The aryl hydrocarbon receptor-dependent deregulation of cell cycle control induced by polycyclic aromatic hydrocarbons in rat liver epithelial cells

Disruption of cell proliferation control by polycyclic aromatic hydrocarbons (PAHs) may contribute to their carcinogenicity. We investigated role of the aryl hydrocarbon receptor (AhR) in disruption of contact inhibition in rat liver epithelial WB-F344 'stem-like' cells, induced by the weakly mutagenic benz[a]anthracene (BaA), benzo[b]fluoranthene (BbF) and by the strongly mutagenic benzo[a]pyrene (BaP). There were significant differences between the effects of BaA and BbF, and those of the strongly genotoxic BaP. Both BaA and BbF increased percentage of cells entering S-phase and cell numbers, associated with an increased expression of Cyclin A and Cyclin A/cdk2 complex activity. Their effects were significantly reduced in cells expressing a dominant-negative AhR mutant (dnAhR). Roscovitine, a chemical inhibitor of cdk2, abolished the induction of cell proliferation by BbF. However, neither BaA nor BbF modulated expression of the principal cdk inhibitor involved in maintenance of contact inhibition, p27(Kip1), or pRb phosphorylation. The strongly mutagenic BaP induced apoptosis, a decrease in total cell numbers and significantly higher percentage of cells entering S-phase than either BaA or BbF. Given that BaP induced high levels of Cyclin A/cdk2 activity, downregulation of p27(Kip1) and hyperphosphorylation of pRb, the accumulation of cells in S-phase was probably due to cell proliferation, although S-phase arrest due to blocked replication forks can not be excluded. Both types of effects of BaP were significantly attenuated in dnAhR cells. Transfection of WB-F344 cells with siRNA targeted against AhR decreased induction of Cyclin A induced by BbF or BaP, further supporting the role of AhR in proliferative effects of PAHs. This suggest that activation of AhR plays a significant role both in disruption of contact inhibition by weakly mutagenic PAHs and in genotoxic effects of BaP possibly leading to enhanced cell proliferation. Thus, PAHs may increase proliferative rate and the likelihood of fixation of mutations.     

Uncertainty-based dynamic multimedia human health risk assessment for polycyclic aromatic hydrocarbons (PAHs) in a land oil exploitation area

With the increasing development of the petrochemical industry and the growing demand for oil, polycyclic aromatic hydrocarbons (PAHs) pollutions in the environment, especially in petroleum exploitation areas, are caused by the discharge of waste from the petroleum extraction process into an environmental system. This study aims to develop a new health risk assessment approach based on interval dynamic multimedia fugacity (IDMF) model and uncertainty analysis that could analyze the human exposure risk level for PAH contamination. The developed IDM health risk assessment (IDMHRA) approach is applied to assess previous, current, and future risks at a case study site in Daqing, Heilongjiang, China, from 1985 to 2020 for model validation. The human health risk assessment results show that 11 PAHs (NAP, ANT, FLA, PYR, BaA, CHR, BbF, BkF, BaP, IPY, and DBA) in the study site require further remediation efforts in terms of their unacceptable non-carcinogenic and carcinogenic risk. The results of risk source analysis reveal that soil media is the main risk pathway as compared with other exposure pathways. It can be seen that remediation process for soil contamination in the study site is urgently demanded. The assessment results demonstrate that the developed IDMHRA approach provides an effective tool for decision-makers and environmental managers to make remediation decisions in contaminated sites.     

Glutathione transferase pi class 2 (GSTp2) protects against the cardiac deformities caused by exposure to PAHs but not PCB-126 in zebrafish embryos

Glutathione transferases (GSTs) are phase II enzymes that detoxify a wide range of toxicants and reactive intermediates. One such class of toxicants is the ubiquitous polycyclic aromatic hydrocarbons (PAHs). Certain PAHs are known to cause developmental cardiac toxicity in fish. Herein, we explored the role of GST pi class 2 (GSTp2) in PAH- and PCB-induced cardiac toxicity in zebrafish (Danio rerio) embryos. We measured expression of GSTp2 in embryos exposed to individual and co-exposures of the PAHs benzo[k]fluoranthene (BkF), benzo[a]pyrene (BaP), and fluoranthene (FL) as well as 3,3',4,4',5-pentachlorobiphenyl (PCB-126). GSTp2 mRNA expression was induced by exposure to BkF, BaP, PCB-126, and BaP+FL and BkF+FL co-exposure. A splice junction morpholino was then used to knockdown GSTp2 in developing zebrafish. GSTp2 knockdown exacerbated the toxicity caused by co-exposures to BkF+FL and BaP+FL. However, GSTp2 knockdown did not affect PCB-126 toxicity. These results further suggest that pi class GSTs serve a protective function against the synergistic toxicity caused by PAHs in developing zebrafish.     

