Search PubMed⌕ Search

Biomedical subjects

D Warshawsky

Publications and source records attributed to D Warshawsky.

At least 37 records · Page 2Linked to original sources

In vivo footprints are found in the Xenopus 63 kDa keratin gene promoter prior to the appearance of mRNA.

Previous work on the promoter region of the 63 kDa keratin gene demonstrated that in vivo footprints did not change during the transition from low-level to high-level transcription. Reverse transcription polymerase chain reaction and in vivo footprinting were used to determine if these DNA-protein interactions are present before transcription begins. The results presented indicate that during development, DNA-protein interactions are present in the promoter region of the 63 kDa keratin gene at stage 44, four days prior to the initial appearance of 63 kDa keratin mRNA, at stage 48. Thus, the occupancy of these sites at stage 44 is not sufficient for transcription, but may have a role in 'poising' the keratin promoter for the initiation of epidermal-specific transcription. The results suggest that the developmental history of a gene may be important in regulating its temporal and spatial expression.

Animals↗

Chronic, topical administration of 4-aminobiphenyl induces tissue-specific DNA adducts in mice.

While current human exposure to 4-aminobiphenyl (4-ABP) is mainly through inhalation, historically, occupational exposure occurred most often through the skin. 4-ABP targets the urinary bladder in humans, dogs, and rats and the liver and urinary bladder in mice. This study examines the time course of DNA adduct levels in mouse target tissues, liver and urinary bladder, and nontarget tissues, lung and skin, after repeated dermal exposure to subcarcinogenic doses of 4-ABP. It was found that, in female mice dermally treated with 50 nmol of 4-ABP twice weekly for 21 weeks, DNA adduct levels measured by 32P-postlabeling increased over time in target and nontarget tissues, but the greatest rate of accumulation occurred in urinary bladder. At 21 weeks liver, urinary bladder, and skin reached their highest median adduct levels of 55, 82, and 58, respectively. Median adduct levels in lung reached a maximum of 3.2 at 3 weeks of exposure. An adduct which had similar chromatographic properties to a standard previously identified as N-(deoxyguanosin-8-yl)-4-aminobiphenyl was the primary adduct detected in all tissues. There were significant correlations in adduct levels between liver and urinary bladder and liver and skin, but not between skin and urinary bladder. These data suggest that urinary bladder adducts are the result of hepatic and not dermal activation. However, adducts were detected at relatively high levels in skin but not in lung, suggesting that skin may have the metabolic capacity to activate 4-ABP when it is applied topically.

Administration, Cutaneous↗

Synthesis, characterization, and mutagenicity of nitrated 7H-dibenzo[c,g]carbazole and its phenolic derivatives.

The nitrated N-heterocyclic aromatic hydrocarbons (NAHs) are found in a variety of environmental sources; many of them have been determined to be mutagenic in short-term assays and/or carcinogenic in animal tests. In this laboratory, we synthesized and characterized nitrated 7H-dibenzo[c,g]carbazole (DBC) and the nitrophenolic metabolites of DBC as potential mutagenic and carcinogenic xenobiotics. The nitro group was formed exclusively at the 5 and/or the symmetric 9 position of DBC, 2-hydroxy-DBC, 3-hydroxy-DBC, and 4-hydroxy-DBC. Ames plate incorporation mutagenicity assays were conducted using Salmonella typhimurium strains TA98 and TA100, with or without rat liver homogenates (S9). Mutagenicities of the nitrated DBCs were higher than the parent DBC in strain TA98, 5,9-Dinitro-DBC had stronger mutagenic responses than 5-nitro-DBC in all assays, particularly in strain TA98 with S9. 5,9-Dinitro-DBC had a higher reduction potential relative to 5-nitro-DBC (-1.09 V and -1.37 V, respectively). Hydroxyl derivatives of 5-nitro-DBC at the 2, 3, 4, 10, or 12 position, synthesized through nitration of the corresponding hydroxy-DBC, possessed greater mutagenicity than the parent 5-nitro-DBC, especially in strain TA100 with or without S9. Our data suggest that nitrated DBC undergoes both nitroreduction and ring oxidation as the primary pathways for the metabolic activation leading to mutagenesis. The relative mutagenicities of the nitrohydroxy-DBC isomers are generally consistent with the resonance stabilization of the positive charge at the arylnitrenium ion, formed from the nitro functional group, as the proposed active electrophile responsible for genotoxic effects.

