Search

Tsc-22 is a novel tumor suppressor gene that represents a new class of transcription factors that has transcriptional repressor activity. We found Tsc-22 downregulation in livers from B6C3F1 mice following treatment for 2 weeks with carcinogenic doses of the antianxiety drug oxazepam (2500 ppm) or the peroxisome proliferator Wyeth-14,643 (500 ppm) but not with two other carcinogens such as o-nitrotoluene or methyleugenol or three noncarcinogens including p-nitrotoluene, eugenol, or acetaminophen. The expression of Tsc-22 was also repressed in B6C3F1 mouse liver tumors that were induced by several chemicals from 2-year carcinogenicity studies as well as in spontaneous liver tumors. To identify potential Tsc-22 target genes in mouse liver, we transfected small interference RNA (SiRNA) designed to inhibit Tsc-22 into murine liver BNL-CL.2 cells. We selected two potential transcriptional targets of Tsc-22, growth arrest and DNA damage-inducible gene 45 beta (Gadd45b) and leucine zipper, putative tumor suppressor 2 (Lzts2) to test based on our previous complementary DNA microarray studies, showing that expression of these cancer-associated genes was increased when Tsc-22 was repressed. SiRNA treatment of BNL-CL.2 cells with Tsc-22 oligonucleotides but not nonspecific oligonucleotides decreased RNA and protein expression of Tsc-22 by 80-90%, while expression of Gadd45b gene, but not Lzts2, was increased over time after an initial decrease. Treatment of these cells with oxazepam for 48 h also resulted in decreased Tsc-22 and increased Gadd45b expression. These data provide evidence that Tsc-22 is a suppressor of Gadd45b expression, which may contribute to an early antiapoptotic response.

The present study characterized the immunohistochemical localization of beta-catenin protein in hepatocellular neoplasms and hepatoblastomas in B6C3F(1) mice exposed to diethanolamine (DEA) for 2 years and evaluated genetic alterations in the Catnb and H-ras genes which are known to play important roles in the pathogenesis of liver malignancies. Genomic DNA was isolated from paraffin sections of each liver tumor. Catnb exon 2 (corresponds to exon 3 in human) genetic alterations were identified in 18/18 (100%) hepatoblastomas from DEA exposed mice. Deletion mutations (15/18, 83%) were identified more frequently than point mutations (6/18, 33%) in hepatoblastomas. Eleven of 34 (32%) hepatocellular adenomas and carcinomas from DEA treated mice had mutations in exon 2 of the beta-catenin gene, while only 1 of 10 spontaneous neoplasms had a deletion mutation of codon 5-6. Common to all liver neoplasms (hepatocellular adenomas, carcinomas and hepatoblastomas) was membrane staining for the beta-catenin protein, while cytoplasmic and nuclear staining was observed only in hepatoblastomas. The lack of H-ras mutations in hepatocellular neoplasms and hepatoblastomas suggests that the ras signal transduction pathway is not involved in the development of liver tumors following DEA exposure which is different from that of spontaneous liver tumors that often contain H-ras mutations.

In this study we used liver neoplasms induced by several chemical carcinogens to investigate potential nuclear targets associated with beta-catenin/Wnt signaling and potential membrane-associated beta-catenin binding partners. Strong expression of cyclin D1, in a pattern similar to that observed previously for beta-catenin, was observed by Western analysis for all five hepatoblastomas examined regardless of treatment. Increased expression of cyclin D1 was also detected in 12 of 35 (34%) hepatocellular neoplasms. Ten of 15 tumors (67%) that had mutations in the Catnb gene had upregulation of cyclin D1, while only 2 of 20 tumors (10%) without Catnb mutations had increased cyclin D1 expression. Immunohistochemical analysis confirmed strong expression of cyclin D1 in most nuclei of hepatoblastomas and scattered nuclear staining in hepatocellular tumors that had Catnb mutations. Increased c-Jun expression was observed in 19 of 30 (63%) hepatocellular tumors and all hepatoblastomas, although upregulation was not completely correlated with Catnb mutation. C-Myc expression was not increased in the tumors. Reduced expression of E-cadherin, which interacts with beta-catenin at the membrane, was observed in some tumors, but this did not correlate with Catnb mutation. Expression of the epidermal growth factor receptor, which may have a role in beta-catenin tyrosine phosphorylation, was lower in some tumors than in normal tissue depending on chemical treatment. The results provide evidence that increased expression of cyclin D1 and c-Jun may provide an advantage during tumor progression and in the transition from hepatocellular neoplasms to hepatoblastomas. Moreover, it is likely increased cyclin D1 expression results at least in part from Catnb mutation, beta-catenin accumulation, and increased Wnt signaling.

