Cutaneous metabolism of benzo[a]pyrene: comparative studies in C57BL/6N and DBA/2N mice and neonatal Sprague--Dawley rats

The metabolism of the polycyclic aromatic hydrocarbon (PAH) carcinogen benzo[a]pyrene (BaP) was studied using microsomes prepared from the skin of the mouse and rat. Topical application of the polychlorinated biphenyl (PCB) Aroclor 1254 or the PAH 3-methylcholanthrene (3-MC) to the skin of the C57BL/6N and DBA/2N mouse and the Sprague-Dawley rat caused statistically significant enhancement of cutaneous microsomal aryl hydrocarbon hydroxylase (AHH) activity in each animal. PCB was a more potent inducer of the enzyme than was 3-MC. BaP metabolism by skin microsomes from the same animals was assessed using high performance liquid chromatography (HPLC). The skin of untreated animals metabolized BaP into 9,10-, 7,8- and 4,5-dihydrodiols, phenols and quinones. Skin application of PCB caused greater than 16–18-fold enhancement of BaP metabolism in the C57BL/6N mouse and the rat and 2–5-fold enhancement in the DBA/2N mouse. Skin application of 3-MC enhanced BaP metabolism 2–8-fold in the C57BL/6N mouse and 5–10-fold in the rat and had no effect in the DBA/2N mouse. The formation of procarcinogenic metabolite BaP-7, 8-diol was greatly enhanced (4–12-fold) by treatment with the PCB and 3-MC in the tumor susceptible C57BL/6N mouse and in the tumor-resistant neonatal Sprague-Dawley rat. In contrast, the formation of BaP-7,8-diol was either slightly enhanced (2-fold) or unaffected by treatment with the PCB or 3-MC in the tumor-resistant DBA/2N mouse. Our data indicate that neither the patterns of metabolism nor the amount of BaP-7,8-diol formation in the skin are reliable predictors of tumor susceptibility to the PAH in rodent skin.     

Strain differences in histamine release from mouse peritoneal mast cells induced by compound 48/80 or A23187

Strain differences among BALB/c, BDF1, CDF1, C3 H/He, C57 BL/6, DBA/2, ddy and ICR mice were investigated with respect to the ratios of histamine release from mouse peritoneal mast cells induced by compound 48/80, a Ca2+ dependent histamine releaser, and the Ca2+ ionophore A23187. The ratios of histamine release from mouse peritoneal mast cells induced by compound 48/80 were found to be high in BALB/c, ddY and ICR mice, but low in BDF1, CDF1, C3 H/He, C57 BL/6 and DBA/2 mice. Those induced by Ca2+ ionophore A23187 were high in BALB/c, BDF1, CDF1, C3 H/He, DBA2, ddy and ICR mice but low in C57 BL/6 mice. These results indicate that differences in histamine release from mouse peritoneal mast cells are strain dependent.     

Spontaneous calcified tongue lesions in DBA mice

Large numbers of spontaneously occurring polypoid or slightly elevated lesions were observed in the tongue, mainly the dorsum linguae near the margo linguae, of DBA mice. Histologically the lesion consisted of granulation tissue with focal calcification, and involved superficially the tongue muscle. Often the calcareous deposits were encircled by multinuclear giant cells. The frequency of the calcified tongue lesion was high in lines of DBA/2 (DBA/2NCrj, DBA/2NJcl and DBA/2J), and DBA/1 (DBA/1Jcl and DBA/1J); the SM/J, BALB/c, C57BL/6 and C3H/He strains did not have the lesion. Among hybrid mice, CDF1, a hybrid of DBA/2 and BALB/c, a few had the lesions but no BDF1 mice, a hybrid of DBA/2 and C57BL/6, had any. The frequency was high in the hybrids of DBA/1 and SM/J. These results seem to indicate that the occurrence of the tongue calcified lesions was controlled by polygene.     

