A benzo[a]pyrene -7,8-dihydrodiol-9,10-epoxide is the major metabolite involved in the binding of benzo[a]pyrene to DNA in isolated viable rat hepatocytes

Benzo[a]pyrene is metabolised by isolated viable hepatocytes from both untreated and 3-methylcholanthrene pretreated rats to reactive metabolites which covalently bind to DNA. The DNA from the hepatocytes was isolated, purified and enzymically hydrolysed to deoxyribonucleosides. The hydrocarbon-deoxyribonucleoside products after initial separation, on small columns of Sephadex LH-20, from unhydrolysed DNA, oligonucleotides and free bases, were resolved by high pressure liquid chromatography (HPLC). The qualitative nature of the adducts found in both control and pretreated cells was virtually identical; however pretreatment with 3-methylcholanthrene resulted in a quantitatively higher level of binding. The major hydrocarbon-deoxyribonucleoside adduct, found in hepatocytes co-chromatographed with that obtained following reaction of the diol-epoxide, (±)7α,8β-dihydroxy-9β,10β-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene with DNA. Small amounts of other adducts were also present including a more polar product which co-chromatographed with the major hydrocarbon-deoxyribonucleoside adduct formed following microsomal activation of 9-hydroxybenzo[a]pyrene and subsequent binding to DNA. In contrast to the results with hepatocytes, when microsomes were used to metabolically activate benzo[a]pyrene, the major DNA bound-product co-chromatographed with the more polar adduct formed upon further metabolism of 9-hydroxybenzo[a]pyrene. These results illustrate that great caution must be exercised in the extrapolation of results obtained from short-term mutagenesis test systems, utilising microsomes, to in vivo carcinogenicity studies.     

Sulfate conjugation of benzo[alpha]pyrene metabolites and derivates

Sulfate conjugation of benzo[alpha]pyrene(BP) metabolites and derivatives was studied. The reaction sequence consisted of two steps; activation of sulfate ion to 3'-phosphoadenosine-5'-phosphosulfate and transfer of the activated sulfate to the BP-derivatives. Both reactions were carried out by enzymes located in the rat liver 105 000 g supernatant. The reactions required MgCl2. Phenol and quinone derivatives were generally good substrates for sulfate conjugation and different reactivities were observed with the dihydrodiol derivatives. Sulfate conjugates were more polar than their parent BP-derivatives and except for quinone conjugates were easily extracted with ethyl acetate. The role of sulfate conjugation in BP carcinogenesis is discussed.     

Metabolism and activation of benzo[a]pyrene by mouse and rat skin in short-term organ culture and in vivo

The metabolic activation of BP was examined in mouse and rat skin in vivo and in short-term organ culture. In mouse skin, larger quantities of ether- and water-soluble metabolites were formed and more BP became bound covalently to DNA and protein than in rat skin. Qualitative differences in the formation of dihydrodiol metabolites and of BP-deoxyribonucleoside adducts between mouse and rat skin were also observed. Organ culture techniques may not provide a true model of metabolic activation in vivo because it was found that the covalent binding of BP to DNA and protein was reduced in skin maintained in culture despite an accumulation of dihydrodiol and other ether-soluble metabolites. In addition, the proportions of the syn- and anti-isomers of BP-7,8-diol 9,10-oxide involved in the formation of adducts with deoxyguanosine differed between skin treated in organ culture and in vivo.     

The non-covalent binding of benzo[a]pyrene and its hydroxylated metabolites to intracellular proteins and lipid bilayers