We hypothesized that the mouse liver tumor response to non-genotoxic carcinogens would involve some common early gene and protein expression changes that could ultimately be used to predict chemical hepatocarcinogenesis. In order to identify a panel of genes to test, we analyzed global differences in gene and protein expression in livers from B6C3F1 mice following dietary treatment with two rodent carcinogens, the benzodiazepine anti-anxiety drug oxazepam (2500 p.p.m.) and the hypolipidemic agent Wyeth (Wy)-14,643 (500 p.p.m.) compared with livers from untreated mice. Male mice were exposed for 2 weeks and 1, 3 or 6 months to oxazepam or Wy-14,643 in an age-matched study design. By histopathological evaluation, no liver preneoplastic foci or tumors were detected at 6 months in treated or control groups. By cDNA microarray analysis [NIEHS Mouse Chip (8700 genes); n = 3 individual livers/group, four hybridizations/sample], expression of 36 genes or 220 genes were changed relative to control livers following 6 months of oxazepam or Wy-14,643 treatment, respectively. To obtain a more comprehensive picture of gene/protein expression changes, we also conducted a proteomics study by 2D-gel electrophoresis followed by matrix assisted laser desorption/ionization-mass spectrometry on cytoplasmic, nuclear, and microsomal subcellular fractions of the same liver samples utilized for the cDNA microarray analysis. Real-time PCR, western blot analysis and immunohistochemistry were utilized for validation and to expand the results to other time points. Cyp2b20, growth arrest- and damage-inducible gene beta (Gadd45beta), tumor necrosis factor alpha-induced protein 2 and insulin-like growth factor binding protein 1 (Igfbp5) genes and proteins were upregulated by oxazepam, and Cyp2b20, Cyclin D1, proliferating cell nuclear antigen, Igfbp5, Gadd45beta and cell death-inducing DNA fragmentation factor alpha subunit-like effector A exhibited higher expression after Wy-14,643 treatment. Most of these genes/proteins were also deregulated at 2 weeks. There appeared to be more distinct than common changes in the expression of carcinogenesis-related genes/proteins between the two compounds, suggesting that the major carcinogenic pathways are different for these compounds and may be distinct for different chemical classes.

Tetrafluoroethylene (TFE) was evaluated for carcinogenicity in inhalation studies because of its high use in the production of Teflon. There was clear evidence of hepatocarcinogenic activity in B6C3F1 mice after 2 yr of TFE exposure. The present study was designed to characterize the mutation profiles of H- and K-ras oncogenes in liver neoplasms in mice after exposure to 0, 312, 625, or 1,250 ppm TFE. ras mutations were identified by restriction fragment length polymorphism, single-stranded conformation polymorphism analysis, and direct sequencing of polymerase chain reaction amplified-DNA isolated from frozen or paraffin-embedded liver neoplasms. A low frequency (15%, 9/59) of H-ras codon 61 mutations was detected in hepatocellular neoplasms when compared with the higher frequency (59% of this study and 56% of historical data) in spontaneously occurring liver neoplasms. There was no difference in the mutation frequency or spectrum among exposure groups or between benign and malignant hepatocellular neoplasms. K-ras mutations at codons 12, 13, and 61 and H-ras mutations at codon 117 were not detected in hepatocellular neoplasms. These data suggest that TFE-induced hepatocellular neoplasms are developed by pathways that are mostly independent of ras mutations. The ras mutation frequency and spectrum were similar to those of the structurally related chemical tetrachloroethylene.

