Effect of a peri fluoro substituent on the conformation of dihydrodiol derivatives of polycyclic aromatic hydrocarbons

$\text{Trans}$-3,4-, 5,6-, 8,9-, and 10,11-dihydrodiols formed from the metabolism of 7-fluorobenz[a]anthracene by rat liver microsomes were isolated by reversed-phase high performance liquid chromatography. Ultraviolet absorption, mass, and NMR spectral analyses indicated that the 5,6- and 8,9-dihydrodiols were preferentially in quasi-diaxial conformations, whereas the 3,4- and 10,11-dihydrodiols were preferentially in quasi-diequatorial conformations. CPK space-filling models suggest that the quasi-diaxial conformation is primarily the result of electronic repulsion between the fluorine and the $\text{peri}$ hydroxyl oxygen. These findings provide a structural basis in the interpretation of the carcinogenic potencies of some fluorinated polycyclic aromatic hydrocarbons.     

Mutational spectra for polycyclic aromatic hydrocarbons in the supF target gene

An SV40-based shuttle vector system was used to identify the types of mutational changes and the sites of mutation within the supF DNA sequence generated by the four stereoisomers of benzo[c]phenanthrene 3,4-dihydrodiol 1,2-epoxide (B[c]PhDE), by racemic mixtures of bay or fjord region dihydrodiol epoxides (DE) of 5-methylchrysene, of 5,6-dimethylchrysene, of benzo[g]chrysene and of 7-methylbenz[a]anthracene and by two direct acting polycyclic aromatic hydrocarbon carcinogens, 7-bromomethylbenz[a]anthracene (7-BrMeBA) and 7-bromomethyl-12-methylbenz[a]anthracene (7-BrMe-12-MeBA). The results of these studies demonstrated that the predominant type of mutation induced by these compounds is the base substitution. The chemical preference for reaction at deoxyadenosine (dAdo) or deoxyguanosine (dGuo) residues in DNA, which is in general correlated with the spatial structure (planar or non-planar) of the reactive polycyclic aromatic hydrocarbon, is reflected in the preference for mutation at AT or GC pairs. In addition, if the ability to react with DNA in vivo is taken into account, the relative mutagenic potencies of the B[c]PhDE stereoisomers are consistent with the higher tumorigenic activity associated with non-planar polycyclic aromatic hydrocarbons and their extensive reaction with dAdo residues in DNA. Comparison of the types of mutations generated by polycyclic aromatic hydrocarbons and other bulky carcinogens in this shuttle vector system suggests that all bulky lesions may be processed by a similar mechanism related to that involved in replication past apurinic sites. However, inspection of the distribution of mutations over the target gene induced by the different compounds demonstrated that individual polycyclic aromatic hydrocarbons induce unique patterns of mutational hotspots within the target gene. A polymerase arrest assay was used to determine the sequence specificity of the interaction of reactive polycyclic aromatic hydrocarbons with the shuttle vector DNA. The results of these assays revealed a divergence between mutational hotspots and polymerase arrest sites for all compounds investigated, i.e., sites of mutational hotspots do not correspond to sites where high levels of adduct formation occur, and suggested that some association between specific adducts and sequence context may be required to constitute a premutagenic lesion. A site-specific mutagenesis system employing a single-stranded vector (M13mp7L2) was used to investigate the mutational events a single benzo[a]pyrene or benzo[c]phenanthrene dihydrodiol epoxide–DNA adduct elicits within specific sequence contexts. These studies showed that sequence context can cause striking differences in mutagenic frequencies for given adducts. In addition, these sequence context effects do not originate only from nucleotides immediately adjacent to the adduct, but are also modulated by more distal nucleotides. The implications of these results for mechanisms of polycyclic aromatic hydrocarbon-induced mutagenesis and carcinogenesis are discussed.     

The effect of the bay-region 12-methyl group on the stereoselective metabolism at the K-region of 7,12-dimethylbenz[a]anthracene by rat liver microsomes.