The non-covalent interactions of benzo[a]pyrene (BP) and several of its hydroxylated metabolites with ligandin, aminoazodye-binding protein A (Z-protein, fatty acid binding protein) and lecithin bilayers have been studied by equilibrium dialysis, an adsorption technique and fluorescence spectroscopy. Binding affinities expressed as $\text{v}\text{/c}$ (where $\text{v}$ = moles of BP or BP metabolite bound per mole of protein or lipid and c = unbound concentration), were measured at concentrations sufficiently low that there was no self-association of the unbound compounds as judged by their fluorescence characteristics. 3-Hydroxybenzo[a]pyrene (BP-3-phenol), 4,5-dihydro-4,5-dihydroxybenzo[a]pyrene (BP-4,5-dihydrodiol) and 7,8-dihydro-7,8-dihydroxybenzo[a]pyrene (BP-7,8-dihydrodiol) bind more strongly ($\text{v}\text{/c = 10}{}^5\text{?5 · 10}{}^5\text{l}\text{·}\text{mol}{}^{\mathrm{?1}}$) to all three binders than does BP itself ($\text{v}\text{/c = 10}{}^4\text{?7 · 10}{}^4\text{l}\text{·}\text{mol}{}^{\mathrm{?1}}$). 9,10-Dihydro-9,10-dihydroxybenzo[a]pyrene (BP-9,10-dihydrodiol) binds to ligandin with an affinity similar to those of the other BP metabolites studied here, but binds much less strongly to both protein A and lecithin ($\text{v}\text{/c = 10}{}^4$ and 3 · 10⁴ l · mol^?1, respectively). The low affinity of BP-9,10-dihydrodiol for lecithin would account for earlier findings that on incubation of BP with isolated rat hepatocytes, this metabolite egressed from the cells to the extracellular medium much more readily than either BP-4,5-dihydrodiol or BP-7,8-dihydrodiol.Calculations based on these results suggest that within hepatocytes BP and its metabolites, including BP-9,10-dihydrodiol, will be found almost exclusively associated (>98%) with lipid membranes.     

Mutagenicity of benzo[a]pyrene 7,8-dihydrodiol and 7,12-dimethylbenz[a]anthracene 3,4-dihydrodiol in S. typhimurium mediated by microsomes from rat liver and mouse skin

The mutagenic activities of trans-7,8-dihydro-7,8-dihydroxybenzo[a]-pyrene (BP 7,8-diol) and of trans-3,4-dihydroxy-7,12-dimethylbenz[a]-anthracene (DMBA 3,4-diol) towards S. typhimurium TA100 were measured in assays that were carried out on a micro-scale in liquid medium in the presence of microsomal fractions prepared from mouse skin or rat liver. In the presence of an NADPH-generating system, microsomal enzymes converted both diols into mutagens that were probably the respective 'bay-region' diol-epoxides. The rate of the enzyme-catalysed conversion of the BP 7,8-diol into mutagens by microsomal preparations from mouse epidermis was similar to that occurring with microsomes from rat liver. Pretreatment of mice by the topical application of benz[a]anthracene (BA) or 7,12-dimethylbenz[a]-anthracene (DMBA) increased the mutagenic activity of BP 7,8-diol mediated by mouse skin microsomal preparations by 2-fold and this was paralleled by a 4-fold increase in epidermal aryl hydrocarbon (benzo[a]pyrene) hydroxylase (AHH) activity. The results are discussed in relation to the high susceptibility of mouse skin to polycyclic aromatic hydrocarbon (PAH) carcinogenesis.     

Glucuronidation of benzo[a]pyrene in hamster embryo cells

The formation of water-soluble metabolites of tritium-labeled benzo[a]pyrene (BP) by cultured hamster embryo cells was studied. The ratio of the radioactivity in the aqueous phase to that in the organic phase increased with the incubation period. After incubation for 48 h with 3.75 nmol/ml of [3H] BP in the medium more than 90% of the 3H-radioactivity was found in the aqueous phase, whereas with 10-fold more BP about half the radioactivity remained in the organic phase. The main metabolites extracted from the medium at 37.5 nmol/ml BP with ethyl acetate by high pressure liquid chromatography (HPLC) were 9,10-diol and 7,8-diol; but after treatment of the medium with beta-glucuronidase the main oxygenated metabolites were phenols, the amount of 9-OH BP being more than that of 3-OH BP. beta-Glucuronidase also released 9,10-diol and 7,8-diol, but most of these diols were in the free form in the medium. The medium from cells treated with 3.75 nmol/ml BP has a quantitatively different profile, and most of the radioactivity obtained by extraction with organic solvent and digestion with beta-glucuronidase was eluted in the regions of phenols. These results show that in hamster embryo cells BP is mainly metabolised to conjugates of phenols with glucuronic acid.     