Logistic regression analysis of age-specific prevalences for neoplastic and non-neoplastic liver lesions was used to examine treatment responses for B6C3F1 and B6D2F1 male mice continuously exposed to chlordane (55 p.p.m.) and to determine whether neoplasms were dependent on continuous exposure in the B6C3F1 mice. In order to determine if ras oncogene activation plays a role in the carcinogenicity of chlordane and whether the activation is dependent on genetic background, liver tumors from chlordane-treated B6C3F1 and B6D2F1 mice were analyzed for the presence of activating mutations in the ras oncogene. The overall liver tumor prevalence at terminal killing was nearly 100% for both strains; however, the age-specific prevalence increased more rapidly in B6C3F1 mice than in B6D2F1 mice. Tumor-bearing B6C3F1 mice had an average of two or more tumors per liver than B6D2F1 mice at their respective terminal killings (5.4 versus 3.3). When chlordane exposure was discontinued for a group of B6C3F1 mice ('stop' group) at 491 days of age, overall tumor multiplicity significantly decreased by 30% from an average of 4.4 per tumor-bearing-animal at 525 days to 3.1 at terminal killing (568 days). Over the same time period the prevalence of hepatocellular carcinomas significantly decreased from 80 to 54% and adenomas from 100 to 93% by terminal killing in B6C3F1 'stop-group' mice. Chlordane induced diffuse hepatocellular centrilobular hypertrophy, frequent multinucleate hepatocytes, toxic change and hepatoproliferative lesions composed predominantly of acidophilic hepatocytes in nearly 100% of both the B6C3F1 and B6D2F1 mice. The development of histological evidence of toxicity closely paralleled the temporal development of hepatocellular neoplasia and decreased in severity when the tumor burden was maximal. No H- or K-ras mutations were detected in the chlordane-induced hepatocellular tumors in B6C3F1 mice (15 adenomas and 15 carcinomas) or B6D2F1 mice (10 adenomas and 10 carcinomas). In conclusion, chlordane induced liver tumors in both B6C3F1 and B6D2F1 male mice by mechanisms independent of ras oncogene activation and 30% of both benign and malignant liver tumors in the B6C3F1 mice regressed after exposure was discontinued.

An inhalation study utilizing over 1400 female B6C3F1 mice was undertaken to study mechanistic factors associated with liver and lung tumor induction following exposure to 2000 ppm of methylene chloride. Mice were exposed to methylene chloride (treated) or chamber air (controls) 6 h per day, for varying durations up to 104 weeks. Several interim sacrifices and 'stop exposures' were included. Exposure to 2000 ppm methylene chloride caused an increase in liver and lung neoplasia in the absence of overt cytotoxicity. Measurement of replicative DNA synthesis done after 13, 26, 52 and 78 weeks of exposure showed a significant decrease in the hepatocyte labeling index at 13 weeks. Replicative DNA synthesis in pulmonary airways after 1, 2, 3, 4, 13 and 26 weeks of exposure to methylene chloride was significantly lower than in air-exposed controls. Likewise, the increase in tumor induction in treated mice was not associated with increased replicative DNA synthesis in liver foci or in alveolar parenchyma. The frequency and pattern of H-ras gene activation were similar in control and methylene chloride-induced liver neoplasms. Similarly, the frequency and pattern of K-ras activation in lung neoplasms were not altered by exposure to methylene chloride. Early exposure to methylene chloride for only 26 weeks was sufficient to cause an increase in lung tumors by 2 years, suggesting that methylene chloride may cause early and persistent loss of growth control in lung cells. This implies that risk management strategies should be aimed at minimizing or eliminating exposure to methylene chloride. Liver neoplasms continued to increase in incidence and multiplicity as exposure continued, suggesting that methylene chloride-induced hepatocarcinogenesis is facilitated by continuing exposure to methylene chloride. Since methylene chloride is a more potent inducer of lung than liver neoplasia, it is recommended that health risk assessment be based on the lung data. While no novel molecular lesions have been found to explain the induction of lung and liver neoplasia in mice, ongoing studies may identify other molecular changes that are important in the genesis of these neoplasms. Hence, it may be necessary to revise risk assessment and management strategies in light of future research findings.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a potent environmental toxin which has been found to be non-genotoxic in short term in vitro tests but strongly carcinogenic in two stage models of hepatocellular carcinogenesis in female rats. Many recent studies have shown that after treatment of mice with various genotoxic or non-genotoxic compounds, the H-ras oncogene mutational patterns exhibited by hepatocellular tumors appear to vary specifically with the chemical. To gain insight into the mechanism of TCDD-associated carcinogenesis, susceptible B6C3F1 mice and resistant C57BL/6 mice were treated with a single dose of vinyl carbamate (VC) or vehicle, and TCDD was administered once every 2 weeks for 1 year to half of the animals in each group. Liver tumor prevalence was assessed and found to be highest in the VC + TCDD treatment groups, reaching nearly 100% at 600 days in both sexes and both strains of mice. DNA was isolated from 20 or more frozen liver tumors (if available) from each exposure group and analyzed for H-ras mutations in codon 61 by sequencing after PCR amplification of exon 2. Fifty-one percent of tumors analyzed from B6C3F1 mice treated with TCDD alone had H-ras codon 61 mutations with a pattern similar to that detected in spontaneous tumors. Seventy-eight percent of tumors from B6C3F1 mice treated with both VC and TCDD had codon 61 mutations, and most mutations were A-->T transversions in the second base as observed similarly with VC alone. In the C57BL/6 strain comparable results were found in the respective exposure groups. These data suggest that TCDD is acting as a promoter of lesions previously initiated either spontaneously or by VC. Moreover, the intrinsic resistance of both male and female C57BL/6 mice to liver tumor formation seemed to disappear after treatment with TCDD.

