Abstract  The B6C3F1 mouse is used worldwide to gauge the carcinogenic hazard posed by chemicals to humans. An assessment of the ability of this rodent model to predict human neoplasia requires an evaluation of similarities and differences in the genetics of tumor formation between these two species. We examined 142 spontaneous and chemically-induced liver tumors isolated from the B6C3F1 mouse for losses of heterozygosity (LOH) at 78 polymorphic loci and compared these results to genetic changes known to occur in human hepatocellular carcinoma. Approximately a third of the 142 mouse tumors exhibited LOH, suggesting that tumor suppressor gene inactivation may be involved in the formation of mouse liver tumors. Most of the LOH observed was restricted to seven chromosome sites and most of the tumors that underwent LOH lost alleles from only one of those seven sites. The relatively few losses seen in these mouse tumors distinguished them from clinical stage human tumors in that, in the mouse tumors, interstitial deletions appeared more frequently than losses of whole chromosomes. Only four mouse tumors lost a whole chromosome. LOH occurred at loci of the mouse genome syntenic to areas of the human genome known to harbor the Wilms', retinoblastoma, APC, MCC and DCC tumor suppressor genes; these genes have never been associated with hepatocellular carcinomas. Losses observed on chromosomes 5 and 8 (syntenic to human chromosomes 4 and 16) suggest tumor suppressor genes that are common to hepatocellular carcinomas from both species, while losses on chromosome 9 suggest involvement of a previously unidentified tumor suppressor gene.

Abstract  We performed three types of studies to evaluate the genotoxicity of the chlorinated organic solvent perchloroethylene (PERC or tetrachloroethylene) and its volatile metabolites, trichloroacetyl chloride (TCAC) and trichloroacetic acid (TCA), as well as the volatile metabolites of trichloroethylene, i. e. dichloroacetyl chloride (DCAC), dichloroacetic acid (DCA), and 2,2,2-trichloroethanol (TCE). In the first set of studies, which involved the evaluation of these chemicals in the Microscreen prophage-induction assay, only DCA (³S9) was genotoxic, producing 6.6–7.2 plaque-forming units/mM. This places DCA among the weakest of the >100 chemicals that have been identified previously as inducers of prophage in this assay. In the second set of studies, which involved the evaluation of these chemicals in the vapor state in Salmonella TA100 using a Tedlar® bag vaporization technique, DCA (³/–S9), DCAC (–S9), and TCAC (³/–S9) were mutagenic, producing 3–5x increases in revertants/plate relative to the background. S9 enhanced the mutagenic potency of DCA but had no effect on the mutagenic potency of TCAC. The potencies ranged from 0.7 to 3.9 rev/p. p. m., resulting in a potency ranking of DCA > DCAC {approx} TCAC. The lowest effective concentrations were 50–300 p. p. m., which are similar to those for ethylene oxide and epichlorohydrin in this assay. In the third set of studies, the mutation spectra of DCA, DCAC, and TCAC were determined at the base-substitution allele hisG46 of Salmonella TA100. DCA and DCAC induced primarily G · C {uparrow} A · T transitions, whereas TCAC induced primarily G · C {uparrow} T · A transversions, which was also the predominant mutation among the background revertants. The DCAC and DCA mutation spectra might be explained by a mutational mechanism in which the compounds are metabolized to etheno adducts on cytosine, causing the DNA polymerase to misincorporate. This report is the first demonstration of the mutagenicity of DCA and of the mutation spectrum of any of these chlorinated organics. In conjunction with previous studies, these results support consideration of a genotoxic mechanism for the carcinogenicity of PERC and trichloroethylene because of the mutagenicity of their metabolites, including DCA.