Metabolism of benzo[a]pyrene VI. Stereoselective metabolism of benzo[a]pyrene and benzo[a]pyrene 7,8-dihydrodiol to diol epoxides

(±)-7β,8α-Dihydroxy-9β,10β-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (diol epoxide-1) and (±)-7β,8α-dihydroxy-9α,10α-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (diol epoxide-2) are highly mutagenic diol epoxide diastereomers that are formed during metabolism of the carcinogen (±)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene. Remarkable stereoselectivity has been observed on metabolism of the optically pure (+)- and (?)-enantiomers of the dihydrodiol which are obtained by separation of the diastereomeric diesters with (?)-α-methoxy-α-trifluoromethylphenylacetic acid. The high stereoselectivity in the formation of diol epoxide-1 relative to diol epoxide-2 was observed with liver microsomes from 3-methylcholanthrene-treated rats and with a purified cytochrome P-448-containing monoxygenase system where the (?)-enantiomer produced a diol epoxide-2 to diol epoxide-1 ratio of 6 : 1 and the (+)-enantiomer produced a ratio of 1 : 22. Microsomes from control and phenobarbital-treated rats were less stereospecific in the metabolism of enantiomers of BP 7,8-dihydrodiol. The ratio of diol epoxide-2 to diol epoxide-1 formed from the (?)- and (+)-enantiomers with microsomes from control rats was 2 : 1 and 1 : 6, respectively. Both enantiomers of BP 7,8-dihydrodiol were also metabolized to a phenolic derivative, tentatively identified as 6,7,8-trihydroxy-7,8-dihydrobenzo[a]pyrene, which accounted for ～30% of the total metabolites formed by microsomes from control and phenobarbital-pretreated rats whereas this metabolite represents ～5% of the total metabolites with microsomes from 3-methylcholanthrene-treated rats. With benzo[a]pyrene as substrate, liver microsomes produced the 4,5-, 7,8- and 9,10-dihydrodiol with high optical purity (>85%), and diol epoxides were also formed. Most of the optical activity in the BP 7,8-dihydrodiol was due to metabolism by the monoxygenase system rather than by epoxide hydrase, since hydration of (±)-benzo[a]pyrene 7,8-oxide by liver microsomes produced dihydrodiol which was only 8% optically pure. Thus, the stereospecificity of both the monoxygenase system and, to a lesser extent, epoxide hydrase plays important roles in the metabolic activation of benzo[a]pyrene to carcinogens and mutagens.     

Covalent binding of benzo[a]pyrene metabolites to DNA, RNA and chromatin proteins in the AKR mouse embryo cell-line

A specific fraction from the nuclei of the AKR mouse embryo cell-line (fraction I) displayed a much greater localization of radioactivity compared to fraction II and III when the chemical carcinogen, [3H]benzo[a]pyrene (B[a]P) was incubated with the cells for 24 h. The radioactivity in fraction I consisted of both covalently and non-covalently bound metabolites. Isolation of the DNA, RNA and protein of fraction I revealed that 94% of the covalently bound radioactivity was to protein, 5% to RNA and 1% to DNA. Analysis of the fraction I proteins by SDS gel electrophoresis revealed that there was more radioactivity covalently bound to the larger proteins than to smaller proteins. Isoelectric focusing (IEF) of the purified proteins displayed two peaks of radioactivity, one at a pH of 5 and the other at 11. The former proteins bound more radioactivity per mass of protein than the latter proteins. Analysis of fraction I histones on acid urea polyacrylamide gels showed that the radioactivity coincided with histones H3 and H2B and low levels of radioactivity associated with histones H1, H2A and H4. Two significant peaks of radioactivity closely migrated near but did not co-migrate with histone H1. The distribution of the bound radioactivity is probably a reflection of the availability of the proteins to the reactive carcinogen metabolites. The possible binding of B[a]P metabolites to phosphorylated histones and to the high mobility of group (HMG) proteins 1 and 2 is discussed.     