Of the chlorinated hydrocarbons discussed above, all six are associated with induction of hepatocellular neoplasia in mice. None of the six is considered to be potent mutagen and most are without any significant genotoxic activity as assessed by conventional in vitro testing schemes. Although some of the agents have biological effects in common (see Figure 4), there is no single biological response (mode of action) that they all share to provide a mechanistic basis for the observed murine hepatocarcinogenicity. Based upon the information currently available for each of the chlorinated hydrocarbons discussed above, it is probable that some modes of action may be more contributory to the rodent carcinogenic response than others; however, no mode of action, pathway, or mechanism should be considered to be mutually exclusive. The murine hepatocarcinogenic effect of TriCE is most probably contingent upon its species-specific metabolism to trichloroacetic acid and DCA. There is fairly consistent evidence that cytotoxicity and reparative hyperplasia are associated with doses of TriCE that cause induction of liver neoplasms. The possibility that peroxisome proliferation is playing a role in the induction of mouse hepatocellular neoplasia remains a tempting explanation, since higher intracellular steady states of H2O2 production would be consistent with observed enhanced cellular proliferation as well as the possibility of in vivo DNA damage. The mouse hepatocarcinogenicity associated with TetCE most probably is associated with species-specific metabolic production of trichloroacetic acid. As with TriCE, cytotoxicity and reparative hyperplasia may represent a potential mode of action for the observed hepatocarcinogenicity. Once again, the potential for enhanced peroxisome proliferation is consistent with enhanced cell proliferation and oxygen radical damage would help explain the random point mutations in ras proto-oncogenes documented in DNA from TetCE-induced mouse liver tumors. DCA-induced mouse hepatocellular neoplasia is probably influenced by cytotoxicity and reparative hyperplasia, but there is also recent evidence that DCA may directly damage DNA, implying an in vivo genotoxic mechanism may be operational. Likewise, altered expression of several genes suggests that subversion of signal transduction may play a role in the induction or progression of liver tumor development. As with TetCE and TriCE, a role for peroxisome proliferation is still a consideration, although the liver tumor response is obvious at doses too low to cause peroxisome proliferation.(ABSTRACT TRUNCATED AT 400 WORDS)

Oxazepam has been the subject of recent toxicological and carcinogenesis studies because it is a commonly prescribed tranquilizer and has been shown to cause tumors in rodents. In this study, male and female B6C3F1 mice received 0, 125, 2500 or 5000 p.p.m. oxazepam in the diet for up to 2 years. Hepatocellular adenomas and carcinomas, as well as hepatoblastomas, which developed in these mice, were examined for the presence of activated ras proto-oncogenes. DNA was isolated from 20 or more tumors from each exposure group and analyzed by oligonucleotide hybridization, single-stranded conformation polymorphism analysis and direct sequencing of PCR-amplified H-ras gene fragments for codon 61 mutations. Thirteen of 37 (35%) hepatocellular adenomas and carcinomas from the 125 p.p.m. exposure group had mutations in codon 61, while mutations were detected in only 2 of 25 or 8% of the liver tumors from the 2500 p.p.m. exposure group and none of the 22 tumors from the 5000 p.p.m. group. This compares to 63% of 126 historical control liver tumors and 55% of 20 liver tumors from unexposed B6C3F1 mice in this study. In addition, 12 hepatoblastomas from the two high dose groups were examined for H-ras mutations at codon 61, but none were detected. No tumor DNAs from any of the exposure groups tested had mutations in codons 12, 13 or 117 of the H-ras gene or codons 12 or 13 of the K-ras gene, the other known hotspots for ras activation in mouse liver tumors. These results, together with those from the National Toxicology Program study showing no evidence of cytotoxicity or genotoxicity by oxazepam, suggest that oxazepam preferentially promotes cells that have activating lesions other than ras.