长江口南支表层沉积物中多环芳烃分布特征及生态风险

2008年5月和8月先后2次采集长江口南支表层沉积物样品,采用高效液相色谱进行多环芳烃测定,研究其分布、来源与生态风险。结果表明:长江口南支表层沉积物中PAHs总量在8.9~312.2ng.g-1;PAHs组成以芘、菲、苯并[b]荧蒽、苯并[a]蒽、苯并[a]芘为主,各站芘的含量均最高,本研究PAHs总含量与长江口、黄河口和鸭绿江口近期的调查数据相近,但明显低于珠江口和闽江口数据,以及长江口潮滩沉积物中PAHs数据;PAHs环数组成以中、高环为主,表明长江口南支PAHs主要来源于相对高温条件下不完全燃烧过程。采用平均效应中值商法评价长江口南支PAHs生态风险结果表明,调查区域PAHs产生生态风险的概率较小(<10%)。     

Estimation of Toxicity Equivalency and Probabilistic Health Risk on Lifetime Daily Intake of Polycyclic Aromatic Hydrocarbons from Urban Residential Soils

In this study, toxicity equivalents and health risks, based on concentration of 16 priority polycyclic aromatic hydrocarbons (PAHs) in urban residential soils were estimated for the human population in Gwalior, India. Benzo(a)pyrene total potency equivalents (BaP TPE) were estimated for assessment of human health risk from direct contact with PAH-contaminated soil. Potential risk to contaminated groundwater from leaching of carcinogenic PAHs was assessed by estimating the index of additive cancer risk (IACR). On the basis of lifetime average daily intake of 16 PAHs through ingestion of PAH-contaminated soils, lifetime cancer risk to human adults and children was estimated. The concentration of probable human carcinogenic PAHs in soils accounted for 38% of ∑16PAHs. BaP TPE and index of additive cancer risk (IACR) were lower than guideline values of 0.6 mg kg^?1 and <1, respectively. Estimated lifetime average daily intakes of PAHs via soil ingestion were lower than recommended dose. However, the ILCR for human adults was within acceptable limits recommended by regulatory agencies, but may need action for children in Gwalior, India.     

Sensitive biomarker of polycyclic aromatic hydrocarbons (PAHs): urinary 1-hydroxyprene glucuronide in relation to smoking and low ambient levels of exposure.

The study was conducted in a Chinese population with occupational or environmental exposures to polycyclic aromatic hydrocarbons (PAHs). A total of 106 subjects were recruited from coke-oven workers (workers), residents in a metropolitan area (residents) and suburban gardeners (gardeners). All subjects were monitored twice for their personal exposures to PAHs. The biological samples were collected for measurements of 1-hydroxypyrene (1-OHP) and cotinine in urine. The geometric means of personal exposure levels of pyrene, benz(a)anthracene (BaA) and benzo(a)pyrene (BaP) in workers were 1.470, 0.978 and 0.805 microg m-3, respectively. The corresponding levels in residents were 0.050, 0.034 and 0.025 microg m-3; and those in gardeners were 0.011, 0.020 and 0.008 microg m-3, respectively. The conjugate of 1-OHP with glucuronide (1-OHP-G) is the predominant form of pyrene metabolite in urine and it showed strong associations with exposures not only to pyrene, but also to BaA, BaP and total PAHs. Most importantly, a significant difference in 1-OHP-G was even detected between the subgroups with exposures to BaP at < 0.010 and > 0.010 but < 0.020 microg m-3, suggesting that 1-OHP-G is a good marker that can be used for the risk assessment of BaP exposure at levels currently encountered in ambient air. Furthermore, multiple regression analyses of 1-OHP-G on PAHs exposure indicated that cigarette smoke was a major confounding factor and should be considered and adjusted for while using 1-OHP to estimate PAHs exposure.     

