B6C3F1 Mouse Liver Research Articles

Induction of mutations by 2-acetylaminofluorene in lacI transgenic B6C3F1 mouse liver.

Mutations induced in liver cells by the hepatocarcinogen 2-acetylaminofluorene (2-AAF) were characterized after i.p. administration on 4 consecutive days at 100 mg/kg per injection in male B6C3F1 Big Blue transgenic mice that harbored the Escherichia coli lacI reporter gene. Animals were sacrificed at 5, 10 or 60 weeks following the last injection, livers removed and DNA packaged in vitro into bacteriophage lambda particles. The bacteriophage were assayed for lacI function by plating on E. coli in the presence of X-gal. Approximately 3 x 10(5) plaques were assayed per animal. Solvent-treated control mice exhibited a slight increase in mutant frequency over time, from 3.93 x 10(-5) at 5 weeks to 5.02 x 10(-5) at 60 weeks. In contrast, treatment with 2-AAF yielded an approximately 2-fold increase in mutant frequency at 5 and 10 weeks after treatment relative to controls, with frequencies of 8.13 x 10(-5) and 7.43 x 10(-5) respectively. However, by 60 weeks post-treatment the mutant frequency was not significantly increased over concurrent controls. Similar to results in other systems, 2-AAF induced predominantly single base changes targeted to G:C base pairs, primarily G:C-->T:A transversions (27%). In contrast to results in other bacterial and eukaryotic systems, no deletions were observed among the 2-AAF-induced mutations and the 4 base hot spot deletion that is frequently observed in lacI in E. coli was not observed in this system, suggesting that the lacI transgene may be relatively refractory to frameshift mutations in vivo in the mouse.

Differential display identified changes in mRNA levels in regenerating livers from chloroform-treated mice.

The nongenotoxic-cytotoxic carcinogen chloroform induces liver necrosis, regenerative cell proliferation, and, eventually, liver tumors in female B6C3F1 mice when administered by gavage at doses of 238 or 477 mg/kg/d. Administration of 1800 ppm of chloroform in the drinking water results in similar daily doses but does not produce liver toxicity or cancer. The differential-display technique was used to compare the expression of a subset of mRNAs in normal (control) and regenerating liver after chloroform-induced toxicity to define the proportion of genes whose expression changes under hepatotoxic conditions and to identify the genes that might play a role in regeneration and perhaps cancer. RNA was purified from the livers of female B6C3F1 mice after 4 d or 3 wk of gavage treatment with 3, 238, or 477 mg/kg/d of chloroform or treatment with 1800 ppm chloroform in drinking water. There was a remarkably high degree of consistency of gene expression among the animals and across dose and treatment groups as visualized by the differential-display technique. Of the 387 bands observed, only four (about 1%) changed expression in regenerating liver. The genes were assigned locus names by GenBank after sequence submission. The genes with increased mRNA levels as confirmed by northern blot analysis were MUSTIS21, a mouse primary response gene induced by growth factors and tumor promoters; MUSMRNAH, a gene highly homologous to a human gene isolated from a prostate carcinoma cell line; and MUSFRA, a novel gene. The novel gene MUSFRB exhibited decreased mRNA levels. No change in expression was seen among control mice given the nontoxic regimens of 3 mg/kg/d chloroform or 1800 ppm chloroform in drinking water, indicating that changes in expression were associated with toxicity and regeneration rather than chloroform per se. These genes and others that may be identified by expanding this approach may play a role in regeneration and perhaps in the process of chloroform-induced carcinogenesis in rodent liver.

Assessment of the mutagenicity of dichloroacetic acid in lacI transgenic B6C3F1 mouse liver.