Abstract  An alkaline unwinding assay was used to quantitate the induction of DNA strand breaks (DNA SB) in the livers of rats and mice treated in vivo, in rodent hepatocytes in primary culture, and in CCRF-CEM cells, a human lymphoblastic leukemia cell line, following treatment with tri- (TCA), di- (DCA), and mono- (MCA) chloroacetic acid and their corresponding aldehydes, tri- (chloral hydrate, CH), di- (DCAA) and mono- (CAA) chloroacetaldehyde. None of the chloroacetic acids induced DNA SB in the livers of rats at 4 hr following a single administration of 1-10 mmole/kg. TCA (10 mmole/kg) and DCA (5 and 10 mmole/kg) did produce a small amount of strand breakage in mice (7% at 4 hr) but not at 1 hr. N-nitrosodiethylamine (DENA), an established alkylating agent and a rodent hepatocarcinogen, produced DNA SB in the livers of both species. TCA, DCA, and MCA also failed to induce DNA strand breaks in splenocytes and epithelial cells derived from the stomach and duodenum of mice treated in vivo. None of the three chloroacetaldehydes induced DNA SB in either mouse or rat liver. The continuous exposure of mice to 5 g/L DCA in the drinking water for 7 and 14 days did not induce appreciable hepatic DNA SB (< 10% at 14 days), although peroxisome proliferation, as evidenced by an increased cyanide-insensitive palmitoyl CoA oxidase (PCO) activity, was stimulated to 490% (7 days) and 652% (14 days) of control. Under this protocol, DENA (0.1 g/L) produced DNA damage after both 7 days (73% of control) and 14 days (57% of control). Similarly, long-term exposure of rats (30 weeks) to 2 g/L DCA in the drinking water, a level that increased PCO activity to 364% of the control value, exhibited no DNA damage. Both the chloroacetic acids and the chloroacetaldehydes were ineffective in inducing DNA SB in cultured rat and mouse hepatocytes at concentrations below those that yielded cytotoxicity. The chloroacetic acids were also ineffective in the CCRF-CEM cells. However, two of the chloroaldehydes, DCAA and CAA, did induce DNA SB in the CCRF-CEM cells at concentrations that did not decrease the cell viability after 2 hr of treatment. Prior incubation of DCAA and CAA with a rat S9 liver homogenate eliminated much of the DNA damaging activity. These studies provide further evidence that the chloroacetic acids lack genotoxic activity not only in rodent liver, a tissue in that they induce tumors, but in a variety of other rodent tissues and cultured cell types.

Abstract  Trichloroethylene (TCE) has previously been shown to be carcinogenic in mouse liver when administered by daily gavage in corn oil. The metabolism of TCE results, in part, in the formation of trichloroacetic acid (TCA) as a major metabolite and dichloroacetic acid (DCA) as a minor metabolite. These chlorinated acetic acids have not been shown to be genotoxic, although they have been shown to induce peroxisome proliferation. Therefore, we determined the ability they have been shown to induce peroxisome proliferation. Therefore, we determined the ability of TCE, TCA, or DCA to act as tumor promoters in mouse liver. Male B6C3F1 mice were administered intraperitoneally 0, 2.5, or 10 micrograms/g body wt ethylnitrosourea (ENU) on Day 15 of age. At 28 days of age, the mice were placed on drinking water containing either TCE (3 or 40 mg/liter), TCA (2 or 5 g/liter), or DCA (2 or 5 g/liter). All drinking waters were neutralized with NaOH to a final pH of 6.5-7.5. The animals were killed after 61 weeks of exposure to the treated drinking water (65 weeks of age). Both DCA and TCA at a concentration of 5 g/liter were carcinogenic without prior initiation with ENU, resulting in hepatocellular carcinomas in 81 and 32% of the animals, respectively. DCA and TCA also increased the incidence of animals with adenomas and the number of adenomas/animal in those animals that were not initiated with ENU. While 2.5 micrograms/g body wt ENU followed by NaCl in the drinking water resulted in only 5% of the animals with hepatocellular carcinomas, 2.5 micrograms/g body wt ENU followed with 2 or 5 g/liter DCA resulted in a 66 or 78% incidence of carcinoma, respectively, or, followed with 2 or 5 g/liter TCA, resulted in a 48% incidence at either concentration. None of the untreated animals had hepatocellular carcinomas. Therefore our results demonstrate that DCA and TCA are complete hepatocarcinogens in B6C3F1 mice.