Effect of various substituents in the 6-position on the relative carcinogenic activity of a series of benzo[a]pyrene derivatives

To test the hypothesis that polycyclic aromatic hydrocarbons capable of being converted to a reactive ester of the mesohydroxymethyl metabolite would be carcinogenic, a series of 6-substituted derivatives of benzo[a]pyrene (B[a]P) were tested for carcinogenicity in Sprague-Dawley rats by subcutaneous injection of the compound in sesame oil on alternate days for 30 doses. At the 0.2-μmol dose level B[a]P, 6-acetoxymethyl(6-AcOCH₂)B[a]P, 6-hydroxymethyl(6-HOCH₂)B[a]P, 6-methyl(6-CH₃)B[a]P and 6-benzoyloxymethyl(6-BzOCH₂)B[a]P were nearly equipotent, 6-formyl(6-OCH)-and 6-chloromethyl(6-ClCH₂)B[a]P were less active, and 6-methoxymethyl (6-MeOCH₂)B[a]P was inactive. At lower doses the order of potency was estimated to be: 6-AcOCH₂- = 6-HOCH₂- = or > B[a]P > 6-CH₂- > 6-BzOCH₂- > 6-ClCH₂- > 6-OCH- > 6-BrCH₂B[a]P. Incubation of these compounds in the presence of cofactors or cofactors plus a microsomal preparation of rat subcutis indicated that enzymic activation was necessary for metabolism to highly polar products and for conversion of 6-AcOCH₂-, 6-BzOCH₂- and 6-OCHB[a]P to 6-HOCH₂B[a]P. The halomethyl compounds were converted to 6-HOCH₂B[a]P in the absence of enzyme by hydrolysis. 6-MeOCH₂B[a]P was unchanged in this system. These observations are consistent with the foregoing hypothesis with regard to derivatives of B[a]P and demonstrate that compounds of this series that are capable of conversion to the 6-HOCH₂-derivatives are carcinogenic.     

Metabolic activation of benzo[a]pyrene in human skin maintained in short-term organ culture

The metabolic activation of benzo[a]pyrene (BP) was examined in six samples of human skin after topical application of the hydrocarbon to the skin in short-term organ culture. The results show that all of the samples were capable of metabolizing BP to water-soluble products and to ether-soluble products that included the 4,5-, 7,8- and 9,10-dihydrodiols and a product which had chromatographic properties identical with those of authentic trans-11,12-dihydro-11,12-dihydroxybenzo[a]pyrene (BP-11,12-diol). The major BP-deoxyribonucleoside adduct detected in each skin sample appeared to be formed from the reaction of r-7,t-8-dihydroxy-t-9,10-oxy-7,8,9,10-tetrahydrobenzo[a]pyrene (anti-BP-7,8-diol 9,10-oxide) with deoxyguanosine residues in DNA.     

Fluorescence study of DNA-complexes formed after metabolic activation of benzo(a)pyrene derivatives

Benzo(a)pyrene derivatives (1-, 2-, 3-, 7-, and 9-hydroxy-benzo(a)pyrene and trans-9,10-dihydro-9,10-dihydroxy-, -4,5-dihydro-4,5-dihydroxy-, and -7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene) were metabolized by liver microsomes isolated from 3-methylcholanthrene-treated rats in the presence of calf thymus DNA. The isolated DNA was then assayed by fluorescence for bound metabolic products. Only 2-hydroxy-benzo(a)pyrene, 9-hydroxy-benzo(a)pyrene and trans-7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene yielded detectable amounts of DNA-bound products. In contrast to the product(s) from 9-hydroxy-benzo(a)pyrene, the metabolites of 2-hydroxy-benzo(a)pyrene and trans-7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene, both strong carcinogens, had similar excitation spectra and gave considerably increased fluorescence intensities when the DNA was denatured. These data indicate structural similarities in the DNA complexes formed after metabolic activation of 2-hydroxy-benzo(a)pyrene and trans-7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene.     

Release of mutagenic metabolites of benzo[a]pyrene from the perfused rat liver after inhibition of glucuronidation and sulfation by salicylamide

The role of glucuronide and sulfate conjugation in presystemic inactivation of benzo[a]pyrene (BP) metabolites was investigated with rat livers perfused with BP (12 mumol). Comparisons were made between metabolite profiles and mutagenicity of medium from perfusions with and without salicylamide, a selective inhibitor of glucuronide and sulfate conjugation. After 4 h perfusion in the presence of salicylamide, certain BP metabolites (diols, quinones, phenols, and metabolites more polar than BP-9,10-diol) were significantly increased at the expense of quinones and phenols in the glucuronide fraction. Mutagenicity of medium (detected by the Ames test, using tester strains TA98 and TA100) was low in perfusion without salicylamide. Mutagenicity detected with tester strain TA98 was significantly increased in perfusions with salicylamide. Involvement of glucuronidation in BP inactivation was also observed at the subcellular level; when cofactors of glucuronidation were added to liver homogenates along with the NADPH regenerating system in the Ames test, BP mutagenicity was markedly decreased. Both the activation of BP to mutagenic metabolites and the inactivation of BP metabolites by glucuronidation was much more pronounced with liver homogenates from 3-methylcholanthrene-treated rats than with those from phenobarbital-treated animals or untreated controls. The results suggest an important role for glucuronidation and sulfation in the inactivation and elimination of polycyclic aromatic hydrocarbons.     