Dichloroacetic acid (DCA) is a chlorination byproduct found in finished drinking water. When administered in drinking water this chemical has been shown to produce hepatocellular adenomas and carcinomas in B6C3F1 mice over the animal's lifetime. In this study, we investigated whether mutant frequencies were increased in mouse liver using treatment protocols that yielded significant tumor induction. DCA was administered continuously at either 1.0 or 3.5 g/l in drinking water to male transgenic B6C3F1 mice harboring the bacterial lacI gene. Groups of five or six animals were killed at 4, 10 or 60 weeks and livers removed. At both 4 and 10 weeks of treatment, there was no significant difference in mutant frequency between the treated and control animals at either dose level. At 60 weeks, mice treated with 1.0 g/l DCA showed a 1.3-fold increase in mutant frequency over concurrent controls (P = 0.05). Mice treated with 3.5 g/l DCA for 60 weeks had a 2.3-fold increase in mutant frequency over the concurrent controls (P = 0.002). The mutation spectrum recovered from mice treated with 3.5 g/l DCA for 60 weeks contained G:C-->A:T transitions (32.79%) and G:C-->T:A transversions (21.31%). In contrast, G:C-->A:T transitions comprised 53.19% of the recovered mutants among control animals. Although only 19.15% of mutations among the controls were at T:A sites, 32.79% of the mutations from DCA-treated animals were at T:A sites. This is consistent with the previous observation that the proportion of mutations at T:A sites in codon 61 of the H-ras gene was increased in DCA-induced liver tumors in B6C3F1 mice. The present study demonstrates DCA-associated mutagenicity in the mouse liver under conditions in which DCA produces hepatic tumors.

Dissimilar characteristics of N-methyl-N-nitrosourea-initiated foci and tumors promoted by dichloroacetic acid or trichloroacetic acid in the liver of female B6C3F1 mice.

Dichloroacetic acid (DCA) and trichloroacetic acid (TCA) are metabolites of the industrial solvent and environmental contaminant trichloroethylene (TCE), as well as contaminants of chlorinated drinking water. Human exposure to these chemicals is of concern as all three have been shown to increase liver tumor incidence in mice. Differences in dose-response curves, progression to cancer, and postexposure regression of lesions suggest that TCA and DCA work through different mechanisms. The purpose of this study was to further characterize the proliferative hepatocellular lesions promoted by TCA and DCA using biomarkers of cell growth, differentiation, and metabolism in liver sections to better delineate the distinctions in the mechanism of the two chloroacetates. Fifteen-day-old female mice were initiated with 25 mg/kg N-methyl-N-nitrosourea. The initiated mice were administered DCA or TCA (20.0 mmol/L) in drinking water from age 49 days until euthanasia at age 413 days. The pathologic assessment showed that the foci of altered hepatocytes and tumors occurring in the animals promoted with DCA were eosinophilic and positive immunohistochemically for TGF-alpha, c-jun, c-myc, CYP 2E1, CYP 4A1, and glutathione S-transferase-pi (GST-pi). The DCA lesions also were essentially negative for c-fos and TGF-beta, but nontumor hepatocytes were consistently TGF-beta-positive. In contrast, tumors promoted by TCA were predominantly basophilic, lacked GST-pi, and stained variably; usually, more than 50% of the tumor hepatocytes were essentially negative for the other biomarkers. This study demonstrates some striking differences in certain molecular biomarkers of cell growth, differentiation, and metabolism between DCA and TCA. The results also suggest some potential growth signal transduction pathways that may contribute to the DCA promotion of tumors, further support the premise that these two chloroacetates promote hepatocarcinogenesis in different ways, and provide a rational basis for a similar comparison with TCE. Such a comparison should give some insight as to whether DCA, TCA, or both are playing a significant role in the murine liver carcinogenesis of the parent compound, TCE.

Promotion by mixtures of dichloroacetic acid and trichloroacetic acid of N-methyl-N-nitrosourea-initiated cancer in the liver of female B6C3F1 mice.