Liver tumors from B6C3F1 mice induced by the potent peroxisome proliferator ciprofibrate, a hypolipidemic drug, were evaluated for the presence of transforming genes by the nude mouse tumorigenicity assay. As reported earlier, the tumors were not activated by a point mutation in codon 61 of H-ras. Two of the eight tumors examined contained a mutation in codon 13 or an H-ras gene mutated in codon 117. Screening of another 23 ciprofibrate-induced liver tumors by oligonucleotide hybridization analysis and direct DNA sequencing resulted in the identification of three tumor DNA samples with point mutations in codon 117 of the H-ras gene. In addition, another tumor sample contained a K-ras gene with a mutation in codon 61. Mutations in these codons have been seen only rarely in chemically induced liver tumors from this mouse strain. Of 15 spontaneous B6C3F1 liver tumors screened in the same manner, one exhibited a K-ras gene activated by a mutation in codon 13 and a second contained an H-ras gene activated by a mutation in codon 117. These ras gene mutations have not been reported previously from spontaneous liver tumors. The frequency and spectrum of ras oncogene mutations characterized in ciprofibrate-induced liver tumors differ significantly from the frequency and pattern identified in spontaneously occurring liver tumors. The results of this study with a limited number of samples suggest that ras protooncogene activation or activation of other protooncogenes that can be detected by the nude mouse tumorigenicity assay are not frequent events in the mechanism of carcinogenicity of the peroxisome proliferator ciprofibrate. However, the lower frequency and distinct pattern of H-ras mutations observed in these tumors disprove the assumption of promotion of spontaneous hepatocarcinogenesis by ciprofibrate.

Activation of the ras family of oncogenes occurs frequently in liver tumors of the B6C3F1 mouse, a strain which is highly sensitive to hepatocarcinogenesis. Many other mouse strains are much more resistant to hepatocarcinogenesis; the aim of this study was to determine the frequency and pattern of oncogene activation in spontaneous and chemically induced liver tumors of three such strains, the C57BL/6J, the C57BL/6 x DBA/2 F1 hybrid (B6D2F1) and the C57BL/6 x Balb/c F1 hybrid (B6BCF1). The C57BL/6, DBA/2 and Balb/c strains are all relatively resistant to spontaneous hepatocarcinogenesis (1.5-3.6% of animals develop liver tumors in 2 years); with regard to chemically induced hepatocarcinogenesis the Balb/c is highly resistant, the C57BL/6 has low susceptibility and the DBA/2 has low to moderate susceptibility. The nude mouse tumorigenicity assay was used to search for activated oncogenes in 15 C57BL/6J liver tumors induced by a single neonatal dose of vinyl carbamate (VC, 0.15 mumol/g body weight). Three tumors contained H-ras genes activated by point mutations at codon 61 and one contained a non-ras oncogene. The polymerase chain reaction and allele-specific oligonucleotide hybridization were used to study H-ras mutations in spontaneous and VC-induced tumors from all three strains of mice. The frequency of H-ras codon 61 mutations in tumors induced by 0.15 mumol/g body weight VC in the C57BL/6J mouse (5/37) was similar to that in spontaneous tumors (2/9); surprisingly, tumors induced by a lower dose of VC (0.03 mumol/g body weight) had a higher frequency of H-ras mutations (12/28). The frequencies of H-ras activation detected in VC (0.03 mumol/g body weight)-induced tumors from the two F1 hybrids studied differed markedly. Only one VC-induced B6BCF1 tumor contained a mutated H-ras gene (1/10), whereas the majority of B6D2F1 tumors contained such mutations (23/33). Several spontaneous B6D2F1 liver tumors contained H-ras codon 61 mutations (6/15). Thus, H-ras activation frequency does not determine susceptibility to hepatocarcinogenesis in inbred mice and their F1 hybrids, since a relatively high frequency of H-ras mutations was observed in two resistant strains and a low frequency was found in the other strain.