Inhibitory effect of 7,8-benzoflavone on DMBA- and BaP-induced bone marrow micronuclei in mouse

Frequencies of micronucleated polychromatic erythrocytes (PCE) were analyzed in bone-marrow cells of mice injected with 7,12-dimethylbenz[a]anthracene (DMBA), benzo[a]pyrene (BaP), 7,8-benzoflavone (-naphthoflavone) and the combination of either 7,8-benzoflavone and DMBA or 7,8-benzoflavone and BaP. 7,8-Benzoflavone was injected 48 and 24 h before injecting mice either with DMBA or BaP. Bone-marrow samples were collected at 24, 48, 72 and 96 h. The observed maximum mean number of micronucleated PCE per 500 PCE was 8.6 at 48 h with DMBA and 11.6 at 72 h with BaP. 7,8-Benzoflavone reduced the number of micronucleated PCE in the above treatments with DMBA by 90% and in the case of BaP by 75%. In other words, 7,8-benzoflavone acted as a potent inhibitor in preventing chromosomal breaks caused by DMBA or BaP.     

Effect of tobacco smoke components on organogenesis in plant tissues

Callus tissue derived from haploid plants of Nicotiana tabacumdifferentiated when inoculated on media fortified with differentconcentrations of tobacco smoke components: benzo(a)pyrene (BaP),benzo(e)pyrene (BeP), dibenz(a, h)anthracene (DBA), pyrene andchrysene. Neither any auxins nor cytokinins were present inthe medium. BaP was found to be the most potent morphogeneticagent. However, these treatments did not induce any vegetativebuds on the callus obtained from diploid plants of tobacco. ¹ This study was carried out under Contract No. 12-14-100-10341(73)with the Agricultural Research Service, U. S. Department ofAgriculture, administered by the Eastern Marketing and NutritionResearch Division, 600 East Mermaid Lane, Philadelphia, Pennsylvania19118, U.S.A. (Received February 4, 1971; )     

Metabolism of benzo[a]pyrene: Effect of 3-methylcholanthrene pretreatment on metabolism by microsomes from lungs of genetically “responsive” and ”nonresponsive” mice

The metabolism of [¹⁴C]benzo[a]pyrene by microsomes from the lungs of normal and 3-methylcholanthrene-treated DBA/2J, C57BL/6J, and A/HeJ mouse strains was quantitatively analyzed by high-pressure liquid chromatography. The ratio of dihydrodiols of benzo[a]pyrene to total metabolites formed was greater with lung microsomes than with liver microsomes in all three strains. The ratio of epoxide hydrase to monooxygenase activity in mouse lung was shown to be considerably higher than in mouse liver. Benzo[a]pyrene metabolism by control lung microsomes showed some strain differences. C57BL/6J and A/HeJ mice formed twice as much dihydrodiols as a percentage of total metabolism compared to DBA/2J mice. DBA/2J mice produced somewhat less phenol 2 fraction and considerably more quinone 1 and 2 fractions than the other two mouse strains as a percentage of total metabolism. Treatment of C57BL/6J and DBA/2J mice with 3-methylcholanthrene resulted in a 20-fold increase in the metabolism of benzo[a]pyrene, while A/HeJ mice were induced more than 50-fold. The profiles of metabolites from the 3-methylcholanthrene-induced animals were nearly identical in all three mouse strains.     