Structure elucidation of a 6-methylbenzo[a]pyrene-DNA adduct formed by horseradish peroxidase in vitro and mouse skin in vivo

Activation of polycyclic aromatic hydrocarbons (PAH) by horseradish peroxidase (HRP) with H₂O₂ has been studied as a model system for one-electron oxidation. This peroxidase has been used to catalyze binding of $\text{6-}\text{[}{}^{14}\text{C]methylbenzo}\text{[a]}\text{pyrene}$ (BP-6-CH₃) to DNA, which was purified, hydrolyzed to deoxyribonucleosides and analyzed by high pressure liquid chromatography (HPLC). The predominant hydrocarbon-DNA adduct observed was identified as BP-6-CH₃ bound at the 6-methyl group to the 2-amino group of dG, confirming that activation by HRP occurs by one-electron oxidation. When DNA from mouse skin treated in vivo with [¹⁴C]BP-6-CH₃ was purified, hydrolyzed and analyzed by HPLC, a profile was observed which was qualitatively similar to that from the peroxidase system. In particular, the identified adduct with the hydrocarbon bound at the 6-methyl group to the 2-amino group of dG was obtained. These results demonstrate that one-electron oxidation is the mechanism of activation by HRP for aromatic hydrocarbons and indicate that the same mechanism may occur in mouse skin, a target tissue for hydrocarbon carcinogenesis.     

Formation of the 11,12-diol as a metabolite of benzo(a)pyrene by rat skin in vivo

The dihydrodiols present as metabolites in rat skin after topical application of ³H-labelled benzo(a)pyrene included a significant amount of radioactivity that cochromatographed with synthetic $\text{trans}$-11,12-dihydro-11,12-dihydroxybenzo(a)pyrene. Treatment of the radioactive metabolite with hot mineral acid gave a product that had chromatographic properties identical to those of the phenol similarly formed from the synthetic dihydrodiol and acetylation of the metabolite yielded a product that cochromatographed with the diacetate of the synthetic dihydrodiol. These observations show that the 11,12-dihydrodiol is formed as a metabolite of BP in rat skin $\text{in vivo}$. The metabolite was not detected in mouse skin.     

Benzo[a]pyrene uptake into rat liver microsomes: Effects of adsorption of benzo[a]pyrene to asbestos and non-fibrous mineral particulates

The fluorescence yield of benzo[a]pyrene (BP) increases dramatically upon its transfer from the surface of particulates to rat liver microsomes. Adsorption of BP to Canadian chrysotile, anthophyllite, hematite and silica results in greatly enhanced uptake rates into microsomes when compared to uptake from a microcrystalline dispersion of BP. The fibrous minerals chrysotile and anthophyllite were more effective than silica and hematite in enhancing BP uptake. Simple mixtures of BP microcrystals and particles did not display enhanced transport, indicating that adsorption of BP to the particulate surface is necessary for enhanced microsomal uptake. BP was not released into microsomes from carbon black.We suggest that particulate-enhanced availability of BP may be of significance in the co-carcinogenesis between particulates and polynuclear aromatic hydrocarbons. However, other mechanisms are also possible, and are not excluded by our experiments. The fluorescence methodology described in this paper provides a novel and convenient means to quantify microsomal uptake of BP and thereby investigate further the mechanisms of cocarcinogenesis.     