The enantiomers of a trans-5,6-dihydrodiol formed in the metabolism of 7,12-dimethylbenz[a]anthracene by rat liver microsomes (microsomal fractions) were resolved by chiral stationary-phase high-performance liquid chromatography. The major 7,12-dimethylbenz[a]anthracene trans-5,6-dihydrodiol enantiomer and its hydrogenation product 5,6,8,9,10,11-hexahydro-trans-5,6-diol were found to have 5S,6S absolute configurations by the exciton chirality c.d. method. The R,R/S,S enantiomer ratios of 7,12-dimethylbenz[a]anthracene trans-5,6-dihydrodiol formed in the metabolism of 7,12-dimethylbenz[a]anthracene by liver microsomes from untreated, 3-methylcholanthrene-treated and phenobarbital-treated male Sprague-Dawley rats were found to be 11:89, 6:94, and 5:95 respectively. These findings and those reported previously on the metabolic formations of trans-5,6-dihydrodiols from 7-methylbenz[a]anthracene and 12-methylbenz[a]anthracene suggest that the 12-methyl group in 7,12-dimethylbenz[a]anthracene plays an important role in determining the stereoselective metabolism at the K-region 5,6-double bond. Furthermore, the finding that formation of 5S,6S-dihydrodiol as the predominant enantiomer was not significantly affected by the isoenzymic composition of cytochrome P-450 present in microsomes prepared from the livers of the rats pretreated with the different inducing agents indicates that the stereoselectivity depends on the substrate metabolized rather than on the precise nature of the metabolizing-enzyme system.     

Metabolite repression inhibits degradation of benzo[a]pyrene and dibenz[a,h]anthracene by Stenotrophomonas maltophilia VUN 10,003

Large inocula of Stenotrophomonas maltophilia VUN 10,003 were used to investigate bacterial degradation of benzo[a]pyrene and dibenz[a,h]anthracene. Although strain VUN 10,003 was capable of degrading 10–15 mg l⁻¹ of the five-ring compounds in the presence of pyrene after 63 days, further addition of pyrene after degradation of the five-ring polycyclic aromatic hydrocarbons (PAHs) ceased did not stimulate significant decreases in the concentration of benzo[a]pyrene or dibenz[a,h]anthracene. However, pyrene was degraded to undetectable levels 21 days after its addition. The amount of benzo[a]pyrene and dibenz[a,h]anthracene degraded by strain VUN 10,003 was not affected by the initial concentration of the compounds when tested at 25–100 mg l⁻¹, by the accumulation of by-products from pyrene catabolism or a loss of ability by the cells to catabolise benzo[a]pyrene or dibenz[a,h]anthracene. Metabolite or by-product repression was suspected to be responsible for the inhibition: By-products from the degradation of the five-ring compounds inhibited their further degradation. Journal of Industrial Microbiology & Biotechnology (2002) 28, 88–96 DOI: 10.1038/sj/jim/7000216 Received 30 January 2001/ Accepted in revised form 10 October 2001     

Mutagenicity of reactive derivatives of carcinogenic hydrocarbons: evidence of DNA repair

The ability of cellular DNA repair enzymes, which are active on ultraviolet light-induced lesions in DNA, to recognize and repair damage induced in DNA by exposure to carcinogenic polycylic hydrocarbons was investigated and the effect of such repair processes on the mutagenicity of the hydrocarbons determined. The carcinogenic hydrocarbos, 7-bromomethylbenz[a]anthracene (7-BrMeBA) and 7-bromomethyl-12-methylbenz[a]anthracene (7-BrMe-12-MeBA), chosen for this study because they form well characterized, stable products with DNA, were dissolved at various concentrations in acetone, added under mild conditions to biologically active DNA isolated from Bacillus subtilis, and the reaction stopped by ethanol precipitation. The hydrocarbons were determined by specific radioactivity to be covalently linked to DNA at a frequency of from 1–5 per 1000 nucleotides. An increased frequency of bound hydrocarbon molecules was directly correlated with a decrease in the buoyant density of the DNA as measured in analytical CsCl centrifugation studies. The samples of hydrocarbon-bound DNA were tested for survival of biological activity and for the frequency of induced forward mutations in two recipient strains (hcr⁺ and hcr^?) of Bacillus subtilis which differ in their ability to repair ultraviolet light-induced lesions in DNA. The survival of the biological activity was significantly higher in the repairing strain (hcr⁺). A higher frequency of mutations was detected in the repairing strain as well. The loss of transforming activity and the increase in the frequency of mutations (up to 20-fold) was directly proportional to the amount of hydrocarbon bound to the DNA samples. The majority of these mutations proved unable to revert spontaneously. Finally, the ability of highly purified rat liver endonuclease, shown to recognize lesions in UV-irradiated DNA, to recognize such hydrocarbon lesions was investigated. Tritiated 7-BrMeBA-treated DNAs exposed to the enzyme were found to sustain single-strand nicks in proportion to the amount of hydrocarbon bound while untreated DNA remained substantially intact. The action of the endonuclease appeared to result in an increase in the biological activity of DNA containing hydrocarbon residues when this was assayed in the hcr^? mutant.     