Inhibitory effect of toluene on tumor promotion in mouse skin

In the two-stage mouse model for skin tumorigenesis with phorbol-12-myristate-13-acetate (PMA) as promoter, topical application of 40 microliters of toluene 2X/week at the initiation/promotion site (the back) reduced the average number of tumors/mouse (ANT/M) to approximately one-fourth that of controls. Control procedure involved initiation of C3H mice with benzo[a]pyrene (BaP) and CD-1 mice with 7,12-dimethylbenz[a]anthracene (DMBA) followed by promotion with from 1 to 5 micrograms PMA in 40 microliters acetone 2X/week. Forty microliters of toluene 2X/week per se was a weak promoter (6-13% of control ANT/M), and produced mild skin irritation at the application site but behavior and body weights were normal. The toluene inhibition of tumorigenesis was not a direct chemical action on PMA since similar effects occurred whether toluene was the vehicle for PMA or whether it was applied up to 1 day before PMA (i.e., prepromotion). Prepromotion with acetone had no effect on tumorigenesis, substantiating its use as control vehicle and suggesting that the toluene inhibition was a specific tissue reaction. The inhibitory effect appeared to be on PMA promotion rather than on initiation since toluene and acetone produced similar numbers of tumors when used as the vehicle for BaP or DMBA in two-stage or BaP in single-stage trials. The inhibition was not permanent since tumorigenesis returned to control rates 2-3 weeks after prepromotion with toluene ceased but promotion with PMA in acetone continued. Toluene may be unique among reported promotion inhibitors in that it is a widely used commercial chemical which sometimes serves as a vehicle in cancer-screening trials. Since its metabolism is reasonably well defined, it may be of value in exploring further the process of tumor promotion.     

Removal and transformation of high molecular weight polycyclic aromatic hydrocarbons in water by live and dead microalgae

The removal and transformation of seven high molecular weight polycyclic aromatic hydrocarbons (PAHs), namely benz[a]anthracene, benzo[b]fluoranthene, benzo[k]fluoranthene, benzo[a]pyrene, dibenzo[a,h]anthracene, indeno[1,2,3-c,d]pyrene and benzo[g,h,i]perylene, by a freshwater microalga Selenastrum capricornutum under gold and white light irradiation was studied. The two light sources did not result in significant differences in the biodegradation of the selected PAHs in live algal cells, but white light was more effective in promoting photodegradation than was gold light in dead cells. The removal efficiency of seven PAHs, as well as the difference between live and dead microalgal cells, was PAH compound-dependent. Benz[a]anthracene and benzo[a]pyrene were highly transformed in live and dead algal cells, and dead cells displayed greater transformation levels than live cells. Further investigation comparing the transformation of single PAH compound, benzo[a]pyrene, by S. capricornutum and another green microalgal species, Chlorella sp., demonstrated that the transformation in dead cells was similar, indicating the process was algal-species independent. Dead algal cells most likely acted as a photosensitizer and accelerated the photodegradation of PAHs.     

Differences in antibody production against mouse hepatitis virus (MHV) among mouse strains

Several strains of mice were examined for antibody production after intranasal inoculation with a low virulence strain of mouse hepatitis virus (MHV), MHV-NuU. C57BL/6N mice were shown to be high responders in the production of complement fixing (CF) antibody as compared to C3H/HeN, BALB/c-AnN, DBA/2N mice. F1 hybrids B6C3 and BDF1 from C57BL/6N mice, showed CF antibody responses as high as C57BL/6N, suggesting that high responsiveness is genetically controlled. All these mouse strains were able to produce high titred neutralizing antibody to MHV.     

Degradation and mineralization of high-molecular-weight polycyclic aromatic hydrocarbons by defined fungal-bacterial cocultures