Heterocyclic polycyclic aromatic hydrocarbon carcinogenesis: 7H-dibenzo[c,g]carbazole metabolism by microsomal enzymes from mouse and rat liver

The metabolism of dibenzo[c,g]carbazole (DBC), was studied in vitro using microsomal fractions of mouse and rat liver from animals, which were treated with 3-methylcholanthrene (MC). The separation of extractable metabolites by high pressure liquid chromatography (HPLC) and thinlayer chromatography (TLC) as well as identification of most of them by nuclear magnetic resonance, mass spectrometry and comparison with synthetically obtained products are described. The microsomes of both species produced the same twelve compounds of which the following have been identified: five monohydroxylated derivatives (phenols), the product of further oxidation of one of them, and a dihydrodiol. The 5-OH-DBC (60% including its spontaneously-formed dimer) and the 3-OH-DBC (14%) are the main metabolites. Three minor metabolites cochromatographed with synthetically prepared 2-OH-DBC, 4-OH-DBC and 6-OH-DBC. The dihydrodiol detectable in small quantity (4–6%) was tentatively identified as 3,4-dihydroxy-3,4-dihydro-DBC by the sensitivity of its formation to very low concentrations of the inhibitor of microsomal epoxide hydrolase, 1,1,1-trichloropropene oxide, by its molecular ion and major fragment in mass spectrometry and by its dehydration product 3-OH-DBC. No other dihydrodiols were detected. The qualitative and quantitative effects of various modulators of metabolism (enzyme inhibitors, apparently homogeneous epoxide hydrolase, glutathione, supernatant fraction) were investigated. The results are discussed with respect to possible ultimate carcinogens.     

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.     

Remediation of benzo[a]pyrene and chrysene-contaminated soil with industrial hemp (Cannabis sativa)

The phytoremediation, with industrial hemp (Cannabis sativa), of a Hawaiian silty clay soil contaminated with two polycyclic aromatic hydrocarbons (PAHs), chrysene and benzo[a]pyrene, was studied. Hemp showed a very high tolerance to the contaminants. The growth rates of hemp, compared with control, in soils fortified with chrysene and benzo[a]pyrene at concentrations of each varying from 25 to 200 micrograms/g were consistently above 100%. The plants grew from seed for 45 days in soil fortified with PAHs at concentrations of 25, 50, and 75 micrograms/g. Controls were pots with contaminated soil but no plant. PAHs levels were significantly reduced in all pots (control and seeded pots), expect for one set at a high concentration of chrysene, which may be due to uneven spiking. A time course study over 28 days was done to monitor changes of microbial count and levels of chrysene. Little changes were observed for the total microbial count in the soil, and the concentration of chrysene in the soil decreased slightly in the pots containing plants. However, the chrysene levels in those pots were consistently lower than those in the pots without plants.     

Ubiquitous binding of benzo[a]pyrene metabolites to DNA and protein in tissues of the mouse and rabbit

The in vivo formation of benzo[alpha]pyrene (BP) metabolite-DNA adducts in several tissues of mice and rabbits was examined. Included were tissues with widely divergent xenobiotic metabolizing capabilities such as liver and brain. The major adduct identified in each tissue was the (+)-7 beta,8 alpha-dihydroxy-9 alpha,10 alpha-epoxy-7,8,9,10-tetrahydro-BP (BPDEI)-deoxyguanosine adduct. A 7 beta,8 alpha-dihydroxy-9 beta,10 beta-epoxy-7,8,9,10-tetrahydro-BP (BPDEII)-deoxyguanosine adduct, a (-)-BPDEI-deoxyguanosine adduct and an unidentified adduct were also observed. These adducts were present in all of the tissues of the mice and in the lungs of the rabbits; only BPDEI and BPDEII were seen in the rest of the rabbit tissues. In all of the tissues studied, the DNA adduct levels were unexpectedly similar. For example, the BPDEI-DNA adduct levels in muscle and brain of mice were approx. 50% of those in lung and liver at each oral BP dose examined. After an i.v. dose of BP in rabbits, the BPDEI adduct levels in lung were three times those in brain or liver and twice those in muscle. The binding of BP metabolites to protein was also determined in these tissues. The tissue-to-tissue variation in protein binding levels of BP metabolites was greater than that for BPDEI-DNA adducts. There are several possible explanations for the in vivo binding of BP metabolites to DNA and protein of various tissues. First, oxidative metabolism of BP in each of the examined tissues might account for the observed binding. Second, reactive metabolites could be formed in tissues such as liver and lung and be transported to cells in tissues such as muscle and brain where they bind to DNA and protein. In any case, the tissue-to-tissue variations in protein and DNA binding of BP-derived radioactivity do not correlate with differences in cytochrome P-450 activity.