, it was shown that several indoor and outdoor APM extracts only interact with TTR, but not with TBG. As APM has the potency to deplete lung vitamin A in vivo and vitamin A might have a protective effect in the process of lung carcinogenesis, APM might increase the susceptibility for the development of lung cancer.

Aerosols↗

Evaluation of the use of uncertainty factors in deriving RfDs for some chlorinated compounds.

Risk assessment of exposure to chemicals having a toxic endpoint routinely uses the reference dose (RfD) approach based on uncertainty factors of 10. The purpose of this investigation was to evaluate whether the magnitude of the U.S. Environmental Protection Agency (EPA) 10x uncertainty factors has scientific merit when compared with data from recent human and animal experimental studies. A compilation and comparison of ratios between LOAEL/NOAEL (lowest observed adverse effect level/no observed adverse effect level) and subchronic/chronic values was made for six chlorinated compounds, namely, carbon tetrachloride, methylene chloride, pentachlorophenol, monochlorobenzene, chlorpyrifos, and 1,1-dichloroethane. Data sets demonstrated that 91.3% of the LOAEL/NOAEL ratios were < or = 6 while 87% of the ratios for the same parameter were < or = 5. Furthermore, subchronic/chronic ratios were < or = 3.5. From our investigation we concluded that automatic safety factors of 10x are not scientifically supportable and are overly conservative for the chlorinated compounds studied here.

Animals↗

Anaerobic biodegradation of DDT residues (DDT, DDD, and DDE) in estuarine sediment.

The potential for anaerobic biodegradation of 1,1,1-trichloro-2,2-bischlorophenylethane (DDT), 1,1-dichloro-2,2,-bischlorophenylethane (DDD), and dichlorodiphenylchloroethylene (DDE) in anoxic sediment slurries collected from the Keelung River was investigated in this study. o,p'- and p,p'-DDT were dechlorinated to o,p'- and p,p'-DDD, respectively, and then transformed to other compound(s). 1-Chloro-2,2-bis (p-chlorophenyl) ethylene (DDMU) and trace amount of dichlorobenzophenone (DBP) were detected in sediment slurries amended with p,p'-DDT or p,p'-DDD. DDMU was also detected in sediment slurries amended with p,p'-DDE. The relative transformation rates for both o,p'- and p,p'-isomers of DDT, DDD, and DDE were DDT>DDD>DDE. Re-addition of DDT, DDD, or DDE to the sediment slurries after initial removal enhanced the respective dechlorination rates. The transformation rates of the p,p'-isomers of both DDT and DDD were faster than those of the respective o,p'-isomers. p,p'-DDT dechlorination in the p,p'-DDT-adapted sediment slurries were inhibited by the addition of molybdate, or molybdate plus sulfate, but not inhibited by the addition of sulfate. Addition of bromoethane-sulfonic acid (BESA) slightly inhibited p,p'-DDT dechlorination. Non-adapted sediment slurries lost the ability to dechlorinate pentachlorophenol during adaptation to p,p'-DDT. p,p'-DDD was the major transformation product of p, p'-DDT in 3,4,4',5-tetrachlorobiphenyl-adapted sediment slurries, which suggested that the microbial community in the 3,4,4',5-CB-adapted sediment was unable to remove chlorine from the aromatic rings of p,p'-DDT.

Alkanesulfonic Acids↗

Impact of four pesticides on the growth and metabolic activities of two photosynthetic algae.