This study investigated the biodegradation of high-molecular-weight polycyclic aromatic hydrocarbons (PAHs) in liquid media and soil by bacteria (Stenotrophomonas maltophilia VUN 10,010 and bacterial consortium VUN 10,009) and a fungus (Penicillium janthinellum VUO 10, 201) that were isolated from separate creosote- and manufactured-gas plant-contaminated soils. The bacteria could use pyrene as their sole carbon and energy source in a basal salts medium (BSM) and mineralized significant amounts of benzo[a]pyrene cometabolically when pyrene was also present in BSM. P. janthinellum VUO 10,201 could not utilize any high-molecular-weight PAH as sole carbon and energy source but could partially degrade these if cultured in a nutrient broth. Although small amounts of chrysene, benz[a]anthracene, benzo[a]pyrene, and dibenz[a,h]anthracene were degraded by axenic cultures of these isolates in BSM containing a single PAH, such conditions did not support significant microbial growth or PAH mineralization. However, significant degradation of, and microbial growth on, pyrene, chrysene, benz[a]anthracene, benzo[a]pyrene, and dibenz[a,h]anthracene, each as a single PAH in BSM, occurred when P. janthinellum VUO 10,201 and either bacterial consortium VUN 10,009 or S. maltophilia VUN 10,010 were combined in the one culture, i.e., fungal-bacterial cocultures: 25% of the benzo[a]pyrene was mineralized to CO(2) by these cocultures over 49 days, accompanied by transient accumulation and disappearance of intermediates detected by high-pressure liquid chromatography. Inoculation of fungal-bacterial cocultures into PAH-contaminated soil resulted in significantly improved degradation of high-molecular-weight PAHs, benzo[a]pyrene mineralization (53% of added [(14)C]benzo[a]pyrene was recovered as (14)CO(2) in 100 days), and reduction in the mutagenicity of organic soil extracts, compared with the indigenous microbes and soil amended with only axenic inocula.     

Unexpected DNA damage caused by polycyclic aromatic hydrocarbons under standard laboratory conditions

The genotoxicity of 15 polycyclic aromatic hydrocarbons was determined with the alkaline version of the comet assay employing V79 lung fibroblasts of the Chinese hamster as target cells. These cells lack the enzymes necessary to convert PAHs to DNA-binding metabolites. Surprisingly, 11 PAHs, i.e., benzo[a]pyrene (BaP), benz[a]anthracene, 7,12-dimethylbenz[a]anthracene, 3-methylcholanthrene, fluoranthene, anthanthrene, 11H-benzo[b]fluorene, dibenz[a,h]anthracene, pyrene, benzo[ghi]perylene and benzo[e]pyrene caused DNA strand breaks even without external metabolic activation, while naphthalene, anthracene, phenanthrene and naphthacene were inactive. When the comet assay was performed in the dark or when yellow fluorescent lamps were used for illumination the DNA-damaging effect of the 11 PAHs disappeared. White fluorescent lamps exhibit emission maxima at 334.1, 365.0, 404.7, and 435.8 nm representing spectral lines of mercury. In the case of yellow fluorescent lamps these emissions were absent. Obviously, under standard laboratory illumination many PAHs are photo-activated, resulting in DNA-damaging species. This feature of PAHs should be taken into account when these compounds are employed for the initiation of skin cancer. The genotoxicity of BaP that is metabolically activated in V79 cells stably expressing human cytochrome P450-dependent monooxygenase (CYP1A1) as well as human epoxide hydrolase (V79-hCYP1A1-mEH) could not be detected with the comet assay performed under yellow light. Likewise the DNA-damaging effect of r-7,t-8-dihydroxy-t-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (anti-BaPDE) observed with the comet assay was only weak. However, upon inhibition of nucleotide excision repair (NER), which is responsible for the removal of stable DNA adducts caused by anti-BaPDE, the tail moment rose 3.4-fold in the case of BaP and 12.9-fold in the case of anti-BaPDE. These results indicate that the genotoxicity of BaP and probably of other compounds producing stable DNA adducts are reliably detected with the comet assay only when NER is inhibited.     

Metabolism of benzo[a]pyrene and 7,12-dimethylbenz[a]anthracene in cultured human fetal aortic smooth muscle cells.

Cultured human fetal aortic smooth muscle cells derived from the abdominal aorta converted benzo[a]pyrene (BaP) and 7,12-dimethylbenz[a]anthracene (DMBA) $\text{via}$ cytochrome P-450-dependent monooxygenation to metabolites detectable by both a highly sensitive radiometric assay and high pressure liquid chromatography (HPLC). Cells incubated with ³H-BaP transformed this substrate primarily to phenols. ¹⁴C-DMBA was converted to metabolites that cochromatographed with 12-hydroxymethyl-7-methylbenz[a]anthracene, 7-hydroxymethyl-12-methylbenz-[a]anthracene, 7,12-dihydroxymethylbenz[a]anthracene, and trans-8,9-dihydrodiol-7,12-DMBA. Exposure of cells in culture to 13 μM 1,2-benz[a]anthracene resulted in increased oxidative metabolism of both BaP and DMBA. In the case of BaP, total phenol formation was increased, while with DMBA all metabilities detected by HPLC were increased. Support for the potential role of metabolism of polycyclic aromatic hydrocarbons by aortic smooth muscle cells in the etiology of atherosclerosis was obtained.     