Abstract  Dichloroacetic acid (DCA) and trichloroacetic acid (TCA) are found in drinking water and are metabolites of trichloroethylene. They are carcinogenic and promote liver tumors in B6C3F1 mice. Hypomethylation of DNA is a proposed nongenotoxic mechanism involved in carcinogenesis and tumor promotion. We determined the effect of DCA and TCA on the level of DNA methylation in mouse liver and tumors. Female B6C3F1 mice 15 days of age were administered 25 mg/kg N-methyl-N-nitrosourea and at 6 weeks started to receive 25 mmol/liter of either DCA or TCA in their drinking water until euthanized 44 weeks later. Other animals not administered MNU were euthanized after 11 days of exposure to either DCA or TCA. DNA was isolated from liver and tumors, and after hydrolysis 5-methylcytosine (5MeC) and the four bases were separated and quantitated by HPLC. In animals exposed to either DCA or TCA for 11 days but not 44 weeks, the level of 5MeC in DNA was decreased in the liver. 5MeC was also decreased in liver tumors from animals exposed to either chloroacetic acid. The level of 5MeC in TCA-promoted carcinomas appeared to be less than in adenomas. Termination of exposure to DCA, but not to TCA, resulted in an increase in the level of 5MeC in adenomas to the level found in noninvolved liver. Thus, hypomethylated DNA was found in DCA and TCA promoted liver tumors and the difference in the response of DNA methylation to termination of exposure appeared to support the hypothesis of different mechanisms for their carcinogenic activity.

Abstract  Dichloroacetic acid (DCA) and trichloroacetic acid (TCA) are major metabolites of tetrachloroethylene (PCE) and trichloroethylene (TCE) and are found in chlorinated drinking water. All four chlorinated compounds are liver carcinogens in B6C3F1 mice. It has previously been reported that approximately 20% of hepatic tumors induced by PCE exhibited loss of heterozygosity (LOH) on chromosome 6, suggesting the presence of a tumor suppressor gene. In the current investigation, we determined whether TCA or DCA also induced LOH on chromosome 6. Liver tumors were initiated in 15 day old female B6C3F1 mice with N-methyl-N-nitrosourea (MNU) and promoted with 20 mmol/l DCA or TCA in their drinking water. Twenty-four and thirty-seven liver tumors promoted by DCA and TCA, respectively, were examined for LOH using 4 polymorphic loci on chromosome 6. Ten of 37 (27%) tumors (7 of 27 carcinomas and 3 of 10 adenomas) promoted by TCA exhibited LOH at least for two loci on chromosome 6. All 10 tumors that exhibited LOH, lost the C57BL/6J allele at both the D6mit9 loci, while two also lost at least one of the C3H/HeJ alleles. No LOH on chromosome 6 was observed in the 24 liver tumors promoted by DCA. The LOH on chromosome 6 in TCA but not in DCA-promoted tumors supports it as an active metabolite of PCE and demonstrates different pathogenesis at least for some of the DCA and TCA-promoted liver cancer.

Abstract  Dichloroacetic acid (DCAA) and trichloroacetic acid (TCAA) are major nonvolatile disinfection by-products of water chlorination. These compounds are currently being considered for regulation because of potential adverse health effects. In the current study, DCAA and TCAA dermal exposures were investigated in four human subjects during a thirty minute walk or swim in a pool by measuring the pool water concentrations and urinary excretion rates of DCAA and TCAA. These two compounds were eliminated in urine within approximately 3 hours of the exposure, with the dermal DCAA dose being ~6 mug from pool water containing 600 mug/L. The amount of water ingested by each subject during a 30 minute swim was estimated to be between 12 and 45 mL. The DCAA permeability coefficient at pH 7 was calculated to be between 1 and 8 x 10sup -sup 3 cm/h, when assuming that only 3% of the dermal dose, as was observed for ingestion, was excreted and between 2 and 9 x 10sup -sup 5 cm/h, assuming that 48% of the dermal dose, an upper limit, was excreted. Exposure estimates indicate that ingestion is the major route of exposure and that the dermal contribution during typical household uses is a minor contributor to the total exposure of these compounds from chlorinated drinking water