The acute toxicity was determined for soil algae Chlorella kesslerei and Anabaena inaequalis, exposed to pesticides lindane, pentachlorophenol (PCP), isoproturon (IPU), and methyl parathion (MP). Toxicity markers included growth inhibition, chlorophyll biosynthesis, and total carbohydrate content, as a function of dose and time. Concentration response functions (EC50) were estimated by probit data transformation and weighted linear regression analyses. Lindane's toxicity to Chlorella increased sharply with time (EC50 = 7490, 10.3, 0.09 mg L(-1); 24, 48, 72 h), but remained nearly constant through 72 h with Anabaena (8.7-6.7 mg L(-1); 24-72 h). PCP at low concentrations stimulated algal growth and chlorophyll a production, an effect reversed at higher doses. Anabaena was less tolerant of PCP and MP than was Chlorella. The 96-h static EC50 values for Chlorella were: 0.003, 34, 0.05, and 291 mg L(-1) for lindane, PCP, isoproturon, and MP, respectively; for Anabaena, these were 4.2, 0.13, 0.21, and 19 mg L(-1). Carbohydrate production responses were similar to those of cell density (growth) and chlorophyll biosynthesis, with MP having the lowest adverse impact. The overall relative toxicity among the four tested pesticides was: for Chlorella, lindane > IPU >> PCP >> MP; and for Anabaena, PCP > IPU > lindane > MP. The results confirm that toxicants such as these pesticides may affect individual (though related) species to significantly different degrees.

Anabaena↗

pH homeostasis in promyelocytic leukemic HL60 cells.

By measuring the membrane potential using the influx of the lipophilic cation tetraphenylphosphonium and intracellular pH using 2,7-biscarboxy-ethyl-5(6)-carboxyfluorescein and the distribution of the weak acid 5,5-dimethyl-2,4-oxazolidinedione, we have determined that intracellular pH is 0.9-1.1 pH units above electrochemical equilibrium in undifferentiated HL60 cells, indicating that these cells actively extrude proton equivalents. The Na/H exchanger is not the system responsible for keeping the pH above the electrochemical equilibrium, since adding inhibitors of this transport system (dimethylamiloride and ethylisopropylamiloride) or removing the extracellular sodium has no effect on intracellular pH. In contrast, the addition of the Cl/HCO3 exchange inhibitors H2 4,4'-diisothiocyanostilbene-2,2'-disulfonate (DIDS) or pentachlorophenol (PCP) causes a drop in intracellular pH, and the removal of extracellular chloride in the presence of bicarbonate leads to a large intracellular alkalinization, which indicates a role for the anion exchanger in pH homeostasis in these cells. In addition, we find that the intracellular chloride concentration is about one order of magnitude above electrochemical equilibrium. We conclude that an H2DIDS and PCP inhibitable system, probably the Cl/HCO3 exchanger, is at least partially responsible for keeping intracellular pH above electrochemical equilibrium in HL60 cells under resting conditions. We also find no change in intracellular pH when cells differentiate along the granulocytic pathway (having been induced by the addition of dimethylsulfoxide or of retinoic acid), which indicates that changes in intracellular pH are not causally related to cell differentiation.

4,4'-Diisothiocyanostilbene-2,2'-Disulfonic Acid↗

The role of sulfation in the metabolic activation of N-hydroxy-4'-fluoro-4-acetylaminobiphenyl.

The role of sulfation in the metabolic activation of the liver carcinogen N-hydroxy-4'-fluoro-4-acetylaminobiphenyl (N-OH-FAABP) in male rat liver was investigated. N-OH-FAABP was a substrate for sulfotransferases in vitro and sulfation was inhibited by the sulfotransferase inhibitors pentachlorophenol (PCP) and 2,6-dichloro-4-nitrophenol (DCNP). The main metabolite of N-OH-FAABP excreted in bile in vivo, and in the isolated perfused liver, was identified as the N-O-glucuronide conjugate. Inhibition of sulfation in vivo by PCP or DCNP, or in vitro by omission of inorganic sulfate, resulted in a large increase in the excretion of the N-O-glucuronide conjugate. It was estimated that at least 21% of the dose was sulfated in control animals. Inhibition of sulfation in vivo by PCP or DCNP prevented the covalent binding of N-OH-FAABP to liver (and kidney) macromolecules by 70% and 20% respectively. HPLC analysis of the fluorobiphenyl DNA and RNA adducts showed that the formation of both N-acetylated and deacetylated (deoxy)-guanosine adducts was prevented. Furthermore, omission of inorganic sulfate in the isolated perfused liver prevented the formation of all fluorobiphenyl DNA adducts by 70-80%. It is concluded that two sulfotransferase-dependent pathways exist for the metabolic activation of N-OH-FAABP in male rat liver: (i) direct sulfation of the hydroxamic acid, resulting, upon decomposition of the FAABP-N-sulfate ester, in the formation of N-acetylated DNA adducts and (ii) deacetylation followed by sulfation of the hydroxylamine to FABP-N-sulfate, leading to the formation of deacetylation DNA adducts.