Aryl hydrocarbon receptor-mediated activity of mutagenic polycyclic aromatic hydrocarbons determined using in vitro reporter gene assay

Activation of aryl hydrocarbon receptor (AhR) by 30 polycyclic aromatic hydrocarbons (PAHs) was determined in the chemical-activated luciferase expression (CALUX) assay, using two exposure times (6 and 24h), in order to reflect the metabolization of PAHs. AhR-inducing potencies of PAHs were expressed as induction equivalency factors (IEFs) relative to benzo[a]pyrene and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). In 24h exposure assay, the highest IEFs were found for benzo[k]fluoranthene, dibenzo[a,h]anthracene and dibenzo[a,k]fluoranthene (approximately three orders of magnitude lower than TCDD) followed by dibenzo[a,j]anthracene, benzo[j]fluoranthene, indeno[1,2,3-cd]pyrene, and naphtho[2,3-a]pyrene. The 6h exposure to PAHs led to a significantly higher AhR-mediated activity than the 24h exposure (generally by two orders of magnitude), probably due to the high rate of PAH metabolism. The strongest AhR inducers showed IEFs approaching that of TCDD. Several PAHs, including some strong mutagens, such as dibenzo[a,l]pyrene, cyclopenta[cd]pyrene, and benzo[a]perylene, elicited only partial agonist activity. Calculation of IEFs based on EC25 values and/or 6h exposure data is suggested as an alternative approach to estimation of toxic potencies of PAHs with high metabolic rates and/or the weak AhR agonists. The IEFs, together with the recently reported relative mutagenic potencies of PAHs [Mutat. Res. 371 (1996) 123; Mutat. Res. 446 (1999) 1] were combined with data on concentrations of PAHs in extracts of model environmental samples (river sediments) to calculate AhR-mediated induction equivalents and mutagenic equivalents. The highest AhR-mediated induction equivalents were found for benzo[k]fluoranthene and benzo[j]fluoranthene, followed by indeno[1,2,3-cd]pyrene, dibenzo[a,h]anthracene, benzo[a]pyrene, dibenzo[a,j]anthracene, chrysene, and benzo[b]fluoranthene. High mutagenic equivalents in the river sediments were found for benzo[a]pyrene, dibenzo[a,e]pyrene, and naphtho[2,3-a]pyrene and to a lesser extent also for benzo[a]anthracene, benzo[b]fluoranthene, indeno[1,2,3-cd]pyrene, benzo[j]fluoranthene, dibenzo[a,e]fluoranthene and dibenzo[a,i]pyrene. These data illustrate that AhR-mediated activity of PAHs, including the highly mutagenic compounds, occurring in the environment but not routinely monitored, could significantly contribute to their adverse effects.     

Dimethylnitrosamine metabolism: II. In vitro activation of dimethylnitrosamine by hepatic and renal tissues from crosses among BALB/c, DBA and C57BL mice