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.     

Regio- and stereoselective metabolism of 7,12-dimethylbenz[a]anthracene by Mycobacterium vanbaalenii PYR-1

The degradation of 7,12-dimethylbenz[a]anthracene (DMBA), a carcinogenic polycyclic aromatic hydrocarbon, by cultures of Mycobacterium vanbaalenii PYR-1 was studied. When M. vanbaalenii PYR-1 was grown in the presence of DMBA for 136 h, high-pressure liquid chromatography (HPLC) analysis showed the presence of four ethyl acetate-extractable compounds and unutilized substrate. Characterization of the metabolites by mass and nuclear magnetic resonance spectrometry indicated initial attack at the C-5 and C-6 positions and on the methyl group attached to C-7 of DMBA. The metabolites were identified as cis-5,6-dihydro-5,6-dihydroxy-7,12-dimethylbenz[a]anthracene (DMBA cis-5,6-dihydrodiol), trans-5,6-dihydro-5,6-dihydroxy-7,12-dimethylbenz[a]anthracene (DMBA trans-5,6-dihydrodiol), and 7-hydroxymethyl-12-methylbenz[a]anthracene, suggesting dioxygenation and monooxygenation reactions. Chiral stationary-phase HPLC analysis of the dihydrodiols showed that DMBA cis-5,6-dihydrodiol had 95% 5S,6R and 5% 5R,6S absolute stereochemistry. On the other hand, the DMBA trans-5,6-dihydrodiol was a 100% 5S,6S enantiomer. A minor photooxidation product, 7,12-epidioxy-7,12-dimethylbenz[a]anthracene, was also formed. The results demonstrate that M. vanbaalenii PYR-1 is highly regio- and stereoselective in the degradation of DMBA.     

Stereoselective fungal metabolism of 7,12-dimethylbenz[a]anthracene: identification and enantiomeric resolution of a K-region dihydrodiol

Syncephalastrum racemosum UT-70 and Cunninghamella elegans ATCC 36112 metabolized 7,12-dimethylbenz[a]anthracene (7,12-DMBA) to hydroxymethyl metabolites as well as 7-hydroxymethyl-12-methylbenz[a]anthracene trans-3,4-, -5,6-, -8,9-, and -10,11-dihydrodiols. The 7,12-DMBA metabolites were isolated by reversed-phase high-performance liquid chromatography and identified by their UV-visible absorption, mass, and nuclear magnetic resonance spectral characteristics. A comparison of the circular dichroism spectra of the K-region (5,6-position) dihydrodiol of both fungal strains with those of the 7,12-DMBA 5S,6S-dihydrodiol formed from 7,12-DMBA by rat liver microsomes indicated that the major enantiomer of the 7-hydroxymethyl-12-methylbenz[a]anthracene trans-5,6-dihydrodiol formed by both fungal strains had a 5R,6R absolute stereochemistry. Direct resolution of the fungal trans-5,6-dihydrodiols by chiral stationary-phase high-performance liquid chromatography indicated that the ratios of the R,R and S,S enantiomers were 88:12 and 77:23 for S. racemosum and C. elegans, respectively. These results indicate that the fungal metabolism of 7,12-DMBA at the K region (5,6-position) is highly stereoselective and different from that reported for mammalian enzyme systems.     

Stereoselective fungal metabolism of 7,12-dimethylbenz[a]anthracene: identification and enantiomeric resolution of a K-region dihydrodiol.