Hepatic tumor promoting activity was determined for mixtures of dichloroacetic acid (DCA) and trichloroacetic acid (TCA) in female B6C3F1 mice initiated on day 15 of age with 25 mg/kg N-methyl-N-nitrosourea. The mice received in their drinking water from 6 to 50 weeks of age either DCA (7.8, 15.6, or 25 mmol/l) with/without 6.0 mmol/l TCA or TCA (6.0 or 25 mmol/l) with/without 15.6 mmol/l DCA. Proliferative lesions (foci of altered hepatocytes and hepatocellular adenomas) promoted by TCA increased linearly with its concentration and were predominantly basophilic and negative for glutathione S-transferase-pi (GST-pi), while those promoted by DCA increased exponentially with its concentration and were eosinophilic and positive for GST-pi. The promoting activity of DCA and TCA in mixtures was at least additive. The proliferative lesions resulting from exposure to the mixtures were predominately similar to those promoted by DCA, i.e. contained eosinophilic and GST-pi-positive hepatocytes.

Loss of tumor-promoting activity of unleaded gasoline in N-nitrosodiethylamine-initiated ovariectomized B6C3F1 mouse liver.

Unleaded gasoline (UG) vapor (2056 ppm) increased the incidence of liver tumors in a chronic bioassay and exhibited tumor-promoting activity in N-nitrosodiethylamine (DEN)-initiated female mouse liver. Estrogen inhibited mouse liver tumor development and the hepatocarcinogenic and tumor-promoting dose of UG produced uterine changes suggestive of estrogen antagonism. To directly test the hypothesis that UG-induced tumor-promoting ability is secondary to its interaction with the mouse liver tumor inhibitor, estrogen, we compared the tumor-promoting ability of UG in ovariectomized (Ovex) mice with the hepatic tumor-promoting ability of UG in intact mice. Ovaries were surgically removed at 4 weeks of age. Exposure to wholly vaporized UG (2018 ppm) under bioassay and tumor-promoting conditions began at 8 weeks of age. After 4 months of exposure, UG increased relative liver weight and hepatic microsomal cytochrome P450 pentoxyresourfin-O-dealkylase and ethoxyresorufin-O-deethylase activity to a similar extent in intact and Ovex mice. Non-focal hepatocyte proliferation, as measured by the incorporation of bromo-deoxyuridine, was not changed by UG exposure and was similar in all treatment groups. After 4 months of exposure to DEN-initiated mice, UG significantly increased the volume fraction of liver occupied by foci (three-fold) as compared to control intact mice. As expected, volume of foci was elevated in DEN/Ovex/control mice as compared to DEN/intact/control mice. In DEN/Ovex mice UG did not significantly increase the focal volume fraction. Thus, the tumor promoting activity of UG, as demonstrated by increased volume fraction of liver occupied by hepatic foci in intact mice, is greatly attenuated in Ovex mice. The volume fraction data in Ovex mice support the hypothesis that the tumor promoting activity of UG is dependent upon the interaction of UG with ovarian hormones. These data also indicate that hepatic microsomal cytochrome P450 PROD and EROD induction, hepatomegaly and non-focal hepatic LI are not specific markers of hepatic tumor promoting activity of UG.

Genomic Instability, as Measured by Microsatellite Alterations, Is Not Associated with Liver Tumor Development in the Genetically Susceptible B6C3F1 Mouse

Certain human heritable forms of colon cancer have characteristically high frequencies of microsatellite alterations. These microsatellite changes are markers of genomic instability and the direct consequence of mutations in genes involved with DNA mismatch repair processes, which are in part responsible for maintaining the sequence integrity of the genome. Given that the B6C3F1 mouse is genetically predisposed to develop liver tumors we were interested in determining whether tumors derived in this strain of mouse may contain alterations in microsatellite sequences. The analysis of 48 tumors at 24 different microsatellite loci revealed that microsatellite alterations were detected in 12 of 48 tumors (25%). Although this frequency is relatively high, 11 of the 12 tumors exhibited only a single alteration and in 10 of those tumors this change was at the same microsatellite locus. Microsatellite alterations were also detected in the DNA isolated from 6 of 22 (27%) normal liver tissues with 4 of the 6 occurring at the same locus where the majority of changes were observed in the tumors. Based on these results, we conclude that the microsatellite alterations present in the mouse liver tumor tissue are most likely the result of spontaneous mutational events. Consequently, the genomic instability operational in a particular type of hereditary human colon cancer does not appear to be operational in the genetically predisposed B6C3F1 mouse liver. In addition, we demonstrated that the activation of the H-rasgene, which causes some forms of genetic instabilityin vitro,does not contribute to genetic instability within liver tumors as measured by microsatellite alterations.