Crosses among BALB/c, C57BL and DBA mice were performed to investigate the genetic mechanisms involved in metabolism of DMN by renal and hepatic tissues. Liver S-9 fractions from parental strain DBA had the greatest potential to activate DMN and liver fractions from parental strain BALB/c had the lowest. No age or sex-related differences were observed within strain. Crossing of either C57BL or DBA to BALB/c mice resulted in F1 hybrids with liver microsomal enzymes that gave results similar to the BALB/c parental strain. There were no sex or age differences within crossbred strains in the potential of liver to activate DMN. In contrast male DBA and C57BL parental mice renal S-9 fractions did not differ significantly from each other but did differ significantly from male BALB/c renal fractions and from female and immature animals of all strains. Crossing of either DBA or C57BL mice with BALB/c mice resulted in male F1 hybrids whose renal S-9 fractions did not differ significantly from males of the parental BALB/c strain. In all instances, male renal S-9 fractions had a significantly greater potential to activate DMN than female or immature animals. F1 DBA X C57BL hybrids had renal S-9 fractions that did not differ significantly from the parental strains. These data suggest that the gene(s) for low DMN metabolism of BALB/c mice are apparently dominant over the genes from both DBA and C57BL. The exact genetic or physiological mechanism needs further elucidation.     

Acute cytotoxicities of polynuclear aromatic hydrocarbons determined in vitro with the human liver tumor cell line,HepG2

The neutral red in vitro cytotoxicity assay was adapted for use with the human hepatocellular tumor cell line HepG2 to detect the cytotoxic potencies of polynuclear aromatic hydrocarbons (PAHs). Using benzo[a]pyrene (B[a]P) as the representative PAH, it was determined that a 3-day exposure was the most suitable for detecting cytotoxic potency and that preexposure to S g/ ml Arochlor enhanced the sensitivity of the HepG2 cells to the toxicant. Such enhanced sensitivity probably reflected increased metabolic conversion of the B[a]P to active metabolites after culturing the cells in the presence of Arochlor. This was shown by a 3-fold increase in the activity of 7-ethoxycoumarin deethylase, an indicator of mixed-function oxygenase activity. Furthermore, a reduction in sensitivity to B[a]P occurred when the cells were cultured in the presence of -napthoflavone, an inhibitor of aryl hydrocarbon hydroxylase activity. When Arochlor-induced cells were transferred to medium lacking Arochlor, the level of 7-ethoxycoumarin deethylase quickly declined to basal levels. Arochlor-induced cells were also able to detect the cytotoxic potencies of benzo[k]fluoranthene, benzo[b]-fluoranthene, chrysene, benzo[a]anthracene pyrene, phenanthrene, and fluoranthene, whereas fluorene, anthracene, acenaphthene, and acenaphthylene were not cytotoxic.Abbreviations AHH aryl hydrocarbon hydroxylase - 7-EDase 7-ethoxycoumarin O-deethylase - 3-MC 3-methylcholanthrene - MFO mixed function oxidase - NR neutral red - PAH polycyclic aromatic hydrocarbon     

Oxidation of polycyclic aromatic hydrocarbons by the bacterial laccase CueO from E. coli

Laccases produced by white rot fungi are capable of rapidly oxidizing benzo[a]pyrene. We hypothesize that the polycyclic aromatic hydrocarbon (PAH)-degrading bacteria producing laccase can enhance the degree of benzo[a]pyrene mineralization. However, fungal laccases are glycoproteins which cannot be glycosylated in bacteria, and there is no evidence to show that bacterial laccases can oxidize benzo[a]pyrene. In this study, the in vitro oxidation of PAHs by crude preparations of the bacterial laccase, CueO, from Escherichia coli was investigated. The results revealed that the crude CueO catalyzed the oxidation of anthracene and benzo[a]pyrene in the same way as the fungal laccase from Trametes versicolor, but showed specific characteristics such as thermostability and copper dependence. In the presence of 2,2'-azino-bis-(3-ethylbenzothiazoline-6-sulfonic acid), high amounts of anthracene and benzo[a]pyrene, 80% and 97%, respectively, were transformed under optimal conditions of 60°C, pH 5, and 5 mmol l(-1) CuCl(2) after a 24-h incubation period. Other PAHs including fluorene, acenaphthylene, phenanthrene, and benzo[a]anthracene were also oxidized by the crude CueO. These findings indicated the potential application of prokaryotic laccases in enhancing the mineralization of benzo[a]pyrene by PAH-degrading bacteria.     