Applicability of the black slug Arion ater for monitoring exposure to polycyclic aromatic hydrocarbons and their subsequent bioactivation into DNA binding metabolites

The applicability of terrestrial black slugs Arion ater (Mollusca, Gastropoda) was studied for biomonitoring environmental exposure to polycyclic aromatic hydrocarbons (PAHs). In laboratory experiments, slugs were orally exposed to benzo[a]pyrene (BaP) for a short term (3 days) or a long term (119 days) period. Test animals were collected in the field, or were reared under laboratory conditions to ensure that they had no history of PAH-exposure. Benzo[a]pyrene hydroxylase (BPH) activity was measured in the digestive gland as a biomarker for BaP exposure. Bulky DNA adduct formation in kidney was measured as an effect biomarker for BaP bioactivation into DNA-binding metabolites. Although success of clutching was relatively low (5 out of 18 slugs produced egg packages), sufficient number of slugs were obtained to perform exposure experiments due to high hatching (89%) and survival rates (79%). After a short exposure to a relatively high BaP doses of 20 and 200 microg/g fresh feed, a dose-dependent and significant increase of BPH activity and bulky DNA adduct levels could be demonstrated in A. ater. Induction factors were low (two times control level), but optimization of the test conditions yielded a higher BPH induction factor of 4.8 times control level. BPH activity and bulky DNA adduct levels, however, did not increase after a long-term exposure to environmentally relevant BaP doses (upto 0.25 microg/g fresh feed). Based on this lack of response after realistic exposure it is concluded that A. ater is not sensitive to BaP exposure and, therefore, not suitable for monitoring environmental exposure to PAHs.     

Health risk assessment of atmospheric polycyclic aromatic hydrocarbons over the Central Himalayas

Carcinogenic risk assessments of polycyclic aromatic hydrocarbons (PAHs) in four sites from the Central Himalayas (Bode, Lumbini, Pokhara, and Dhunche) were performed. Lifetime Average Daily Dose (LADD), Lifetime lung cancer risk (LLCR) and Incremental lifetime cancer risk (ILCR) were calculated in order to evaluate the cancer risk. PAHs levels were converted to BaP equivalent concentrations (B[a]Peq), and models of health risk assessment were applied. B[a]Peq concentrations exceeded the standard limited value (1 ng/m³) in all the four sites. The human health risk assessment (HHRA) demonstrated high carcinogenic risk on residents of Bode and Lumbini. Further, LLCR in all sites were over the acceptable range (1.15E-03, 7.90E-04, 1.40E-04 and 9.96E-05, respectively); however, ILCR ranking exhibited acceptable range in Lumbini, Pokhara, and Dhunche (7.10E-06, 1.26E-06, and 8.95E-07). The risk variation among the sites is due to the difference in pollution status. The study shows health risk due to atmospheric PAHs via inhalation prevails all the seasons throughout, differing only seasonally; nevertheless, the concentration and carcinogenic risk decreased remarkably from south-north transect of the central Himalaya. Keeping some uncertainties aside, this study provides noble insights and helps to formulate new advance assessment on the carcinogenic risk of atmospheric PAHs over the Central Himalayas.     

PAHs and their Carcinogenic Potencies in Diesel Fuel and Diesel Generator Exhaust

The PAH profile was characterized in diesel fuel samples collected from different service stations in Agra (India) by using a gas chromatograph equipped with a flame ionization detector (FID). The low molecular weight PAHs were predominant, ranging from 4.4 × 10² to 1.7 × 10³ mg l^{? 1} in fuel. Exhaust emissions from a diesel generator and a four-stroke engine (Skoda) powered by these fuels were monitored by a stack sampler and quantified for PAHs. The high molecular weight PAHs (DbA+IP, BghiP, and BaP, BbF+BkF) were the dominant PAHs in exhaust emissions. Differences in PAH emission factors for the two engines were found and these differences could be related to the combustion conditions affecting the temperature of flue gas. Emission factors and output/input ratio for individual PAHs suggest that the low molecular weight compounds in the fuel contribute to pyrosynthesis of high molecular weight in exhaust. Unburnt fuel partially contributes to low molecular weight PAHs in exhaust. Further, the relative carcinogenic contributions of each compound in the fuel and exhaust were calculated using the TEF approach. DbA + IP and BaP were significant contributors to the carcinogenicity of the PAH mixture in the exhaust.     