Analysis of Ha-ras Gene in the B6C3F1 Mouse Liver by Non-RI PCR-SSCP.

The codon 61 of the activated Ha-ras gene is detected most frequently among mutations of proto-oncogenes in spontaneously-occurring hepatocellular tumors in B6C3F1 mice. In the present study, the ras mutations and their patterns in normal liver tissue, foci of cellular alteration (FCA), and hepatocellular tumor from untreated mice were analyzed using the non-RI PCR-SSCP method. The Ha-ras gene with mutated codon 61 was detected in 1.6% (2/122) from normal liver tissues, 16.7% (6/36) from spontaneous FCA tissues, 30.4% (48/158) from spontaneous hepatocellular tumor tissues, and 7.7% (3/39) from normal portion in spontaneous hepatocellular tumor tissues. Furthermore, mutation in the Ha-ras gene was compared between spontaneous and induced hepatocellular proliferative lesions including hepatocellular tumor from archival materials at our Center. Although no clear difference was found between genotoxic carcinogen and non-genotoxic carcinogens in the incidence of Ha-ras gene mutation in the induced tumors, the incidence of Ha-ras gene mutation in FCA, which was induced by genotoxic carcinogen, was higher than that in FCA induced by non-genotoxic carcinogens. These data suggested that to analyze the incidence of Ha-ras gene mutation in proliferative lesions in the livers of B6C3F1 mice, especially in the FCA is useful in evaluation of hepatocarcinogenicity of the chemicals.

In vitro quantitative determination of phospholipid adducts of chloroform intermediates in hepatic and renal microsomes from different rodent strains

We have comparatively studied in vitro the oxidative and reductive pathways of chloroform metabolism in hepatic and renal microsomes of rodent strains used for carcinogenicity testing (B6C3F1 mice, Osborne Mendel and Sprague Dawley rats). To this aim we exploited the regioselective binding of phosgene to phospholipid (PL) polar heads and of dichloromethyl radical to PL fatty acyl chains, using a method based on the chemical transmethylation of PL adducts, followed by phase partitioning of the resulting products (De Biasi et al., 1992). The analysis of results let us to conclude at first that a 14C label partitioning by 89.2 (±6.5)% or 13.7 (±5.0)% in the aqueous phase is typical of the PL adduct with phosgene (PL-PHOS) or with dichloromethyl radical (PL-RAD), respectively. Metabolism of 0.1 mM CHCl 3 was mainly oxidative in all the samples, being hepatic microsomes more active than renal ones by about one order of magnitude and levels of CHCl 3-derived PL adducts in B6C3F1 mouse liver microsomes higher than in rat samples. At 5 mM CHCl 3, total levels of PL adducts in renal microsomes reached levels almost similar to those found in liver microsomes. However, while B6C3F1 mouse kidney microsomes produced both reactive metabolites, similarly as the hepatic samples, Osborne Mendel rat kidney microsomes bioactivated CHCl 3 only reductiveiy, producing the radical. The relevance of this finding depends on the fact that phosgene is known to be the major cause of CHCl 3 toxicity, based on data with the rat liver and mouse liver and kidney, while nephrotoxicity in rats occurs with minimal production of COCl 2. Chloroform reductive bioactivation may therefore provide a reasonable explanation for the toxicity of chloroform to the rat kidney. The same finding may be of interest in elucidating the metabolic reasons of the chloroform-induced kidney tumors in Osborne Mendel rats.