Aminobiphenyl Compounds↗

The role of specific DNA adducts in the induction of micronuclei by N-hydroxy-2-acetylaminofluorene in rat liver in vivo.

N-Hydroxy-2-acetylaminofluorene (N-OH-AAF) was administered i.p. to male Wistar rats 17 h after partial hepatectomy. Hepatocytes were analyzed for the presence of micronuclei 7 h, 1, 2, 3 and 4 days after injection. N-OH-AAF treatment resulted in a high frequency of micronucleated hepatocytes at days 3 and 4 (19.5% and 19.6% respectively). The frequency of micronucleated hepatocytes was not increased above control values when hepatocytes were isolated as early as 7 h, 1 or 2 days after injection. Pretreatment with the sulfotransferase inhibitor pentachlorophenol (PCP) 45 min before injection of N-OH-AAF almost completely prevented the formation of micronuclei by N-OH-AAF. Parallel biochemical studies indicated that inhibition of sulfation of N-OH-AAF by PCP pretreatment prevented the formation of the N-acetylated DNA adducts N-deoxyguanosin-8-yl-AAF and 3-deoxyguanosin-N2-yl-AAF by approximately 85%. Total adduct formation to DNA was, however, not lowered because of an increase in the formation of the deacetylated adduct, N-deoxyguanosin-8-yl-AAF. The lower frequency of micronucleated hepatocytes observed in the group pretreated with PCP, did not result from less proliferative activity in this group as compared to the group treated with N-OH-AAF alone. Therefore, the decrease in the formation of micronuclei indicates that PCP prevents the clastogenic damage caused by N-OH-AAF. It is concluded that the clastogenicity of N-OH-AAF in rat liver is related to the formation of N-acetylated DNA adducts (i.e. N-deoxyguanosin-8-yl-AAF and/or 3-deoxyguanosin-N2-yl-AAF) and is not related to the formation of the deacetylated DNA adduct N-deoxyguanosin-8-yl-AF.

2-Acetylaminofluorene↗

Sulfation-dependent formation of N-acetylated and deacetylated DNA adducts of N-hydroxy-4-acetylaminobiphenyl in male rat liver in vivo and in isolated hepatocytes.

Administration of 3H-labeled N-hydroxy-4-acetylaminobiphenyl (N-OH-AABP) to male Wistar rats with or without prior partial hepatectomy (PH) resulted in covalent binding of 3H activity to liver macromolecules. Pretreatment with the sulfotransferase inhibitor pentachlorophenol (PCP) 45 min before administration of the arylhydroxamic acid strongly decreased the covalent binding. Analysis of aminobiphenyl adducts after TFA hydrolysis of DNA and RNA showed that PCP decreased the formation of both the N-acetylated adduct N-[deoxy)guanosin-8-yl)-4-acetylaminobiphenyl [(d)G-C8-AABP] and the deacetylated adduct N-[deoxy)-guanosin-8-yl)-4-aminobiphenyl [(d)G-C8-ABP] by 60-80%. In incubations with hepatocytes from male Wistar or Sprague-Dawley rats, omission of inorganic sulfate also strongly decreased the covalent binding of 3H-labeled N-OH-AABP to RNA and protein. Analysis of RNA adducts showed a 70-80% decrease in the formation of G-C8-ABP in the absence of sulfate. Another, as yet unidentified, adduct was only slightly decreased. Similar results were obtained with the structurally related carcinogen N-hydroxy-4'-fluoro-4-acetylaminobiphenyl (N-OH-FAABP). Pretreatment with PCP decreased the incidence of gamma-glutamyltranspeptidase-positive foci in the liver of male rats when analyzed 30 days after a single injection of N-OH-AABP or N-OH-FAABP by 60 and 80% respectively. Thus, both N-acetylated and deacetylated RNA and DNA adducts of N-OH-AABP in rat liver are formed by sulfation and this metabolic activation pathway is responsible for the formation of genotoxic metabolites involved in the generation of preneoplastic cells.