Syncephalastrum racemosum UT-70 and Cunninghamella elegans ATCC 36112 metabolized 7,12-dimethylbenz[a]anthracene (7,12-DMBA) to hydroxymethyl metabolites as well as 7-hydroxymethyl-12-methylbenz[a]anthracene trans-3,4-, -5,6-, -8,9-, and -10,11-dihydrodiols. The 7,12-DMBA metabolites were isolated by reversed-phase high-performance liquid chromatography and identified by their UV-visible absorption, mass, and nuclear magnetic resonance spectral characteristics. A comparison of the circular dichroism spectra of the K-region (5,6-position) dihydrodiol of both fungal strains with those of the 7,12-DMBA 5S,6S-dihydrodiol formed from 7,12-DMBA by rat liver microsomes indicated that the major enantiomer of the 7-hydroxymethyl-12-methylbenz[a]anthracene trans-5,6-dihydrodiol formed by both fungal strains had a 5R,6R absolute stereochemistry. Direct resolution of the fungal trans-5,6-dihydrodiols by chiral stationary-phase high-performance liquid chromatography indicated that the ratios of the R,R and S,S enantiomers were 88:12 and 77:23 for S. racemosum and C. elegans, respectively. These results indicate that the fungal metabolism of 7,12-DMBA at the K region (5,6-position) is highly stereoselective and different from that reported for mammalian enzyme systems.     

Degradation of benz[<Emphasis Type="Italic">a</Emphasis>]anthracene by <Emphasis Type="Italic">Mycobacterium vanbaalenii</Emphasis> strain PYR-1

Cultures of Mycobacterium vanbaalenii strain PYR-1 grown in mineral salts medium and nutrients in the presence of benz[a]anthracene metabolized 15% of the added benz[a]anthracene after 12days of incubation. Neutral and acidic ethyl acetate extractable metabolites were isolated and characterized by high performance liquid chromatography (HPLC) and uv–visible absorption, gas chromatography/mass (GC/MS) and nuclear magnetic resonance (NMR) spectral analysis. Trimethylsilylation of the metabolitesfollowed by GC/MS analysis facilitated identification of metabolites. The characterization of metabolites indicated that M. vanbaalenii initiated attack of benz[a]anthracene at the C-1,2-, C-5,6-, C-7,12- and C-10,11-positions to form dihydroxylated and methoxylated intermediates. The major site of enzymatic attack was in the C-10, C-11 positions. Subsequent ortho- and meta-cleavage of each of the aromatic rings led to the accumulation of novel ring-fission metabolites in the medium. The major metabolites identified were 3-hydrobenzo[f]isobenzofuran-1-one (3.2%), 6-hydrofuran[3,4-g]chromene-2,8-dione (1.3%), benzo[g]chromene-2-one (1.7%), naphtho[2,1-g]chromen-10-one (48.1%), 10-hydroxy-11-methoxybenz[a]anthracene (9.3%), and 10,11-dimethoxybenz[a]anthracene (36.4%). Enzymatic attack at the C-7 and C-12 positions resulted in the formation of benz[a]anthracene-7,12-dione, 1-(2-hydroxybenzoyl)-2-naphthoic acid, and 1-benzoyl-2-naphthoic acid. A phenyl-naphthyl metabolite, 3-(2-carboxylphenyl)-2-naphthoic acid, was formed when M. vanbaalenii was incubated with benz[a]anthracene cis-5,6-dihydrodiol, indicating ortho-cleavage of 5,6-dihydroxybenz[a]anthracene. A minor amount of 5,6-dimethoxybenz[a]anthracene was also formed. The data extend and propose novel pathways for the bacterial metabolism of benz[a]anthracene.     

Comparative carcinogenicity of picene and dibenz[a,h]anthracene in the rat.

Early carcinogenicity tests found no evidence of activity for picene but found considerable initiating and carcinogenic activity for dibenz[a,h]anthracene (DBA). More recent investigation suggested that both pentacyclics were complete carcinogens when administered as single sc injections in NMRI mice, despite findings that picene acted as neither an initiating nor promoting agent. To investigate this contradiction, the complete carcinogenicities of both isomers were compared by sc injection in female Sprague-Dawley rats. The results demonstrate that 1 micromol of DBA, administered three times weekly for 20 doses, induces sarcomas in all test animals by 33 weeks (100%). Similar treatment with picene did not induce sarcoma in any test animals by 37 weeks (0%). The present results agree with the earlier studies. It follows from these results that the predictions of the unified theory for the appearance of carcinogenic properties following administration of picene and dibenz[a,h]anthracene to test animals have been confirmed.     