Biotransformation↗

Benzo[a]pyrene coated ferric oxide and aluminum oxide particles: uptake, metabolism and DNA binding in hamster pulmonary alveolar macrophages and tracheal epithelial cells in vitro.

Ferric oxide (Fe2O3) and aluminum oxide (Al2O3) particles are widely encountered in occupational settings. Benzo[a]pyrene (B[a]P), a well-characterized environmental carcinogen, is frequently adsorbed onto particles. It has been shown that B[a]P-coated Fe2O3 particles (B[a]P-Fe2O3) significantly increased lung tumors in the hamster in contrast to B[a]P-coated Al2O3 (B[a]P-Al2O3) or B[a]P alone. In order to determine the genotoxic effects of these particles on the metabolism of B[a]P, pulmonary alveolar macrophages (AM) from male Syrian golden hamsters were incubated with 5 microg (19.8 nmol) B[a]P-coated respirable size (99% < 5 microm) Fe2O3 and Al2O3 particles with loads from 0.5 to 2.0 mg. Intracellular uptake of B[a]P by AM at 24 h was higher with B[a]P-Fe2O3 than that of B[a]P alone (P < 0.05) or B[a]P-Al2O3 (P < 0.05). Total B[a]P metabolism was significantly greater in AM exposed to B[a]P-coated Fe2O3 at 1.0 and 1.5 mg than in the AM exposed to B[a]p-al2O3 (0.5, 1.0 and 1.5 mg) (P < 0.05) or B[a]P alone (P < 0.05). Similar significant differences for Fe2O3 relative to Al2O3 and B[a]P alone were also apparent for total dihydrodiols, quinones and phenolic metabolites. Co-administration of 5 microg alpha-naphthoflavone (alpha-NF, an inhibitor of cytochrome P-4501A1 and P-4501A2) and 10(-3) M cyclohexene oxide (CO, an inhibitor of epoxide hydrolase) significantly reduced B[a]P metabolism in B[a]P-Fe2O3 (P < 0.05) and B[a]P-Al2O3 (P < 0.05) treated groups relative to B[a]P alone. AM were co-cultured with hamster tracheal epithelial cells (HTE) and treated as described above for metabolism studies to assess the DNA binding of B[a]P metabolites in the target cells, using 32P-postlabeling techniques. Two adducts were observed that had chromatographic behavior similar to 7R,8S,9S-trihydroxy-10R-(N2-deoxyguanosyl-3'-phosphate)-7,8,9,10-t etrahydrobenzo[a]pyrene [(+)-anti-BPDE-dG, adduct 1, major adduct representing 70-80% of total adducts] and 7S,8R,9R-trihydroxy-10S-(N2-deoxyguanosyl-3'-phosphate)-7,8,9,10-t etrahydrobenzo[a]pyrene [(-)-anti-BPDE-dG, adduct 2, representing 20-30% of total adducts]. B[a]P-Fe2O3 treatment enhanced the levels of the two B[a]P-DNA adducts in the HTE compared with B[a]P-Al2O3 (P < 0.05) or B[a]P alone. The inhibitors alphaNF and CO significantly reduced total adduct levels in the HTE (P < 0.05) in the B[a]P and B[a]P-Fe2O3 treatments as well as adduct 1 and adduct 2 levels. Our data suggest that the cocarcinogenic effect of B[a]P-Fe2O3 relative to B[a]P-coated Al2O3 can be due to: (i) the enhancement of B[a]P metabolism in AM by Fe2O3 associated with the increased uptake of B[a]P; and (ii) augmentation of DNA adduct formation in epithelial cells.

Aluminum Oxide↗

Chronic, topical exposure to benzo[a]pyrene induces relatively high steady-state levels of DNA adducts in target tissues and alters kinetics of adduct loss.