Identification of functional aryl hydrocarbon receptor and aryl hydrocarbon receptor nuclear translocator in murine splenocytes

The objective of the present studies was to determine whether the aryl hydrocarbon receptor (AhR) and AhR nuclear translocator (ARNT) protein are present and functional in B6C3F1 (C57BL/6 × C3H) mouse splenocytes. Northern analysis of poly (A) RNA isolated from splenocytes revealed transcripts of approximately 6.6 kb which hybridized to the AhR complementary DNA (cDNA) probe. Anti-AhR antibodies identified two major cytosolic forms of the AhR in splenocytes, approximately 95 and 104 kDa, corresponding to the codominately expressed Ahr b alleles in the B6C3F1 mice. Northern analysis utilizing an oligomer probe for ARNT identified three messenger RNA (mRNA) transcripts, approximately 5.6, 2.0, and 1.1 kb, in spleen which was consistent with the banding pattern observed in the B6C3F1 mouse liver. Western blotting confirmed the presence of the approximately 87 kDa ARNT protein in splenocytes. Protein quantitation by slot blot analysis demonstrated approximately 2.0-fold more AhR in liver than in splenocytes. Interestingly, ARNT was approximately 2.4-fold more abundant in splenocytes than in liver. Consistent with these results, comparison by quantitative reverse transcriptase-polymerase chain reaction analysis of AhR and ARNT transcripts in liver and splenocytes demonstrated approximately 2.3-fold more AhR transcripts in liver than in splenocytes and approximately 3.2-fold more ARNT transcripts in splenocytes than in liver. In addition, comparisons between AhR and ARNT transcripts isolated from the liver and splenocytes indicated a greater number of ARNT transcripts as compared with AhR in both preparations. TCDD treatment of splenocytes induced binding of the AhR nuclear complex to the dioxin-responsive enhancer (DRE) as detected by the electrophoretic mobility shift assay. These findings confirm that the AhR and ARNT are present in mouse splenocytes and are capable of binding to the DRE.

Cell Proliferation Rates in Common Cancer Target Tissues of B6C3F1 Mice and F344 Rats: Effects of Age, Gender, and Choice of Marker

Increasing emphasis is being placed on mode of action for chemical carcinogens as an important consideration for risk assessment. Many rodent carcinogens appear to act through nongenotoxic mechanisms, such as induced cell proliferation. Information on cell proliferation rates based on species, age, gender, tissue, and choice of marker will provide a foundation for incorporating such measurements into rodent toxicity studies. Cell proliferation was evaluated in liver, kidney, skin, and forestomach of control male and female B6C3F1 mice and F344 rats at 7, 10, 13, and 20 weeks of age. Proliferating cell nuclear antigen (PCNA), an endogenous cell proliferation marker, and bromodeoxyuridine (BrdU) administered by ip injection 2 hr before euthanization were compared as markers of cell proliferation. Only in liver were BrdU and PCNA labeling indices (LIs; S phase only) statistically similar. As expected, the PCNA proliferating index (PI; G1+ S + G2+ M phases) was consistently greater than the S phase LI in all tissues examined. Age-related differences in LI were evident in liver and kidney, whereas LIs in the forestomach and skin were not age-dependent. In all tissues examined, gender- and species-related differences in cell proliferation were detected. Although BrdU and PCNA LIs were often statistically different, they both provided a useful indication of cell proliferation rates in the tissues examined. These results provide potentially useful information for designing rodent toxicity studies and biological models of carcinogenesis.

Carcinogenic Activity of Dichloroacetic Acid and Trichloroacetic Acid in the Liver of Female B6C3F1 Mice

The concentration–response relationships for the hepatocarcinogenic activity of dichloroacetic acid22Abbreviations used: DCA, dichloroacetic acid; GST-π, glutathioneS-transferase-π; TCA, trichloroacetic acid.(DCA) and trichloroacetic acid (TCA), two contaminants of finished drinking water, were determined in female B6C3F1 mice. Dichloroacetic acid or trichloroacetic acid at 2.0, 6.67, or 20.0 mmol/liter was administered to the mice in the drinking water starting at 7 to 8 weeks of age and until sacrifice after 360 or 576 days of exposure. The relationships of the yield of foci of altered hepatocytes, hepatocellular adenomas, and hepatocellular carcinomas to the concentration of DCA and TCA in the water were best described by second-order and linear regressions, respectively. The liver-to-body weight ratio increased linearly for both DCA and TCA, as did the vacuolization of the liver induced by DCA. The foci of altered hepatocytes and tumors in the animals treated with DCA were predominantly eosinophilic and contained glutathioneS-transferase-π (GST-π, over 80% of the lesions), while the tumors induced by TCA were predominantly basophilic and lacked GST-π, including all 11 hepatocellular carcinomas. Therefore, the carcinogenic activity of DCA and TCA appeared to differ both with respect to their dose–response relationship and to the characteristics of precancerous lesions and tumors.