Acetylation↗

Roles of different forms of cytochrome P450 in the activation of the promutagen 6-aminochrysene to genotoxic metabolites in human liver microsomes.

We reported previously that the potent mutagen 6-aminochrysene is catalyzed principally by rat liver microsomal P4501A and P4502B enzymes to reactive metabolites that induce umu gene expression in O-acetyltransferase-over-expressing strain Salmonella typhimurium NM2009; the proposal was made that there are different mechanisms in the formation of reactive N-hydroxylated and diolepoxide metabolites by P450 enzymes (Yamazaki, H. and Shimada, T., Biochem. Pharmacol., 44, 913-920, 1992). Here we further examined the roles of human liver P450 enzymes and the mechanism of activation of 6-aminochrysene by rat and human P450 enzymes in the Salmonella tester strains. Liver microsomes from 18 different human samples catalyzed activation of 6-aminochrysene more efficiently in S. typhimurium NM2009 than in the original strain of S. typhimurium TA1535/pSK1002. The rates of 6-aminochrysene activation in 18 human liver samples showed good correlation to the contents of P4502B6 as well as contents of P4503A4 and the respective mono-oxygenase activities catalyzed by P4503A4. Among purified P450 enzymes examined, P4501A2 as well as P4503A4 were highly active in transforming 6-amino-chrysene to reactive metabolites, suggesting the involvement of different human P450 enzymes in the reaction. Four human samples that contained relatively high levels of particular P450 enzymes in their microsomes were selected and used for further characterization. Liver microsomes from human samples HL-13 and HL-4 that contained the highest levels of P4502B6 and P4503A4 respectively, were sensitive to the respective antibodies raised against monkey P4502B and human P4503A4; the activity in sample HL-16 having the highest level of P4501A2 was inhibited by anti-P4501A2 IgG. alpha-Naphthoflavone enhanced the activation of 6-aminochrysene very significantly in human liver microsomes enriched in P4503A4 and P4502B6 enzymes. Pentachlorophenol, an inhibitor of acetyltransferase activity, suppressed the activation of 6-aminochrysene in liver microsomes from phenobarbital-treated rats and from human samples HL-4, HL-13 and HL-18 but not HL-16. In contrast, 1,1,1-trichloropropane-2,3-oxide, an inhibitor of epoxide hydrolase activity, enhanced the activation of 6-aminochrysene catalyzed by liver microsomes from beta-naphthoflavone-treated rats and from human samples HL-16 but not HL-4, HL-13 and HL-18. Inclusion of purified rat epoxide hydrolase to the reconstituted system containing rat and human P4501A enzymes caused a decrease in the rates of 6-aminochrysene activation.(ABSTRACT TRUNCATED AT 400 WORDS)

Animals↗

Tamoxifen: evidence by 32P-postlabeling and use of metabolic inhibitors for two distinct pathways leading to mouse hepatic DNA adduct formation and identification of 4-hydroxytamoxifen as a proximate metabolite.