Carcinogen-DNA adduct measurements may become useful biomarkers of effective dose and/or early effect. However, validation of this biomarker is required at several levels to ensure that human exposure and response are accurately reflected. Important in this regard is an understanding of the relative biomarker levels in target and nontarget organs and the response of the biomarker under the chronic, low-dose conditions to which humans are exposed. We studied the differences between single and chronic topical application of benzo[a]pyrene (BAP) on the accumulation and removal of BAP-DNA adducts in skin, lung, and liver. Animals were treated with BAP at 10, 25, or 50 nMol topically once or twice per week for as long as 15 weeks. Animals were sacrificed either at 24, 48, or 72 hr after the last dose at 1 and 30 treatments, and after 24 hr for all other treatment groups. Adduct levels increased with increasing dose, but the slope of the dose-response was different in each organ. At low doses, accumulation was linear in skin and lung, but at high doses the adduct levels in the lung increased dramatically at the same time when the levels in the skin reached apparent steady state. In the liver adduct, levels were lower than in target tissues and apparent steady-state adduct levels were reached rapidly, the maxima being independent of dose, suggesting that activating metabolism was saturated in this organ. Removal of adducts from skin, the target organ, was more rapid following single treatment than with chronic exposure. This finding is consistent with earlier data, indicating that some areas of the genome are more resistant to repair. Thus, repeated exposure and repair cycles would be more likely to cause an increase in the proportion of carcinogen-DNA adducts in repair-resistant areas of the genome. These findings indicate that single-dose experiments may underestimate the potential for carcinogenicity for compounds that follow this pattern.

Administration, Topical↗

Carcinogenicity, DNA adduct formation and K-ras activation by 7H-dibenzo[c,g]carbazole in strain A/J mouse lung.

N-Heterocyclic polynuclear aromatic hydrocarbons (NHA) are environmental pollutants formed during the combustion of organic materials. 7-H-Dibenzo[c,g]carbazole (DBC) is a potent carcinogen in lung, liver and skin. We undertook these studies to determine whether tissue specificity for DBC lung carcinogenicity in the strain A/J mouse is mirrored by formation of DBC-DNA adducts in lung tissue and whether these adducts are consistent with mutation patterns in the K-ras gene. Strain A/J mice were given a single i.p. injection of DBC at doses of 0, 5, 10, 20 or 40 mg/kg and levels of DNA adducts in the lung were monitored by 32P-postlabeling on days 1, 3, 5, 7, 14 and 21. The remaining animals were sacrificed 8 months after DBC treatment and lung tumor multiplicity and K-ras mutation patterns in the tumors were determined. The lung tumor response to DBC was dose related, with an average of 4.7 +/- 1.2 tumors/mouse at 5 mg/kg and 48.1 +/- 5.5 tumors/mouse at 40 mg/kg. As many as seven DBC-DNA adducts were observed in the lung. DNA binding levels in the lung were highest at 40 mg/kg, with maximum binding at 5-7 days. At lower dose levels the maximum binding to DNA decreased and shifted to earlier time points. The DBC-DNA adduct in the lung with the highest level of binding at all dose levels was DBC-DNA adduct 3. The majority of DBC-induced mutations in the K-ras gene in the lung were A-->T (80%) transversions in the third base of codon 61, a mutation that has not been previously observed in chemically induced lung tumors in strain A/J mice.

Animals↗

Degradation of pyrene, benz[a]anthracene, and benzo[a]pyrene by Mycobacterium sp. strain RJGII-135, isolated from a former coal gasification site.

The degradation of three polycyclic aromatic hydrocarbons (PAH), pyrene (PYR), benz[a]anthracene (BAA), and benzo[a]pyrene (BaP), by Mycobacterium sp. strain RJGII-135 was studied. The bacterium was isolated from an abandoned coal gasification site soil by analog enrichment techniques and found to mineralize [14C]PYR. Further degradation studies with PYR showed three metabolites formed by Mycobacterium sp. strain RJGII-135, including 4,5-phenanthrene-dicarboxylic acid not previously isolated, 4-phenanthrene-carboxylic acid, and 4,5-pyrene-dihydrodiol. At least two dihydrodiols, 5,6-BAA-dihydrodiol and 10,11-BAA-dihydrodiol, were confirmed by high-resolution mass spectral and fluorescence analyses as products of the biodegradation of BAA by Mycobacterium sp. strain RJGII-135. Additionally, a cleavage product of BAA was also isolated. Mass spectra and fluorescence data support two different routes for the degradation of BaP by Mycobacterium sp. strain RJGII-135. The 7,8-BaP-dihydrodiol and three cleavage products of BaP, including 4,5-chrysene-dicarboxylic acid and a dihydro-pyrene-carboxylic acid metabolite, have been isolated and identified as degradation products formed by Mycobacterium sp. strain RJGII-135. These latter results represent the first example of the isolation of BaP ring fission products formed by a bacterial isolate. We propose that while this bacterium appears to attack only one site of the PYR molecule, it is capable of degrading different sites of the BAA and BaP molecules, and although the sites of attack may be different, the ability of this bacterium to degrade these PAH is well supported. The proposed pathways for biodegradation of these compounds by this Mycobacterium sp. strain RJGII-135 support the dioxygenase enzymatic processes reported previously for other bacteria. Microorganisms like Mycobacterium sp. strain RJGII-135 will be invaluable in attaining the goal of remediation of sites containing mixtures of these PAH.