Abstract  Peroxisome proliferators, such as lipid-lowering fibrate drugs, are agonists for the peroxisome proliferator-activated receptor alpha (PPARalpha). Sustained activation of PPARalpha leads to the development of liver tumors in rodents. Paradoxically, humans appear to be resistant to the induction of peroxisome proliferation and development of liver tumors by peroxisome proliferators. To examine the species differences in response to peroxisome proliferators, a PPARalpha humanized mouse (hPPARalpha) was generated, in which the human PPARalpha was expressed in liver under control of the Tet-OFF system. To evaluate the susceptibility of hPPARalpha mice to peroxisome proliferator-induced hepatocarcinogenesis, a long-term feeding study of Wy-14,643 was carried out. hPPARalpha and wild-type (mPPARalpha) mice were fed either a control diet or one containing 0.1% Wy-14,643 for 44 and 38 weeks, respectively. Gene expression analysis for peroxisomal and mitochondrial fatty acid metabolizing enzymes revealed that both hPPARalpha and mPPARalpha were functional. However, the incidence of liver tumors including hepatocellular carcinoma was 71% in Wy-14,643-treated mPPARalpha mice, and 5% in Wy-14,643-treated hPPARalpha mice. Upregulation of cell cycle regulated genes such as cd1 and Cdks were observed in non-tumorous liver tissue of Wy-14,643-treated mPPARalpha mice, whereas p53 gene expression was increased only in the livers of Wy-14,643-treated hPPARalpha mice. These findings suggest that structural differences between human and mouse PPARalpha are responsible for the differential susceptibility to the peroxisome proliferator-induced hepatocarcinogenesis. This mouse model will be useful for human cancer risk assessment of PPARalpha ligands.

Abstract  Peroxisome proliferator chemicals (PPC) are thought to mediate their effects in rodents on hepatocyte growth and liver cancer through the nuclear receptor peroxisome proliferator-activated receptor (PPAR) alpha. Recent studies indicate that the plasticizer di-(2-ethylhexyl) phthalate (DEHP) increased the incidence of liver tumors in PPARalpha-null mice. We hypothesized that some PPC, including DEHP, induce transcriptional changes independent of PPARalpha but dependent on other nuclear receptors, including the constitutive-activated receptor (CAR) that mediates phenobarbital (PB) effects on hepatocyte growth and liver tumor induction. To determine the potential role of CAR in mediating effects of PPC, a meta-analysis was performed on transcript profiles from published studies in which rats and mice were exposed to PPC and compared the profiles to those produced by exposure to PB. Valproic acid, clofibrate, and DEHP in rat liver and DEHP in mouse liver induced genes, including Cyp2b family members that are known to be regulated by CAR. Examination of transcript changes by Affymetrix ST 1.0 arrays and reverse transcription-PCR in the livers of DEHP-treated wild-type, PPARalpha-null, and CAR-null mice demonstrated that (1) most (approximately 94%) of the transcriptional changes induced by DEHP were PPARalpha-dependent, (2) many PPARalpha-independent genes overlapped with those regulated by PB, (3) induction of genes Cyp2b10, Cyp3a11, and metallothionine-1 by DEHP was CAR dependent but PPARalpha-independent, and (4) induction of a number of genes (Cyp8b1, Gstm4, and Gstm7) was independent of both CAR and PPARalpha. Our results indicate that exposure to PPARalpha activators including DEHP leads to activation of multiple nuclear receptors in the rodent liver.