Fungal metabolism and detoxification of polycyclic aromatic hydrocarbons

The mutagenic activity of ethyl acetate extracts of culture medium from Cunninghamella elegans incubated 72 h with various polycyclic aromatic hydrocarbons (PAHs) was evaluated in the Salmonella typhimurium reversion assay. All of the PAH extracts were assayed in tester strains TA98 and TA100 both with and without metabolic activation using a liver fraction from Aroclor 1254-treated rats. None of the extracts from fungal incubations with the mutagenic PAHs, benzo[a]pyrene, 7,12-dimethylbenz[a]anthracene, 3-methylcholanthrene and benz[a]anthracene, as well as the non-mutagenic PAHs, naphthalene, phenanthrene and anthracene, displayed any appreciable mutagenic activity. In addition, time course experiments indicated that the rate of decrease in mutagenic activity in the extracts from cultures incubated with benzo[a]pyrene or 7,12-dimethylbenz[a]anthracene was coincident with the rate of increase in total metabolism. The results demonstrated the ability of the fungus C. elegans to detoxify known carcinogens and mutagens and suggests that this organism may play an important role in the metabolism and inactivation of PAHs in the environment.Abbreviations hplc high performance liquid chromatography - tlc thin layer chromatography - PAH polycyclic aromatic hydrocarbon     

High mutagenic potency of several polycyclic aromatic hydrocarbons induced by liver postmitochondrial fractions from control and xenobiotic-treated immature carp

The metabolism of carcinogens in fish was examined by measuring the activation of different polycyclic aromatic hydrocarbons (PAH) by carp (Cyprinus carpio L.) liver post-mitochondrial fractions (S9) using the Salmonella typhimurium TA100 reverse mutation assay. For this study, 1 non-carcinogen, anthracene (AN), and 4 carcinogens, chrysene (CHR), benzo[a]pyrene (BaP), 3-methylcholanthrene (3MC) and 7,12-dimethylbenzanthracene (DMBA), were chosen. The bioactivating potency of the metabolic systems of carp pretreated with phenobarbital (PB), 3MC or Aroclor 1254 (ARO) were compared to uninduced carp liver. The results show that carp liver has the ability to metabolize carcinogenic PAH into mutagenic metabolites, which is enhanced when carp are pretreated with 3MC or ARO, but not with PB. A positive correlation between the induction of aryl hydrocarbon hydroxylase (AHH) activity in carp liver and the mutagenic potencies of CHR, BaP, DMBA and 3MC, has been observed. The bioactivating ability of carp liver S9 was compared with the ability of the same fractions from female Wistar rats (this study) as well as from Sprague-Dawley rats (literature data). When the mutagenic potencies of selected PAH had been normalized on the activity of BaP, the following order of mutagenic activities with S9 fractions from ARO-treated animals was obtained: (1) BaP (1) greater than DMBA (0.26) greater than 3MC (0.22) greater than CHR (0.05) greater than AN (0) for carp; (2) BaP (1) greater than 3MC (0.48) greater than CHR (0.31) greater than DMBA (0.16) greater than AN (0) for Sprague-Dawley rats; and (3) BaP (1) greater than 3MC (0.17) greater than DMBA (0.11) greater than CHR (0) = AN (0) for female Wistar rats. We conclude that carp and rats are very similar in their ability to activate carcinogenic PAH into mutagenic metabolites, which suggests that carp may be very susceptible to the carcinogenic activity of these compounds. According to our results from the mutagenicity study, as well as from the enzyme induction study, we propose the use of carp as a suitable model system for the study of chemical carcinogens.     