Benz(a)Anthracenes↗

Aerobic biodegradation of 4-methylquinoline by a soil bacterium.

Methylquinolines and related N-heterocyclic aromatic compounds are common contaminants associated with the use of hydrocarbons in both coal gasification and wood treatment processes. These compounds have been found in groundwater, and many are known mutagens. A stable, five-member bacterial consortium able to degrade 4-methylquinoline was established by selective enrichment using soil collected from an abandoned coal gasification site. The consortium was maintained for 5 years by serial transfer in a medium containing 4-methylquinoline. A gram-negative soil bacterium, strain Lep1, was isolated from the consortium and shown to utilize 4-methylquinoline as a source of carbon and energy during growth in liquid medium. A time course experiment demonstrated that both the isolate Lep1 and the consortium containing Lep1 were able to degrade 4-methylquinoline under aerobic conditions. Complete degradation of 4-methylquinoline by either strain Lep1 alone or the consortium was characterized by the production and eventual disappearance of 2-hydroxy-4-methylquinoline, followed by the appearance and persistence of a second metabolite tentatively identified as a hydroxy-4-methylcoumarin. Currently, there is no indication that 4-methylquinoline degradation proceeds differently in the consortium culture compared with Lep1 alone. This is the first report of 4-methylquinoline biodegradation under aerobic conditions.

Aerobiosis↗

Comparative carcinogenicity, metabolism, mutagenicity, and DNA binding of 7H-dibenzo[c,g]carbazole and dibenz[a,j]acridine.

Complex mixtures that are produced from the combustion of organic materials have been associated with increased cancer mortality. These mixtures contain homocyclic and heterocyclic polycyclic aromatic hydrocarbons (PAHs), many of which are known carcinogens. In particular, N-heterocyclic aromatic compounds (NHA) are present in these mixtures. Studies to determine the metabolic activation of these compounds have been undertaken. The purpose of this review is to compare and contrast the metabolic activation and biological effects of two NHA, 7H-dibenzo[c,g]carbazole (DBC) and dibenz[a,j]acridine (DBA), in order to better assess the contribution of NHA to the carcinogenic potency of complex mixtures and to develop biomarkers of the carcinogenic process. DBC has both local and systemic effects in the mouse; it is a potent skin and liver carcinogen following topical application and a lung carcinogen following i.p. application. On the other hand, DBA is a moderate mouse skin carcinogen following topical application and a lung carcinogen following subcutaneous injection. The biological differences for DBC and DBA are reflected in target organ-specific proximate and mutagenic metabolites and DNA adduct patterns.

Acridines↗

Tissue-specific in vivo protein-DNA interactions at the promoter region of the Xenopus 63 kDa keratin gene during metamorphosis.

The Xenopus 63 kDa keratin gene is developmentally regulated and is expressed only in the epidermis. Full activation of the 63 kDa keratin gene requires two regulatory steps, the first independent and the second dependent on the thyroid hormone triiodothyronine (T3). Sequence analysis of a genomic clone of the 63 kDa keratin gene identified potential AP2 and SP1 binding sites upstream of the transcription initiation site. Electrophoretic mobility shift assays using purified or enriched proteins, as well as HeLa nuclear extract in conjunction with AP2- and SP1-specific antibodies, have been used to demonstrate that human AP2 and SP1 bind elements upstream of the transcription initiation site. In vivo footprinting with ligation mediated PCR revealed several footprints, within 350 bp upstream of the transcription initiation site, including those at the AP2 and SP1 sites, that are unique to epidermal cells which express the keratin gene. These footprints were absent in blood cells and XL177 cells which do not express the gene. Comparison of footprints between cells which express the 63 kDa keratin gene at low or high levels showed that the same binding sites are occupied, indicating that these sites are required for basal as well as T3-induced expression of the 63 kDa keratin gene.

Animals↗

Biotransformation of benzo[a]pyrene and other polycyclic aromatic hydrocarbons and heterocyclic analogs by several green algae and other algal species under gold and white light.