Exposure to pentachlorophenol (PCP) strongly intensifies the formation of mouse hepatic DNA adducts elicited by oral administration of tamoxifen (TAM), as previously shown by 32P-postlabeling. To explain this effect, PCP was proposed to interfere with the detoxication by sulfate conjugation of an as yet unidentified hydroxylated proximate TAM metabolite. A comparison of the present and earlier results shows that the hepatic TAM adduct pattern in female ICR mice depended on the route of administration of TAM (120 mumol/kg), with oral administration primarily eliciting formation of more polar adducts (termed group I adducts), while after i.p. administration less polar adducts (group II) predominated over group I adducts by a factor of 17.5. All these adducts were also formed in female Sprague-Dawley rats after i.p. dosing with TAM, but total adduct levels were 3.5- to 5-fold higher than in mice. After four daily i.p. treatments, TAM adducts accumulated in mouse liver DNA in a non-linear fashion. Adduct levels were 30-50 times lower in mouse kidney and lung than in liver. The phenolic metabolite 4-hydroxy TAM (120 mumol/kg) exclusively led to formation of polar (group I) hepatic adducts, and this process was stimulated 8-fold by co-administration of PCP (75 mumol/kg). Co-administration of PCP with the parent compound led to an 11-fold enhancement of group I adduct formation; simultaneously, levels of group II adducts were suppressed 6-fold. Another inhibitor of sulfate conjugation, 2,6-dichloro-4-nitrophenol, unlike PCP, had no effect on group I adducts, but it reduced group II adduct formation 2.2-fold. The PCP metabolite 2,3,5,6-tetrachlorohydroquinone (75 mumol/kg) did not significantly affect any major TAM adduct, suggesting that PCP itself was the active compound. Similar to group II TAM adducts, the formation of hepatic safrole-DNA adducts was inhibited in female ICR mice by both sulfotransferase inhibitors, consistent with the proposal that metabolic alpha-hydroxylation of the ethyl group of TAM followed by sulfate conjugation represented a mechanism of TAM activation. On the other hand, the strong intensification of group I adducts by PCP and the lack of this effect by 2,6-dichloro-4-nitrophenol suggested that inhibition of sulfate conjugation may not have been the primary mechanism underlying the intensification of group I adducts formed from TAM or 4-hydroxy TAM. The results presented herein demonstrate conclusively that TAM was activated to DNA-reactive compounds along two distinct pathways which contrasted in their responses to metabolic inhibitors.

Animals↗

32P-post-labelling analysis of DNA adducts formed in the livers of animals treated with safrole, estragole and other naturally-occurring alkenylbenzenes. I. Adult female CD-1 mice.

The binding of a series of alkenylbenzenes to liver DNA of adult female CD-1 mice, isolated 24 h after i.p. administration of non-radioactive test compound (2 or 10 mg/mouse), was investigated by a modified 32P-post-labelling assay. The known hepatocarcinogens, safrole, estragole and methyleugenol, exhibited the strongest binding to mouse-liver DNA (1 adduct in 10 000 - 15 000 DNA nucleotides or 200 - 300 pmol adduct/mg DNA after administration of a 10 mg dose), while several related compounds, which have not been shown thus far to be carcinogenic in rodent bioassays, bound to mouse-liver DNA at 3 - 200x lower levels. The latter compounds included allylbenzene, anethole, myristicin, parsley apiol, dill apiol and elemicin. Eugenol did not bind. Low binding to mouse-liver DNA was also observed for the weak hepatocarcinogen, isosafrole. Two main 32P-labelled adducts, which appeared to be guanine derivatives, were detected for each of the binding chemicals on thin-layer chromatograms. The loss of safrole adducts from liver DNA was biphasic: a rapid loss during the first week (t 1/2 approximately 3 days) was followed by a much slower decline up to 20 weeks after treatment (t 1/2 approximately 2.5 months). Adducts formed by reaction of 1'-acetoxysafrole, a model ultimate carcinogen, with mouse-liver DNA in vitro were chromatographically identical to safrole-DNA adducts formed in vivo. Pretreatment with pentachlorophenol, a known inhibitor of sulphotransferases, inhibited the binding of safrole to mouse-liver DNA, providing further evidence that the metabolic activation of the allylbenzenes proceeds by the formation of 1'-hydroxy derivatives as proximate carcinogens and 1'-sulphoöxy derivatives as ultimate carcinogens.