Abstract  DNA methylation is an important epigenetic mechanism involved in transcriptional control and altered patterns of methylation may lead to the aberrant gene expression contributing to carcinogenesis. Three groups of mice were used in the current study: the relatively liver-tumor-sensitive C3H/He strain and B6C3F1 stock (C57BL/6xC3H/He), as well as the relatively resistant C57BL/6 strain. For a 2-week period, animals from each group were given drinking water containing a tumor-promoting dose of phenobarbital (PB), a nongenotoxic rodent carcinogen. Methylation-sensitive restriction digests using HpaII or MspI were followed by PCR amplification using an arbitrary primer or primer pair, binding preferentially to guanine and cytysine (GC)-rich regions of DNA, including CpG islands. This procedure allows for assessment of methylation at the internal and/or external cytosine of the 5'-CCGG-3' sites recognized by MspI and HpaII. Results with the single primer indicated marked differences in PB-induced hypermethylation at external and internal cytosines of 5'-CCGG-3' sites: C3H/He > B6C3F1 > C57BL/6. Results with the arbitrary primer pair indicated PB-induced hypermethylation at the external cytosine of 5'-CCGG-3' site: B6C3F1 > C3H/He, and a low level of hypomethylation at internal and external cytosine sites in C57BL/6. Thus, there was a clear indication of more methylation changes in GC-rich regions of DNA, primarily hypermethylation, in the tumor-sensitive groups of mice in response to PB treatment. Therefore, this study supports our hypothesis that the capacity to maintain normal methylation patterns is related inversely to tumor susceptibility.

Abstract  The validity of mouse liver tumor end points in assessing the potential hazards of chemical exposure to humans is a controversial but important issue, since liver neoplasia in mice is the most frequent tumor target tissue end point in 2-year carcinogenicity studies. The ability to distinguish between promotion of background tumors versus a genotoxic mechanism of tumor initiation by chemical treatment would aid in the interpretation of rodent carcinogenesis data. Activated oncogenes in chemically induced and spontaneously occurring mouse liver tumors were examined and compared as one approach to determine the mechanism by which chemical treatment caused an increased incidence of mouse liver tumors. Data suggest that furan and furfural caused an increased incidence in mouse liver tumors at least in part by induction of novel weakly activating point mutations in ras genes even though both chemicals did not induce mutations in Salmonella assays. In addition to ras oncogenes, two activated raf genes and four non-ras transforming genes were detected. The B6C3F1 mouse liver may thus provide a sensitive assay system to detect various classes of proto-oncogenes that are susceptible to activation by carcinogenic insult. As illustrated with mouse liver tumors, analysis of activated oncogenes in spontaneously occurring and chemically induced rodent tumors will provide information at a molecular level to aid in the use of rodent carcinogenesis data for risk assessment.

Abstract  Interest in insulin-like growth factors (IGFs) and their effect on carcinogenesis has increased recently because high serum concentrations of IGF1 are associated with an increased risk of breast, prostate, colorectal, and lung cancers. Physiologically, IGF1 is the major mediator of the effects of the growth hormone; it thus has a strong influence on cell proliferation and differentiation and is a potent inhibitor of apoptosis. The action of IGF1 is predominantly mediated through the IGF1 receptor (IGF1R). IGF1R is involved in several oncogenic transformation processes. The availability of unbound IGF1 for interaction with IGF1R is modulated by IGF-binding proteins (IGFBP1-6). IGFBPs, especially IGFBP3, have independent effects on cell growth, for example, IGFBP3 has proapoptotic activities both dependent on and independent of p53.

Abstract  We previously reported that metabolism of chloral hydrate (CH), a widely used sedative and hypnotic, by male B6C3F1 mouse liver microsomes resulted in lipid peroxidation, producing the tumorigen malondialdehyde (MDA). Now we have found that incubation of CH in the presence of calf thymus DNA resulted in the formation of an MDA-modified DNA adduct as detected by 32P-postlabeling analysis. Similar results were obtained from incubation of trichloroacetic acid and trichloroethanol, both metabolites of CH.

Abstract  Several decades of basic and clinical research have demonstrated that there is an association between the insulin-like growth factors (IGFs) and neoplasia. We begin with a brief discussion of the function and regulation of expression of the IGFs, their receptors and the IGF-binding proteins (IGFBPs). A number of investigational interventional strategies targeting the GH or IGFs are then reviewed. Finally, we have assembled the available scientific knowledge about this relationship for each of the major tumor types. The tumors have been grouped together by organ system and for each of the major tumors, various key elements of the relationship between IGFs and tumor growth are discussed. Specifically these include the presence or absence of autocrine IGF-I and IGF-II production; presence or absence of IGF-I and IGF-II receptor expression; the expression and functions of the IGFBPs; in vitro and in vivo experiments involving therapeutic interventions; and available results from clinical trials evaluating the effect of GH/IGF axis down-regulation in various malignancies.