Optimization of PAHs Oxidation from a Concentrate of Soil Attrition Using Potassium Permanganate

The treatment of soils contaminated with organic compounds, such as polycyclic aromatic hydrocarbons (PAHs), by attrition produced large amounts of highly concentrated attrition sludge (PAH – attrition concentrate – PAC). This paper studied the performance of an oxidation process using potassium permanganate (KMnO₄) to degrade PAHs that were initially present in attrition concentrates. The influence of operating conditions (temperature, concentration of KMnO₄ and reaction time) was studied, and these parameters were optimized using a response surface methodology (RSM). The results showed that the temperature and the reaction time had a significant and positive effect on the degradation of PAHs for the experimental domain studied (temperature between 20 and 60°C and reaction time between 1 and 7 h). The interaction between the temperature and the concentration of KMnO₄ significantly influenced the degradation of the PAHs. The temperature and the concentration of KMnO₄ were the main parameters that influenced the degradation of both phenanthrene (Phe) and benzo [a] pyrene (BaP). For benzo [a] anthracene (BaA), the temperature was the most influential factor. According to our results, the optimal conditions were defined as [KMnO₄] = 0.4 M for 5.5 h at 60°C. These optimal conditions led to degradations of 42.9%, 40.8%, 41.0% and 46.0% of the total PAHs, Phe, BaA and BaP, respectively.     

Embryolethality and induction of 7-ethoxyresorufin O-deethylase in chick embryos by polychlorinated biphenyls and polycyclic aromatic hydrocarbons having Ah receptor affinity.

The lethality and 7-ethoxyresorufin O-deethylase (EROD)-inducing potency of some individual polycyclic aromatic hydrocarbons (PAHs) and coplanar polychlorinated biphenyls (PCBs) in chick embryos were measured in order to compare the mechanisms of action of these compounds. In previous studies it was found that coplanar PCBs and certain PAHs have a high embryolethality in the chicken and that they induce embryonic EROD activity. Although the most potent PAHs were almost as embryolethal as the PCBs when injected into hens' eggs 72 h prior to measurement, they were considerably less potent EROD inducers. In the present study, three coplanar PCBs (3,3',4,4'-tetrachlorobiphenyl (TCB), 3,3',4,4',5-pentachlorobiphenyl (PeCB) and 3,3',4,4',5,5'-hexachlorobiphenyl (HCB)) and four of the most toxic PAHs (benzo[a]anthracene (BaA), benzo[k]fluoranthene (BkF), indeno[1,2,3-cd]pyrene (IP) and dibenzo[a, h]-anthracene (DBahA] were administered to chick embryos in different ways, including co-administration. Additive embryolethality was found when BkF and PeCB were co-administered as well as when BaA and DBahA were given simultaneously. The PAHs were more effective as EROD inducers when injected on day 9 (24 h prior to measurement) than when injected on day 7 (72 h prior to measurement). The opposite was found for PeCB and HCB, whereas no difference in potency was noted when comparing TCB injected 24 and 72 h before EROD determination. These substance-related differences were probably due, at least partly, to differences in biotransformation rates. EROD activities found after treatment with high doses of BkF, IP, or DBahA on day 9 were similar to those measured after treatment with PeCB in doses high enough to give maximal induction. Co-administration of high doses of BkF and PeCB did not further increase the activity, indicating that the PAHs and coplanar PCBs induce EROD to a common maximal value. To decrease the influence of metabolization of the PAHs on their EROD-inducing potency, EROD was determined early in development (day 8) and soon after treatment (24 h) in one experiment. In that experiment, the PAHs proved to be only a few times less potent EROD inducers in relation to their embryolethalities compared with the PCBs. The results of the present study, a previously observed similarity in pathology between chick embryos treated with PAHs and embryos treated with coplanar PCBs, and the fact that the most toxic PAHs also are the most avid Ah receptor binders suggest that the coplanar PCBs and the PAHs largely exert their toxicity in chick embryos via an Ah receptor-mediated mechanism. The differences between the compounds in their EROD-inducing potency/embryolethality ratios could probably be explained by their different rates of biotransformation.     