This laboratory has shown that the metabolism of benzo[a]pyrene (BaP), a carcinogenic polycyclic aromatic hydrocarbon (PAH), by a freshwater green alga, Selenastrum capricornutum, under gold light proceeds through a dioxygenase pathway with subsequent conjugation and excretion. This study was undertaken to determine: (1) the effects of different light sources on the enzymatic or photochemical processes involved in the biotransformation of BaP over a dose range of 5-1200 mg/l; (2) the phototoxicity of carcinogenic PAHs and mutagenic quinones to a green alga; (3) the ability of other algal systems to metabolize BaP. Cultures were exposed to different doses of BaP for 2 days at 23 degrees C under gold, white or UV-A fluorescent light on a diurnal cycle of 16 h light, 8 h dark. Under gold light, metabolites of BaP produced by Selenastrum capricornutum were the dihydrodiols of which the 11,12-dihydrodiol was the major metabolite. Under white light, at low doses, the major metabolite was the 9,10-dihydrodiol. With increasing dose, the ratio of dihydrodiols to quinones decreased to less than two. With increasing light energy output, from gold to white to UV-A in the PAH absorbing region, BaP quinone production increased. Of other carcinogenic PAHs studied, only 7H-dibenz[c,g]carbazole was as phototoxic as BaP while 7,12-dimethylbenz[a]anthracene, dibenz[a,j]acridine and non-carcinogenic PAHs, anthracene and pyrene, were not phototoxic. The 3,6-quinone of BaP was found to be highly phototoxic while quinones that included menadione, danthron, phenanthrene-quinone and hydroquinone were not. The data suggest that the phototoxicity of BaP is due to photochemical production of quinones; the 3,6-quinone of BaP is phototoxic and is probably the result of the production of short lived cyclic reactive intermediates by the interaction of light with the quinone. Lastly, only the green algae, Selenastrum capricornutum, Scenedesmus acutus and Ankistrodesmus braunii almost completely metabolized BaP to dihydrodiols. The green alga Chlamydomonas reinhardtii, the yellow alga Ochromonas malhamensis, the blue green algae Anabaena flosaquae and euglenoid Euglena gracilis did not metabolize BaP to any extent. The data indicate that algae are important in their ability to degrade PAHs but the degradation is dependent on the dose of light energy emitted and absorbed, the dose of PAHs to which the algae are exposed, the phototoxicity of PAHs and their metabolite(s) and the species and strain of algae involved. All of these factors will be important in assessing the degradation and detoxification pathways of recalcitrant PAHs by algae.

Anabaena↗

32P-postlabelling analysis of dibenz[a,j]acridine-DNA adducts in mice: identification of proximate metabolites.

N-Heterocyclic polynuclear aromatics are widely-occurring environmental pollutants formed during the pyrolysis of nitrogen-containing organic chemicals. Dibenz[a,j]acridine (DBA), a member of this class, has been shown to be a skin carcinogen in mice. We undertook studies to determine the organ distribution of DBA-DNA adducts and to identify the DBA metabolites which lead to the formation of carcinogen-DNA adducts in vivo. DBA and its metabolites, trans-DBA-1,2-dihydrodiol (DBA-1,2-DHD) trans-DBA-3,4-dihydrodiol (DBA-3,4-DHD) and trans-DBA-5,6-dihydrodiol (DBA-5,6-DHD), were topically applied on mice. DNA was isolated using enzyme-solvent extraction methods, and analyzed for carcinogen-DNA adducts using 32P-postlabelling. In skin, DBA produced two distinct adducts (Adducts 1 and 2). The same two adducts were seen when DBA-3,4-DHD was applied. In addition, the total adduct level elicited by DBA-3,4-DHD was twice that of the parent compound. Two adducts (Adducts 3 and 4) were also seen in mouse skin when DBA-5,6-DHD was applied, but these differed chromatographically from adducts seen with DBA. However, when DBA-3,4-DHD was applied and analyzed using sensitive nuclease P1 32P-postlabelling, all four adducts could be detected. These results suggest that the major route of DBA activation to DNA-binding species in skin is through formation of DBA-3,4-DHD and subsequent metabolism of this compound to a bay-region diol-epoxide. However, we postulate that another activation pathway may proceed through a bis-dihydrodiol-epoxide.

Acridines↗

Induction of micronuclei and sister chromatid exchanges by polycyclic and N-heterocyclic aromatic hydrocarbons in cultured human lymphocytes.