Abstract  Neoplastic cells simultaneously harbor widespread genomic hypomethylation, more regional areas of hypermethylation, and increased DNA-methyltransferase (DNA-MTase) activity. Each component of this "methylation imbalance" may fundamentally contribute to tumor progression. The precise role of the hypomethylation is unclear, but this change may well be involved in the widespread chromosomal alterations in tumor cells. A main target of the regional hypermethylation are normally unmethylated CpG islands located in gene promoter regions. This hypermethylation correlates with transcriptional repression that can serve as an alternative to coding region mutations for inactivation of tumor suppressor genes, including p16, p15, VHL, and E-cad. Each gene can be partially reactivated by demethylation, and the selective advantage for loss of gene function is identical to that seen for loss by classic mutations. How abnormal methylation, in general, and hypermethylation, in particular, evolve during tumorigenesis are just beginning to be defined. Normally, unmethylated CpG islands appear protected from dense methylation affecting immediate flanking regions. In neoplastic cells, this protection is lost, possibly by chronic exposure to increased DNA-MTase activity and/or disruption of local protective mechanisms. Hypermethylation of some genes appears to occur only after onset of neoplastic evolution, whereas others, including the estrogen receptor, become hypermethylated in normal cells during aging. This latter change may predispose to neoplasia because tumors frequently are hypermethylated for these same genes. A model is proposed wherein tumor progression results from episodic clonal expansion of heterogeneous cell populations driven by continuous interaction between these methylation abnormalities and classic genetic changes.

Abstract  A series of straight and branched chain phthalate monoesters were examined for their effects on hepatocyte intercellular communication in male B6C3F1 mouse hepatocytes. Intercellular communication was determined autoradiographically following the passage and incorporation of [5-3H]uridine nucleotides from pre-labelled hepatocytes into non-labelled hepatocytes. Intercellular communication was evaluated in hepatocytes after 8 h treatment of straight and branched chain phthalate esters at sublethal concentrations. Straight chain phthalate monoesters (mono(ethyl)phthalate, mono(n-butyl) phthalate, mono(n-hexyl)phthalate, mono(n-octyl)phthalate, mono(n-nonyl)phthalate and mono(isononyl)phthalate) had no effect on hepatocyte intercellular communication. Branched chain phthalate monoesters that contained an ethylalkyl moiety (i.e. mono(2-ethylpropyl) phthalate, mono(2-ethylbutyl)phthalate, mono(2-ethylpentyl)-phthalate and mono(2-ethylhexyl)phthalate) inhibited intercellular communication. These results show a structure-activity relationship in the ability of phthalate monoesters to inhibit intercellular communication in mouse hepatocytes. Based upon previous correlations between inhibition of intercellular communication in hepatocytes and hepatocarcinogenicity, these data suggest that branched chain phthalate esters may be liver carcinogens in male B6C3F1 mice.

Abstract  Dichloroacetic acid (DCA) arises from the chlorination of drinking water and the metabolism of trichloroethylene (TRI) and is used therapeutically. The toxicity of TRI exposure is dependent on metabolism, and DCA has been proposed to be one contributor to this toxicity. Beyond the identification of some metabolites of DCA and some pharmacokinetic studies, little is known about the tissue distribution and enzymology of DCA metabolism. We present data that indicate that DCA degradation occurs primarily in the cytosol. Low molecular weight components of cytosol are required for the reaction, including nicotinamide cofactor and glutathione (GSH). GSH plays a role in the removal of DCA from cytosol, although not through transferase-mediated conjugation. In rat cytosol, the KM is approximately 0.3 mM, and the apparent Vmax approximates 12 nmoles/min/mg cytosolic protein. These results set DCA apart from other chlorinated compounds that are metabolized by the cytochrome P450 enzyme family