Sources of PAHs to Sediments of the Elizabeth River,VA

Sediments collected from the Elizabeth River, VA, a highly contaminated subestu-ary of the James River, were analyzed for polycyclic aromatic hydrocarbons (PAHs). Select isomer ratios (BbF/BkF, BaA/chrysene, and IP/BghiP) and molecular weight fractions (ΣPAH_202/202-276 and ΣPAH_252/202-276) were identified as source indicators for two former wood-treatment facilities (Atlantic Wood and Eppinger & Russell) located on the southern branch of the Elizabeth River. These facilities are suspected as probable contributors to the high PAH contamination in sediments. Plots of the wood-treatment source indicators, along with those for coal, wood, and automotives, revealed a likely contribution from only one of the former wood-treatment facilities, in addition to the possible contribution of coal/coal gasification to PAH contamination in sediments of the main stem and southern branch of the Elizabeth River. By examining PAH isomer ratios from known or suspected sources, it is possible to distinguish multiple sources of PAHs to an ecosystem.     

Solar-simulated light-exposed benzo[a]pyrene induces phosphorylation of histone H2AX

Polycyclic aromatic hydrocarbons (PAHs), wide-spread mutagenic and carcinogenic environmental pollutants, are consistently exposed to sunlight in the environment. The exposure causes structural change, resulting in the generation of a variety of photomodified products having different bioactivities compared with the parent compounds. In this study, we found that benzo[a]pyrene (BaP) exposed to solar-simulated light (SSL)-induced phosphorylation of histone H2AX (gamma-H2AX), which was recently identified as an early event after the induction of DNA double strand breaks (DSBs). Although BaP itself did not produce gamma-H2AX, SSL-exposed BaP significantly generated gamma-H2AX depending on the period of exposure. Furthermore, we revealed that reactive oxygen species produced by the SSL-exposed BaP mainly contributed to the generation of gamma-H2AX. The appearance of gamma-H2AX means the induction of the most serious form of DNA damage, DSBs, suggesting the potential risk of carcinogenesis.     

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.     

Photomutagenicity of 16 polycyclic aromatic hydrocarbons from the US EPA priority pollutant list

The photomutagenicity of 16 polycyclic aromatic hydrocarbons (PAHs), all on the United States Environmental Protection Agency (US EPA) priority pollutant list, was studied. Concomitant exposing the Salmonella typhimurium bacteria strain TA102 to one of the PAHs and light (1.1 J/cm2 UVA+2.1 J/cm2 visible) without the activation enzyme S9, strong photomutagenic response is observed for anthracene, benz[a]anthracene, benzo[ghi]perylene, benzo[a]pyrene, indeno[1,2,3-cd]pyrene, and pyrene. Under the same conditions, acenaphthene, acenaphthylene, benzo[k]fluoranthene, chrysene, and fluorene are weakly photomutagenic. Benzo[b]fluoranthene, fluoranthene, naphthalene, phenanthrene, and dibenz[a,h]anthracene are not photomutagenic. These results indicate that PAHs can be activated by light and become mutagenic in Salmonella TA102 bacteria. At the same time, the mutagenicity for all the 16 PAHs was examined with the standard mutagenicity test with 10% S9 as the activation system. Benzo[b]fluoranthene, benzo[k]fluoranthene, chrysene, acenaphthylene, and fluorene are weakly mutagenic, while the rest of the PAHs are not. In general, the photomutagenicity of PAHs in TA102 does not correlate with their S9-activated mutagenicity in either TA102 or TA98/TA100 since they involve different activation mechanisms.     

Benzo[a]pyrene exposed to solar-simulated light inhibits apoptosis and augments carcinogenicity

Polycyclic aromatic hydrocarbons (PAHs) such as benzo[a]pyrene (BaP) are widespread environmental pollutants and several lines of experimental evidence have suggested a role in carcinogenesis. PAHs in the environment are exposed to sunlight and photomodified PAHs have been detected in contaminated sediment and air particulate matter; however, the carcinogenicity of photomodified PAHs is not well understood. In this study, we found that solar-simulated light-irradiated BaP (LBaP) inhibited apoptosis, leading to cancer. LBaP suppressed apoptosis induced by cell detachment and serum depletion in a dose and light-irradiated time-dependent manner. The antiapoptotic effect was related to the production of reactive oxygen species from degraded BaP. The cells that survived apoptosis by LBaP treatment were transformed having the ability to form colonies in soft agar and tumors in nude mice. These capabilities were specific to LBaP, not BaP itself. The results suggested that the carcinogenicity of PAHs may be attributable not only to the genetic damage induced by their metabolites, but also to the antiapoptotic effects of oxidative products on exposure to sunlight.     