Many natural environments are contaminated with carcinogenic polycyclic aromatic hydrocarbons (PAHs) and N-heterocyclic aromatic hydrocarbons (NHAs) as complex mixtures of coal tar, petroleum, and shale oil. These potentially hazardous substances are prevalent at many former tar production and coal gasification sites. Three polycyclic [benzo(a)pyrene (BaP), benz(a)anthracene (BAA), and 7,12-dimethylbenz(a)anthracene (DMBA)] and two N-heterocyclic [7H-dibenzo(c,g)carbazole (DBC), and dibenz(a,j)acridine (DBA)] aromatic hydrocarbons were analyzed for cytotoxic and genotoxic effects on human lymphocytes. All of these polyaromatic compounds are normally present in the environment, except for DMBA. Lymphocytes from healthy donors were isolated from whole blood. The 5-ring polycyclic aromatic BaP consistently induced micronuclei in a linear dose-dependent manner with doses from 0.1-10.0 micrograms/ml, whereas the 4-ring compounds (BAA and DMBA) had no effect on the induction of micronuclei above controls except at 5 and 10 micrograms/ml. Of the two N-heterocyclic compounds, DBC produced a significant increase in micronuclei in lymphocytes, but the dose response tended to plateau above 0.1 microgram/ml. DBA showed an effect on the frequency of micronuclei above controls only at high doses of 5 and 10 micrograms/ml. The average background frequency of micronuclei for 7 lymphocyte donors averaged 3.1 per 1,000 stimulated cells, whereas the average frequency of micronuclei at 10 micrograms/ml BaP was 36.8 per 1,000 stimulated cells. The lowest effective dose in 2 donors for BaP occurred at 0.1 microgram/ml. At a challenge dose of 1 microgram/ml (4 microM) of BaP, considerable variation in micronuclei induction between 7 individuals was observed, ranging from 2-6-fold increases above spontaneous frequency. Over a dose range of 1-10.0 micrograms/ml (4-40 microM), BaP also induced sister chromatid exchanges (SCEs) in lymphocytes, whereas BAA had no effect above controls. Parallel studies of both cytogenetic endpoints showed that the micronucleus assay is a more sensitive indicator of BaP exposure at equivalent doses. Mitotic and replication indices of BaP-exposed lymphocytes showed that cell proliferation is only moderately inhibited even at the highest dose; this shows that bulky DNA-adducts are generally compatible with cell survival. The cytogenetic data are consistent, first-off, with reports that individuals in the population vary widely with respect to the inducibility of the CYP1A1 gene, which is known to be involved in polycyclic aromatic hydrocarbon metabolism, in particular, in BaP. Secondly, the data support the fact that polyaromatic compounds differ with regard to micronucleus induction within the same sample(s) of human lymphocytes, indicating selective metabolism of polyaromatic compounds that may reflect carcinogen sensitivity of the individual.(ABSTRACT TRUNCATED AT 400 WORDS)

9,10-Dimethyl-1,2-benzanthracene↗

Carcinogenicity of 7H-dibenzo[c,g]carbazole, dibenz[a,j]acridine and benzo[a]pyrene in mouse skin and liver following topical application.

N-Heterocyclic aromatics are by-products of incomplete combustion of organic material. The overall objective of this study was to determine the relative carcinogenic potencies of 7H-dibenzo[c,g]carbazole (DBC) and dibenz[a,j]acridine (DBA) in a bioassay of complete carcinogenicity on mouse skin in a sensitive strain (Hsd:ICR(Br)) which has been used in metabolism and DNA binding studies of N-heterocyclic aromatics. No-treatment, acetone and benzo[a]pyrene (BaP)-treated animals were used as negative and positive control groups. DBC (50 nmol), DBA (50 nmol), BaP (50 nmol) or DBC plus BaP (25 nmol + 25 nmol) were applied twice weekly in 50 microliters acetone to the backs of 50 female mice/group for 99 weeks or until the appearance of a tumor. DBC, DBA, BaP and DBC plus BaP produced skin tumors in 43, 32, 49 and 42 of 50 mice each based on weekly visual observations with latent periods of 55.1, 62.2, 33.4 and 33.8 weeks, respectively. The histopathology data indicated primary skin lesions in 42, 27, 48 and 47 mice for DBC, DBA, BaP and DBC plus BaP, respectively. In addition, primary liver lesions in 37 mice were present in the DBC group. The morphological and morphometric data indicated a significant increase (P < or = 0.05) in mononuclear cells in the dermis for the BaP and DBC plus BaP groups relative to the control group. Significant increases (P < or = 0.05) were observed in the nuclear area, nucleoli per nucleus and cellular area of hepatocytes in the DBC treatment group relative to the control group. These data indicate that DBC is a potent liver carcinogen as well as a skin carcinogen following topical application.