Importance of the route of administration for genetic differences in benzo[a]pyrene-induced in utero toxicity and teratogenicity

C57BL/6N (Ahb/Ahb) mice have a high-affinity Ah receptor in tissues, whereas AKR/J and DBA/2N (Ahd/Ahd) mice have a poor-affinity Ah receptor. The cytochrome P1-450 induction response (enhanced benzo[a]pyrene metabolism) occurs much more readily in Ahb/Ahb and Ahb/Ahd than in Ahd/Ahd mice, at any given dose of the inducer benzo[a]pyrene. Embryos from the AKR/J X (C57BL/6N)(AKR/J)F1 and the reciprocal backcross were studied during benzo[a]pyrene feeding of the pregnant females. Oral benzo[a]pyrene (120 mg/kg/day) given to pregnant Ahd/Ahd mice between gestational day 2 and 10 produces more intrauterine toxicity and malformations in Ahd/Ahd than Ahb/Ahd embryos. This striking allelic difference is not seen in pregnant Ahb/Ahd mice receiving oral benzo[a]pyrene. Pharmacokinetics studies with [3H]benzo[a]pyrene in the diet and high-performance liquid chromatographic analysis of benzo[a]pyrene metabolism in vitro by the maternal intestine, liver, and ovary and the embryos of control and oral benzo[a]pyrene-treated pregnant females are consistent with "first-pass elimination" kinetics and differences in benzo[a]pyrene metabolism by the embryos and/or placentas versus maternal tissues. In the pregnant Ahd/Ahd mouse receiving oral benzo[a]pyrene, little induction of benzo[a]pyrene metabolism occurs in her intestine and liver; this leads to much larger amounts of benzo[a]pyrene reaching her embryos, and genetic differences in toxicity and teratogenesis are manifest. In the pregnant Ahb/Ahd mouse receiving oral benzo[a]pyrene, benzo[a]pyrene metabolism is greatly enhanced in her intestine and liver; this leads to less benzo[a]pyrene reaching her embryos, much less intrauterine toxicity and malformations, and no genetic differences are manifest. More toxic metabolites (especially benzo[a]pyrene 1,6- and 3,6-quinones) are shown to occur in Ahd/Ahd embryos than in Ahb/Ahd embryos. In additional studies, no prenatal or neonatal "imprinting" effect in C57BL/6N mice by 2,3,7,8-tetrachlorodibenzo-p-dioxin or Aroclor 1254 on benzo[a]pyrene metabolism later in life was detectable. These genetic differences in intrauterine toxicity and teratogenicity induced by oral benzo[a]pyrene are just opposite those induced by intraperitoneal benzo[a]pyrene [Shum et al., '79; Hoshino et al., '81). The data in the present report emphasize the importance of the route of administration when the teratogen induces its own metabolism.     

Levels,Sources, and Toxic Potential of Polycyclic Aromatic Hydrocarbons in Urban Soil of Delhi,India

This study was done to determine the concentration of PAHs in urban soil of Delhi (India). Surface top soil (up to 10 cm depth) samples were collected from four different sampling sites including industrial, roadside, residential, and agricultural areas of Delhi and 16 USEPA priority polycyclic aromatic hydrocarbons (PAHs) were evaluated. Total PAH concentrations at industrial, roadside, residential, and agricultural sites were 11.46 ± 8.39, 6.96 ± 4.82, 2.12 ± 1.12, and 1.55 ± 1.07 mg/kg (dry weight), respectively, with 3–7 times greater concentrations in industrial and roadside soils than that in residential and agricultural soils. The PAH pattern was dominated by 4- and 5-ring PAHs (contributing >50% to the total PAHs) at industrial and roadside sites with greater concentration of fluoranthene, chrysene, benzo[b]fluoranthene, benzo[k]fluoranthene, benzo[a]anthracene, benzo[ghi]perylene, and pyrene, whereas, residential and agricultural sites showed a predominance of low molecular weight 2- and 3-ring PAHs (fluoranthene, acenaphthene, naphthalene, chrysene, and anthracene). Isomeric pair ratios suggested biomass combustion and fossil fuel emissions as the main sources of PAHs. The toxic equivalency factors (TEFs) showed that carcinogenic potency (benzo[a]pyrene-equivalent concentration (B[a]P_eq) of PAH load in industrial and roadside soils was ～10 and ～6 times greater than the agricultural soil.