Cytochrome P-450-catalyzed stereoselective epoxidation at the K region of benz[a]anthracene and benzo[a]pyrene

The enantiomers of K-region benz[a]anthracene (BA) 5,6-epoxide and benzo[a]pyrene (BP) 4,5-epoxide were resolved by chiral stationary-phase high-performance liquid chromatography (CSP-HPLC). The K-region epoxides formed in the metabolism of BA by liver microsomes from untreated (control), phenobarbital (PB)-treated, and 3-methylcholanthrene (MC)-treated male Sprague-Dawley rats were determined by CSP-HPLC to have a 5R,6S/5S,6R enantiomer ratio of 25:75, 21:79, and 4:96, respectively. The K-region 4,5-epoxide formed in the metabolism of BP by the same rat liver microsomal preparations contained a 4R,5S/4S,5R enantiomer ratio of 48:52 (control), 40:60 (PB), and 5:95 (MC), respectively. The results indicate that various cytochrome P-450 isozymes of rat liver exhibit different stereoselective properties in catalyzing the epoxidation reactions at the K region of BA and of BP.     

Microbial metabolism and detoxification of 7,12-dimethylbenz[a]anthracene

Summary Six strains of fungi grown on Sabouraud dextrose broth in the presence of 7,12-dimethylbenz[a]anthracene (DMBA) were surveyed for their ability to metabolize DMBA. Experiments with [¹⁴C]DMBA indicated that the extent of formation of organic-soluble metabolites ranged from 6 to 28% after 5 days of incubation, depending on the organism tested. The yields of water-soluble metabolites also varied, and ranged from 1 to 33% after 5 days.Cunninghamella elegans ATCC 36112 andSyncephalastrum racemosum UT-70 exhibited the highest DMBA-metabolizing activity among the organisms surveyed.S. racemosum metabolized DMBA primarily to 7-hydroxymethyl-12-methylbenz[a]anthracene (7-OHM-12-MBA)_ and 7,12-dihydroxymethylbenz[a]anthracene (7,12-diOHMBA). Minor metabolites included 7-OHM-12-MBA-trans-5,6-, 8,9- and 10,11-dihydrodiols, and glucuronide and sulfate conjugates of phenolic derivatives of DMBA. In contrast, the major DMBA metabolites produced byC. elegans were water-soluble. The predominant organic-soluble metabolites produced byC. elegans included 7-OHM-12-MBA-trans-5,6-, 8,9- and 10,11-dihydrodiols. DMBA-trans-3,4-dihydrodiol was also detected. Circular dichroism spectral analysis revealed that the major enantiomer of the 7-OHM-12-MBA-trans-8,9-dihydrodiol formed by each organism has anS,S absolute configuration, while the major enantiomers of the 5,6-, 10,11- and 3,4-dihydrodiols had anR,R configuration. The mutagenic activity of extracts fromS. racemosum exposed to DMBA were determined inSalmonella typhimurium TA98. The mutagenicity of DMBA decreased by 36% over a period of 5 days as 33% of the compound was metabolized. Comparison of these results with previously reported results in mammalian systems suggests that there are similarities and differences between the fungal and mammalian oxidation of DMBA and that the overall balance of fungal metabolism is towards a detoxification rather than a bioactivation pathway.     

Separation of multiple forms of protein-bound metabolites of the carcinogenic hydrocarbons 3-methylcholanthrene and 7,12-dimethylbenz[a]anthracene from several rodent species

Our findings demonstrate that the carcinogenic hydrocarbons 7,12-dimethylbenz[a] anthracene (DMBA) and 3-methylcholanthrene (3-MCA) bind in multiple forms to the proteins of skin and lung tissue. These metabolites are freed from the proteins by treatment with Raney nickel, thus, the metabolites are most likely bound through cysteine or homocysteine. The numbers and the relative quantities of the bound metabolites vary greatly among the Fischer rat, the Syrian golden hamster, and 3 mouse strains. It is possible that the metabolites (which indicate a particular pathway of metabolic activation) correlate with species susceptibility to hydrocarbon carcinogenesis.     