Abstract  Trichloroacetic acid (TCA), a mouse liver carcinogen, is a drinking water contaminant and a metabolite of solvents such as trichloroethylene and perchloroethylene. Because acidic drugs are often bound more strongly to human than to rodent plasma proteins, a study was undertaken to determine whether this was the case for TCA and to clarify the mechanistic bases for species differences. Equilibrium dialysis was used to measure in vitro binding of a range of TCA concentrations to plasma of humans, rats, and mice. Plots of observed data for free versus bound TCA concentrations were compared with simulations from each of three binding models: a single saturable site model; a saturable plus nonsaturable site model; and a two-saturable site model. Dissociation values (Kd) did not differ significantly from one species to another, but N (number of binding sites/molecule) ranged from 2.97 for humans to 0.17 for mice. Binding capacities (Bmax) for humans, rats, and mice were 709, 283, and 29 microM, respectively. The greater plasma protein binding of TCA in humans would be expected to not only increase the residence time of the compound in the bloodstream, but to substantially reduce the proportion of TCA that is available for uptake by the liver and other tissues. Species differences in the bound fraction diminished at very low, environmentally relevant TCA concentrations, but the percentage bound increased markedly. These findings suggest that the practice of using total blood levels of TCA as a dose metric in interspecies extrapolation of cancer risks needs to be re-examined

Abstract  1. Both trichloroethylene and its metabolite, dichloroacetic acid, produce liver tumors peroxisome proliferation and other adverse cellular alterations in rodents. 2. The hepatic mechanism by which dichloroacetic acid is formed is not conclusively demonstrated, but pharmacokinetic models have successfully associated its formation with trichloroacetic acid as immediate precursor. 3. Previous investigations have shown that dichloroacetic acid is formed from trichloroacetic acid by gut microflora isolated in vitro. 4. To determine the impact of gut microflora on dichloroacetic acid formation from a trichloroethylene dose in vivo, we developed a procedure which reduced gut microflora some 3 orders of magnitude below published levels. 5. The administration of trichloroethylene to control mice and to mice whose gut was practically sterile resulted in equivalent concentrations of dichloroacetic acid and other metabolites in blood and liver, but significantly different content of these metabolites in cecum contents. 6. These data indicate that gut microflora contribute minimally, if at all, to the formation of circulating dichloroacetic acid under these conditions

Abstract  Trichloroacetic acid (TCA) is a by-product of the chlorine disinfection of water containing natural organic material. It is detectable in finished drinking water at levels comparable to the trihalomethanes (30-160 micrograms/L). TCA is also formed in vivo after ingestion of hypochlorite and has been identified as a major metabolite of chlorinated hydrocarbons such as trichloroethylene. The developmental effects of TCA were evaluated in the pregnant Long-Evans rat. Animals were dosed by oral intubation on gestation days 6-15 (plug = 0) with 0, 330, 800, 1,200, or 1,800 mg/kg/day. The vehicle control was distilled water. Maternal observations included clinical signs, weight change, and gross evaluation of organ weights and uterine contents at necropsy (day 20). Live fetuses were examined for external, skeletal, and soft tissue malformation. There were no maternal deaths associated with toxicity prior to sacrifice. Weight gain during treatment was reduced at 800, 1,200, and 1,800 mg/kg. Spleen and kidney weights were increased in a dose-related manner. The mean percent of resorbed implants per litter was 34, 62, and 90 at 800, 1,200, and 1,800 mg/kg, respectively. Live fetuses showed dose-dependent reductions in weight and length. The mean frequency of soft tissue malformations ranged from 9% at the low dose to 97% at the high dose. These were principally in the cardiovascular system (interventricular septal defect, levocardia). Skeletal malformations were found only at 1,200 and 1,800 mg/kg and were mainly in the orbit. Based on these observations TCA was considered to be developmentally toxic in the pregnant rat at doses of 330 mg/kg and above.