Allylbenzene Derivatives↗

Effect of glutathione levels, sulfate levels, and metabolic inhibitors on covalent binding of 2-amino-3-methylimidazo[4,5-f]quinoline and 2-acetylaminofluorene to cell macromolecules in primary monolayer cultures of adult rat hepatocytes.

The covalent binding of radiolabeled 2-amino-3-methylimidazo[4,5-f]quinoline (IQ) and 2-acetylaminofluorene (AAF) to cell macromolecules was studied using primary monolayer cultures of adult rat hepatocytes. A time course for covalent binding was determined, and revealed similar levels of binding for both chemicals. Inhibition of glutathione synthesis by L-buthionine sulfoximine (1 mM) enhanced binding of both AAF and IQ with a greater increase observed for IQ. Addition of excess glutathione (10 mM) to the medium resulted in a slight decrease in IQ but not AAF binding. Addition of the P-450 inhibitor, 2-[2,4-dichloro-6-phenyl)-phenoxy]ethylamine (DPEA, 0.1 mM), resulted in almost total (94%) inhibition of IQ binding, with a lesser effect (42%) on AAF. Methimazole (1 mM), a competitive substrate of the flavin-containing monooxygenase, had no effect on the binding of either compound. Pentachlorophenol, an inhibitor of sulfate conjugation, decreased AAF binding substantially but produced a much smaller decrease in IQ binding. Addition of excess sulfate did not change the binding levels of either IQ or AAF. Cell density had little effect on IQ or AAF binding levels.

2-Acetylaminofluorene↗

Sulfuric acid esters as major ultimate electrophilic and hepatocarcinogenic metabolites of 4-aminoazobenzene and its N-methyl derivatives in infant male C57BL/6J x C3H/HeJ F1 (B6C3F1) mice.

Liver cytosols from 12-day-old male C57BL/6 X C3H/HeJ F1 (B6C3F1) mice contain 3'-phosphoadenosine-5'-phosphosulfate (PAPS)-dependent sulfotransferase activity for N-hydroxy-4-aminoazobenzene and N-hydroxy-N-methyl-4-aminoazobenzene. No acetyl co-enzyme A-dependent transacetylase activity for these hydroxylamines was detected in the cytosols. Pentachlorophenol (PCP) and 2,6-dichloro-4-nitrophenol were only moderately active inhibitors of the sulfotransferase activity; at a 100-microM concentration each compound inhibited the activity by only 50-80%. A single dose of 0.04 mumol/g body weight of PCP administered to 12-day-old male B6C3F1 mice 45 min prior to a single dose of 0.1 mumol/g body weight of [3H]4-aminoazobenzene ([3H]AB) or [3H]N,N-dimethyl-4-aminoazobenzene ([3H]DAB) inhibited DNA adduct formation by approximately 50%. Under identical conditions, PCP also reduced the average number of hepatomas induced per mouse at 9 months by AB and N-methyl-4-aminoazobenzene (MAB) by 52 and 36%, respectively. PCP strongly inhibited the hepatocarcinogenicity of DAB or AB when this agent was administered in the diet with either dye to female CD-1 mice over a 10- month period. Single doses of 0.15 mumol/g body weight of [3H]AB and [3H]DAB bound to hepatic DNA of 12-day-old brachymorphic B6C3F2 mice, which are deficient in the synthesis of PAPS, at levels 15 and 20%, respectively, of those found in their phenotypically normal litter mates. Under identical conditions, the incidence of hepatomas in brachymorphic mice at 9 months were 11 and 29%, with averages of 0.2 and 0.8 hepatomas/mouse for AB and MAB, respectively. Incidences of 77 and 86%, with averages of 6.6 and 5.4 hepatomas/mouse, respectively, were found in their phenotypically normal litter mates. These data strongly indicate that N-sulfoöxy-AB is a major ultimate electrophilic and hepatocarcinogenic metabolite of AB in mice. Similarly, this ester and N-sulfoöxy-N-methyl-4-aminoazobenzene appear to be critical metabolites for these activities of DAB and MAB.

Acetyltransferases↗