Acridines↗

Retardation of benzo[a]pyrene-induced epidermal tumor formation by the potent antioxidant 4b,5,9b,10-tetrahydroindeno[1,2-b]indole.

The ability of the potent antioxidant, 4b,5,9b,10-tetrahydroindeno[1,2-b]indole (THII), to inhibit tumor formation by topically-applied benzo[a]pyrene was evaluated using a complete carcinogenicity mouse skin bioassay. THII was administered by direct application to the skin, in the food or through the drinking water. In each case, THII increased the average time until the appearance of tumors by 4 weeks, and also decreased the total number of tumors compared with benzo[a]pyrene alone. These protective effects corresponded with the ability of THII to inhibit benzo[a]pyrene- or 12-O-tetradecanoylphorbol-13-acetate-induced epidermal ornithine decarboxylase activity, a biomarker of tissue proliferation in skin of the treated animals. This is the first report of an antioxidant administered in food or water inhibiting chemically induced skin carcinogenesis.

Administration, Topical↗

Upregulation of AP-2 in the skin of Xenopus laevis during thyroid hormone-induced metamorphosis.

During amphibian metamorphosis dramatic changes occur in the morphogenesis and differentiation of the epidermis. Concurrently with these changes, the 63 kDa keratin gene is upregulated from low basal levels to high levels. What makes these processes unique is that they are controlled by triiodothyronine (T3) and can be duplicated in cultures of purified epidermal cells. Since there is a 2 day lag period between the addition of T3 and the upregulation of keratin gene expression and terminal differentiation, recent studies have focused on identifying the genes activated during the lag period. We assume that the transcription factors required for upregulation of the keratin gene are induced by T3 during the lag period, and therefore we have cloned the keratin gene so that promoter analyses can be conducted. S1 mapping assays have shown that the same transcription start sites are used during premetamorphosis when the keratin gene is basally expressed, during metamorphosis when it is T3-upregulated, and in the adult epidermis where it is expressed independently of T3. During the early part of the lag period TR beta and AP-2 mRNA levels are upregulated in the epidermis by T3. The transcription factor AP-2 is expressed at high levels in the skin of premetamorphic larvae and induced about fivefold by T3 but is not induced in an epithelial cell line (XL-177). Since the keratin mRNA, AP-2 mRNA, and other genes induced during the lag period are expressed in premetamorphic larvae it appears that T3 functions by upregulating the expression of genes previously activated by a T3-independent process. This preprogramming may account for the tissue specificity of T3 action during metamorphosis.

Animals↗

Fluorescence spectroscopic studies on the identification and quantification of 7H-dibenzo[c,g]carbazole and dibenz[a,j]acridine metabolites.

Fluorescence spectroscopic techniques were developed and employed in the identification and quantitation of the metabolites of the carcinogenic pollutants 7H-dibenzo[c,g]carbazole (DBC) and dibenz[a,j]acridine (DBA) after HPLC separation. Metabolites formed in vitro with 3-methylcholanthrene (3-MC)-induced Sprague-Dawley rat liver microsomal preparations were used as the model for this research. The fluorescence spectra of the three major DBC metabolites matched those of the synthetic standards, 1-OH-, 3-OH- and 5-OH-DBC, respectively. Similarly, the fluorescence spectra of the four major DBA metabolites matched those of the synthetic standards, 1,2-diol-, 3,4-diol-, 5,6-diol- and 5,6-epoxide-DBA, respectively. Synchronous fluorescence spectroscopy (SFS) has been especially helpful for the identification of these metabolites since it produces a single peak for each compound. Regression equations of the SFS peak areas versus concentrations of the synthetic standards were used to calculate quantities of the microsomal metabolites from the SFS peak areas of the metabolites. These values were comparable with those quantities calculated from radioactivity measurements. The use of HPLC combined with SFS is a convenient and sensitive non-radiometric method which can be used to identify and quantify DBC and DBA metabolites.

Acridines↗