Abstract  Dichloroacetate (DCA) and trichloroacetate (TCA) are two hepatocarcinogenic by-products of water chlorination. To compare the effects of DCA and TCA on cell replication in the nodules and tumors they induce, male B6C3F1 mice were administered 2.0 g/L DCA or TCA in their drinking water for 38 or 50 weeks, respectively. The pretreated mice were then given water containing 0, 0.02, 0.5, 1.0, or 2.0 g/L DCA or TCA for two additional weeks to determine whether cell proliferation in the normal liver or tumors that had been induced by DCA or TCA was dependent on continued treatment. Prior to sacrifice the mice were subcutaneously implanted with mini-osmotic pumps to label DNA in dividing cells with 5-bromo-2'-deoxyuridine (BrdU). Serial sections of nodules/tumors and normal liver were stained immunohistochemically for BrdU, the oncoproteins c-Jun and c-Fos, and hematoxylin and eosin (H & E); or with Periodic acid-Schiff (PAS) stain, BrdU, and H & E, respectively. DCA and TCA transiently stimulated the division of normal hepatocytes relative to rates observed in the livers of control mice. However, at 40 and 52 weeks of treatment, replication of normal hepatocytes was substantially inhibited by DCA and TCA, respectively. Cell division within DCA-induced lesions that were identified macroscopically was significantly higher with increasing dose of DCA administered in the last 2 weeks of the experiment. DCA-induced lesions were found to display immunoreactivity to anti-c-Jun and anti-c-Fos antibodies, were predominantly basophilic, and contained very little glycogen relative to surrounding hepatocytes. In contrast, rates of cell division within TCA-induced altered hepatic foci and tumors were very high and appeared to be independent of continued treatment. TCA-induced lesions did not display immunoreactivity to either c-Jun or c-Fos antibodies. Results from this study suggest that the mechanisms by which DCA and TCA induce hepatocarcinogenesis in the male B6C3F1 mouse differ.

Abstract  #WY-14,643 [4-chloro-6-(2,3-xylidino)pyrimidinylthio-acetic acid] is a well-known non-genotoxic carcinogen and peroxisome proliferator that causes liver cancer in rodents by unknown mechanisms. Its ability to sustain elevated rates of hepatocyte DNA synthesis is most likely pivotal in the ultimate development of tumors. The source of this mitogenic stimulus following treatment of rats with WY-14,643 has been hypothesized to be Kupffer cells, the resident hepatic macrophages, since they are activated by peroxisome proliferators in vivo. Therefore, these studies were designed to determine if Kupffer cells are causally responsible for WY-14 643-induced increases in hepatocyte DNA synthesis in vivo. WY-14,643 (100 mg/kg) increased DNA synthesis 8- fold 24 h after treatment; however, inactivation of Kupffer cells with methyl palmitate, a nonhydrolyzable fatty acid ester and known Kupffer cell inhibitor, completely prevented the mitogenic effect of WY-14,643. On the other hand, the ability of WY-14,643 to induce peroxisomes was not affected by methyl palmitate. These data demonstrate that induction of peroxisomes is not dependent on factors from Kupffer cells and support the idea that stimulation of DNA synthesis and induction of peroxisomes occur via distinct mechanisms. Additionally, WY-14,643 increased liver mRNA transcripts of the hepatocyte mitogen tumor necrosis factor alpha (TNF alpha) more than twofold. This increase was also prevented by inactivating Kupffer cells with methyl palmitate. Therefore, it is concluded that Kupffer cells are causally responsible for WY-14,643-induced increases in hepatocyte DNA synthesis most likely by increasing production of TNF alpha, a hepatic mitogen.

Abstract  A very considerable body of data pertaining to the atmospheric behaviour of hydrochlorofluorocarbons (HCFCs) and chlorinated solvents is now available and leads to the following conclusions: (a) these compounds, with the exception of 1,1,1-trichloroethane, make a small or insignificant contribution to stratospheric ozone depletion, global warming, æphoto-chemical smog', æacid rain', or chloride and fluoride levels in precipitation; (b) it seems highly unlikely that the chlorinated solvents degrade in the atmosphere to give chloroacetic acids as major products, as has often been claimed in the literature.