Haloacetate-induced oxidative damage to DNA in the liver of male B6C3F1 mice

Brominated and chlorinated haloacetates (HAs) are by-products of drinking water disinfection. Dichloroacetate (DCA) and trichloroacetate (TCA) are hepatocarcinogenic in rodents, but the brominated analogs have received little study. Prior work has indicated that acute doses of the brominated derivatives are more potent inducers of oxidative stress and increase the 8-hydroxydeoxyguanosine (8-OH-dG) content of the nuclear DNA in the liver. Since, DCA and TCA are also known as weak peroxisome proliferators, the present study was intended to determine whether this activity might be exacerbated by peroxisomal proliferation. Classical responses to peroxisome proliferators, cyanide-insensitive acyl-CoA oxidase activity and increased 12-hydroxylation of lauric acid, were elevated in a dose-related manner in mice maintained on TCA and clofibric acid (positive control), but not with DCA, dibromoacetate (DBA) or bromochloroacetate (BCA). Administration of the HAs in drinking water to male B6C3F1 mice for periods from 3 to 10 weeks resulted in dose-related increases in 8-OH-dG in nuclear DNA of the liver with DBA and BCA, but not with TCA or DCA. These findings indicate that oxidative damage induced by the haloacetates is, at least in part, independent of peroxisome proliferation. In addition, these data suggest that oxidative damage to DNA may play a more important role in the chronic toxicology of brominated compared to the chlorinated haloacetates.

Oxidative DNA Damage and Cell Proliferation in the Livers of B6C3F1 Mice Exposed to Pentachlorophenol in Their Diet

Pentachlorophenol (PCP), which has been used as a wood preservative, was reported to be a liver carcinogen in mice. To investigate the initial effects of PCP administration under the same conditions of exposure as in the carcinogenic study, we examined oxidative stress and cell proliferation, along with other hepatotoxicological parameters, in the livers of B6C3F1 mice fed PCP in their diet at doses of 0.03, 0.06, and 0.12% for up to 4 weeks. We observed significant increases of 8-OHdG levels in hepatic nuclear DNA at doses of 0.03% and above at 2 and 4 weeks. Likewise, dose-dependent increases in the labeling index of cells were detected by counting those that had incorporated 5-bromo-2′-deoxyuridine throughout the experimental period. Also, we found significant elevations of the liver weights, concurrent with increases in hepatic DNA content in the treated mice, which again were dose-related. Serum aspartic transferase activity at doses of 0.06% and above were significantly increased despite these changes being slight. Also, histopathological examination provided no evidence of necrotic changes, but severe hepatocyte swelling in the treated mouse livers. These data indicate that PCP might be able to induce cell proliferation in the mouse liver, as well as induce oxidative DNA damage, suggesting both changes may play an important role in hepatocarcinogenesis.

Isomer-Specific Acute Toxicity and Cell Proliferation in Livers of B6C3F1 Mice Exposed to Dichlorobenzene