Absolute configuration of the 5,6-oxide formed from 7,12-dimethylbenz[a]anthracene by cytochrome P450c

The absolute configurations of the enantiomeric 5,6-arene oxides of 7,12-dimethylbenz[a]anthracene (DMBA) were recently assigned such that the late eluting enantiomer from a chiral HPLC column has 5R,6S absolute configuration. [Mushtaq et al. (1984) BBRC 125, 539]. The authors further concluded that the 5R,6S-enantiomer predominates on metabolism of DMBA by cytochrome P450c in liver microsomes from 3-methylcholanthrene-treated rats. Their chemical assignment of absolute configuration is incorrect. Thus, metabolism of DMBA by these microsomes as well as by homogeneous cytochrome P450c produces 5,6-oxide highly enriched (95%) in the 5S,6R-enantiomer in accord with theoretical predictions.     

Non-enzymatic and microsome-dependent binding of polycyclic hydrocarbons to DNA and polynucleotides

The binding of tritium-labelled 7,12-dimethylbenz[a]anthracene (DMBA), benzo[a]pyrene (BP) and 3-methylcholanthrene (MCA) to DNA or polynucleotides in vitro was re-examined both in the presence and in the absence of rat liver or human placental microsomes.A high level of non-enzymatic binding was evident when thymus DNA was used as acceptor. This non-enzymatic binding made it difficult to determine the effect of microsomes, except in the case of BP when induced rat microsomes were used. Better results were obtained using polynucleotides: a definite microsome-dependent binding occurred between all the polynucleotides and all the hydrocarbons tested.No clear evidence of binding catalysed by microsomes from human placenta was found except in polynucleotide-BP interactions: further studies are required to completely evaluate the ability of such nucleic acid-microsomal system for testing in vitro possible oncogenic substances in animals and humans.     

Differential composition of bacterial communities as influenced by phenanthrene and dibenzo[a,h]anthracene in the rhizosphere of ryegrass (Lolium perenne L.)

Bioremediation technologies of Polycyclic Aromatic Hydrocarbons (PAH) are often limited by the recalcitrance to biodegradation of high molecular weight (HMW) PAH. Rhizosphere is known to increase the biodegradation of PAH but little is known about the biodegradability of these HMW compounds by␣rhizosphere bacteria. This study compared the effects of a 3 and a 5-ring PAH, phenanthrene (PHE) and␣dibenzo[a,h]anthracene (dBA) respectively, on the composition of bacterial community, the bacterial density and the biodegradation activity. Compartmentalized devices were designed to harvest three consecutive sections of the rhizosphere. Rhizosphere and non-rhizosphere compartments were filled with PHE or dBA spiked or unspiked sand and inoculated with a soil bacterial inoculum. Different bacterial communities and degradation values were found 5 weeks after spiking with PHE (41–76% biodegradation) and dBA (12–51% biodegradation). In sections closer to the root surface, bacterial populations differed as a function of the distance to roots and the PAH added, whereas in further rhizosphere sections, communities were closer to those of the non-planted treatments. Biodegradation of PHE was also a function of the distance to roots, and decreased from 76 to 42% within 9 mm from the roots. However, biodegradation of dBA was significantly higher in the middle section (3–6 mm from roots) than the others. Rhizosphere degradation of PAH varies with the nature of the PAH, and C fluxes from roots could limit the degradation of dBA.     

二甲基苯蒽对小鼠皮肤表皮鸟氨酸脱羧酶和转化生长因子βmRNA水平的影响

本文利用Ｎｏｒｔｈｅｒｎ印迹分析技术研究了完全致癌物二甲基苯蒽（ＤＭＢＡ）对小鼠表皮鸟氨酸脱羧酶（ＯＤＣ）ｍＲＮＡ和转化生长因子β（ＴＧＦ－β）ｍＲＮＡ水平的影响。ＤＭＢＡ在１５μｇ和９００μｇ剂量下一次涂用于小鼠皮肤,可使表皮ＯＤＣｍＲＮＡ和ＴＧＦ－βｍＲＮＡ表达增加。ＯＤＣｍＲＮＡ为单一的２．０ｋｂ大小的条带,其表达在在３６ｈ时最为明显。而ＴＧＦ－βｍＲＮＡ大小为２．５ｋｂ和１．９ｋｂ,其表达在３６ｈ时最高,到４８ｈ几乎降至正常,但在７２ｈ又有增加。ＯＤＣ和ＴＧＦ－β可能在ＤＭＢＡ诱癌过程中起重要作用。     

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.