污染土壤中苯并(a)芘的微生物降解途径研究进展

苯并(a)芘(BaP)是一种具有强致癌、致畸和致突变的多环芳烃(PAHs)。为了修复BaP污染的土壤,探索其降解途径是很重要的。为此,综述了国内外有关污染土壤中苯并(a)芘的微生物降解情况,对不同真菌、细菌降解苯并(a)芘的能力、代谢途径、共代谢底物以及环境影响因素进行了介绍和比较,提出了苯并(a)芘中间代谢产物的累积及其环境毒性方面的研究是修复苯并(a)芘污染土壤的重要方向。     

BIODEGRADATION OF PAHS IN LONG-TERM CONTAMINATED SOIL CULTIVATED WITH EUROPEAN WHITE BIRCH (BETULA PENDULA) AND RED MULBERRY (MORUS RUBRA) TREE

The ability of birch (Betula pendula) and mulberry (Morus rubra), cultivated either separately or together with perennial ryegrass (Lolium perenne), to enhance the biodegradation of 15 selected polycyclic aromatic hydrocarbons (PAHs) in long-term contaminated soil was studied in a greenhouse experiment. The microecosystems (MESs) were cultivated for either 12 or 18 months at a natural photoperiod. The fact that the soil chosen for cultivation had been contaminated for over 50 years was expected to be the main factor limiting biodegradation. Extracts of both planted and unplanted soil were analyzed using HPLC. After 1 year of cultivation, the overall content of the investigated compounds had declined to 50%. The concentrations of fluoranthene and pyrene, the PAHs originally present in the soil in the highest concentrations (103.5 and 83.3 mg/kg, respectively), had decreased to 28.0 and 18.0 mg/kg, respectively. In addition, other compounds were successfully degraded, including even benzo[a]pyrene. Benzo[ghi]perylene and indeno[1,2,3-cd]pyrene were the only PAHs remaining and were almost entirely undegraded. Because few significant differences were found between the various types of MESs studied, degradation can primarily be attributed to the presence of degrading microorganisms in the soil.     

Survival and mutagenesis of bacterial plasmids with localized carcinogen adducts

Induction of 6-thioguanine (TG) resistance by chemical mutagens was examined in a line of cells derived from a human epithelial teratocarcinoma cell clone. The cells, designated as P3 cells, have a stable diploid karyotype with 46(XX) chromosomes, including a translocation between chromosomes 15 and 20. Efficient recovery of TG-resistant mutants induced by the direct-acting mutagens: N-methyl-N'-nitro-N-nitrosoguanidine (MNNG); 7 beta, 8 alpha-dihydroxy-9 alpha, 10 alpha-epoxy-7,8,9,10 -tetrahydrobenzo[a]pyrene (BPDE); and benzo[a]pyrene (B[a]P); activated in a cell-mediated assay, required an expression time of 7 days and a saturation density of 2 X 10(4) cells/60-mm petri dish. The TG-resistant mutant cells induced by MNNG and BPDE maintained their resistant phenotype 4-6 weeks after isolation. This mutant phenotype was associated with a more than 10-fold reduction in hypoxanthine-guanine phosphoribosyl transferase (HGPRT) activity relative to that of the parental P3 cell line, which was shown to catalyze the formation of 4.6 pmoles inosine-5'-monophosphate (IMP)/min/microgram protein. Induction of TG resistance was also observed in P3 cells cocultivated in a cell-mediated assay with human breast carcinoma cells, which are capable of polycyclic aromatic hydrocarbon (PAH) metabolism, after treatment with the carcinogenic PAHs: B[a]P, chrysene, 7,12-dimethylbenz[a]anthracene (DMBA), and 3-methylcholanthrene (MCA). The degree of mutant induction in this assay was related to the carcinogenic potency of these PAHs in experimental animals. The most potent mutagen was DMBA, followed in decreasing order by MCA, B[a]P, and chrysene. DMBA, at 0.4 microM, increased the frequency of mutants for TG resistance from 2 for the control to about 200 TG-resistant mutants/10(6) colony-forming cells (CFC). Benzo[e]pyrene (B[e]P) and pyrene, which are not carcinogenic, were not effective in the assay. None of the PAHs was mutagenic in the P3 cells cultivated in the absence of the PAH-metabolizing cells. These results indicate that the P3 cells can be useful for the study of mutagenesis at the HGPRT locus by direct-acting chemical mutagens, as well as by chemicals activated in a cell-mediated assay.