The acute hepatotoxicity of isomers of dichlorobenzene (o-,m-, andp-DCB) was compared in livers of male B6C3F1 mice at different time points after a single intragastric administration. The highest doses ofo-,m-, andp-DCB administered, 300, 300, and 1800 mg/kg, respectively, are below the lethal range. Acute hepatic injury was assessed by serum alanine aminotransferase (ALT) activity and hepatic histology. Hepatocyte replication was estimated by means of immunohistochemical demonstration of BrdU-labeled cells. Botho-DCB andm-DCB at a dose of 300 mg/kg produced significant elevations of liver weight and ALT activity as well as extensive liver cell necrosis. In contrast,p-DCB at a highest dose of 1800 mg/kg induced slight hepatocyte injury. Dose–response studies indicated that the rank order for acute hepatotoxicity of the isomers wasm-DCB >o-DCB much greater thanp-DCB. However,p-DCB induced hepatocyte cell proliferation in spite of the lack of manifest hepatotoxicity. In contrast, increases of cell proliferation due too- orm-DCB exposure occurred only after dosages that caused hepatic injury. These data suggest the hepatocyte proliferation induced byo- orm-DCB is compensatory regeneration while that induced byp-DCB is a response to mitogenic stimulation.

Promotion by dichloroacetic acid and trichloroacetic acid of N-methyl-N-nitrosourea-initiated cancer in the liver of female B6C3F1 mice.

Hepatic tumor promoting activity was determined for dichloroacetic acid (DCA) and trichloroacetic acid (TCA) in female B6C3F1 mice initiated on day 15 of age with 25m/kg N-methyl-N-nitrosourea (MNU). The mice were administered the chloroacetic acids in drinking water starting at 7 weeks of age and continuing until sacrificed 31 or 52 weeks later. Both chloroacetic acids promoted MNU-initiated foci and tumors, however their concentration-response relationships differed being exponential and linear for DCA or TCA, respectively. Lesions promoted by DCA but not by TCA, regressed upon termination of exposure at 31 weeks. Foci and tumors promoted by DCA were eosinophilic and contained glutathione S-transferase-pi(GST-pi), while TCA promoted basophilic tumors lacking GST-pi. Hence, tumor promotion by DCA and TCA appeared to differ both with respect to their concentration-response relationships and to the characteristics of precancerous lesions and tumors.

Oxidative DNA Damage and Cell Proliferation in the Livers of B6C3F1 Mice Exposed to Pentachlorophenol in Their Diet

Pentachlorophenol (PCP), which has been used as a wood preservative, was reported to be a liver carcinogen in mice. To investigate the initial effects of PCP administration under the same conditions of exposure as in the carcinogenic study, we examined oxidative stress and cell proliferation, along with other hepatotoxicological parameters, in the livers of B6C3F1 mice fed PCP in their diet at doses of 0.03, 0.06, and 0.12% for up to 4 weeks. We observed significant increases of 8-OHdG levels in hepatic nuclear DNA at doses of 0.03% and above at 2 and 4 weeks. Likewise, dose-dependent increases in the labeling index of cells were detected by counting those that had incorporated 5-bromo-2'-deoxyuridine throughout the experimental period. Also, we found significant elevations of the liver weights, concurrent with increases in hepatic DNA content in the treated mice, which again were dose-related. Serum aspartic transferase activity at doses of 0.06% and above were significantly increased despite these changes being slight. Also, histopathological examination provided no evidence of necrotic changes, but severe hepatocyte swelling in the treated mouse livers. These data indicate that PCP might be able to induce cell proliferation in the mouse liver, as well as induce oxidative DNA damage, suggesting both changes may play an important role in hepatocarcinogenesis.

Subcellular Localization of TCDD Differs between the Liver, Lungs, and Kidneys after Acute and Subchronic Exposure: Species/Dose Comparisons and Possible Mechanism

Subcellular localization of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related compounds has been examined only in the liver. The objective of this study was (1) to examine and compare the subcellular distribution of TCDD within hepatic and nonhepatic (lungs/kidneys) tissues of female Sprague-Dawley rats acutely exposed to TCDD, (2) to analyze species comparisons in the subcellular localization of TCDD in multiple tissues, (3) to investigate the effect of dose on subcellular distribution of TCDD, (4) to analyze the effect of subchronic exposure on the subcellular distribution of TCDD, and (5) to examine one possible mechanism for subcellular localization of TCDD. Female Sprague-Dawley rats and B6C3F1 mice received a single oral dose of 0.1, 1.0, or 10 μg [3H]TCDD/kg body weight and subcellular fractions of the liver, lungs, and kidneys were prepared by differential centrifugation 3 days after exposure. Analysis of the rat subcellular fractions revealed that TCDD was equally distributed between the hepatic P9 (mitochondrial, lysosomal, and nuclear) and S9 (cytosol and microsomal) fractions at all doses tested. In contrast, TCDD was concentrated in the P9 of rat nonhepatic tissues at all doses studied. Differential centrifugation of the hepatic S9 showed that TCDD was localized within the hepatic P100 (microsomal) fraction at all doses tested. In contrast, TCDD localized in pulmonary and renal S100 (cytosolic) fractions at all doses. The subcellular distribution of TCDD in the liver and lungs of acutely exposed B6C3F1 mice was similar to that observed in the rats. Although TCDD was concentrated within the renal P9, the remainder of TCDD in the S9 was evenly distributed between the S100 and the P100 fractions of acutely exposed B6C3F1 mice. Subchronic exposure of B6C3F1 mice to 1.5 or 150 μg [3H]TCDD/kg/day revealed that increasing dose resulted in equal distribution of TCDD between the hepatic S9 and P9 versus concentration in the renal P9. In addition, a dose-dependent increase in accumulation of TCDD in the hepatic P100 was accompanied by a dose-dependent increase in TCDD localization in the renal S100 of mice subchronically exposed to TCDD. TCDD exposure in rats resulted in a dose-dependent increase in the induction of CYP1A1 protein and associated enzyme activity in hepatic, pulmonary, and renal microsomes. TCDD-induced CYP1A2 protein levels and associated enzymatic activity were only present in hepatic microsomes. This is the first report to suggest that subcellular distribution of TCDD differs between hepatic and nonhepatic tissues and demonstrate that the liver-specific microsomal localization of TCDD in female Sprague-Dawley rats also occurs in the liver of female B6C3F1 mice acutely or subchronically exposed to TCDD. In addition, these data are consistent with the hypothesis that the hepatic sequestration of TCDD is due to an interaction with CYP1A2. Furthermore, the lack of pulmonary/renal sequestration coupled with the lack of localization of TCDD in pulmonary/renal microsomes also supports the role of CYP1A2 as a hepatic microsomal binding protein involved in TCDD sequestration.

Cell Proliferation Rates in Common Cancer Target Tissues of B6C3F1 Mice and F344 Rats: Effects of Age, Gender, and Choice of Marker

Increasing emphasis is being placed on mode of action for chemical carcinogens as an important consideration for risk assessment. Many rodent carcinogens appear to act through nongenotoxic mechanisms, such as induced cell proliferation. Information on cell proliferation rates based on species, age, gender, tissue, and choice of marker will provide a foundation for incorporating such measurements into rodent toxicity studies. Cell proliferation was evaluated in liver, kidney, skin, and forestomach of control male and female B6C3F1 mice and F344 rats at 7, 10, 13, and 20 weeks of age. Proliferating cell nuclear antigen (PCNA), an endogenous cell proliferation marker, and bromodeoxyuridine (BrdU) administered by ip injection 2 hr before euthanization were compared as markers of cell proliferation. Only in liver were BrdU and PCNA labeling indices (LIs; S phase only) statistically similar. As expected, the PCNA proliferating index (PI; G1 + S + G2 + M phases) was consistently greater than the S phase LI in all tissues examined. Age-related differences in LI were evident in liver and kidney, whereas LIs in the forestomach and skin were not agedependent. In all tissues examined, gender-and species-related differences in cell proliferation were detected. Although BrdU and PCNA LIs were often statistically different, they both provided a useful indication of cell proliferation rates in the tissues examined. These results provide potentially useful information for designing rodent toxicity studies and biological models of carcinogenesis.

Carcinogenic Activity of Dichloroacetic Acid and Trichloroacetic Acid in the Liver of Female B6C3F1 Mice

Carcinogenic Activity of Dichloroacetic Acid and Trichloroacetic Acid in the Liver of Female B6C3F1 Mice