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.     

Copper thionein in the kidneys of copper-poisoned sheep

A study has been made of the distribution of copper in the kidneys of copper-poisoned sheep, containing up to 240 μg copper/g fresh cortex. About 64% of the copper in the cortex was present in the cytosol and 75% of this occurred in a form with molecular weight of approx. 12 000. This was partially purified by gel filtration on Sephadex G-75 and Bio-Gel P.10 and ion exchange chromatography on DEAE Sephadex A-25 to give three sub-fractions, which also contained zinc. The amino acid composition, copper content and chromatographic behaviour of these proteins indicated that they were copper-thioneins.No significant amounts of the proteins were detected in the plasma or erythrocytes of the copper-poisoned sheep when they were undergoing the haemolytic crisis typical of this syndrome. It is concluded that metallothionein constitutes the major copper-binding protein in the kidneys of copper-poisoned sheep. However the rapid accumulation of the protein in the kidney, and the development of kidney damage, are unlikely to have arisen from the release of the intact copper-protein from the liver and its transport via the blood to the kidneys.     

Some properties of vicinal diol-epoxides derived from benzo(a)anthracene and benzo(a)pyrene

The alkylating properties of pairs of syn- and anti-isomers of 2 diol-epoxides derived from benzo(a)pyrene (BP) and of 1 derived from benz(a)anthracene (BA) have been investigated. Of the anti-diol-epoxides, anti-BP 7,8-diol-9,10-oxide was the most reactive compound towards DNA, towards sodium p-nitrothiophenolate in a non-aqueous solvent system, and towards 4-(p-nitrobenzyl)pyridine in aqueous solution; anti-BP 9,10,-diol-7,8-oxide was of intermediate reactivity and anti-BA 8,9-diol-10,11-oxide was least reactive. The syn-diol-epoxides gave unsatisfactory results with DNA and 4-(p-nitrobenzyl)pyridine because of their rapid solvolysis in aqueous solution, but with sodium p-nitrothiophenolate showed the order of reactivity syn-BP 7,8-diol-9,10-oxide greater than syn-BA 8,9-diol-10,11-oxide greater than syn-BP 9,10-diol-7,8-oxide. The products of the reaction between diol-epoxides and nucleic acids were examined by Sephadex LH-20 chromatography followed by high-pressure liquid chromatography (HPLC) and the diol-epoxides were shown to react principally with the guanosine and adenosine moieties of RNA.     

Effect of various chemicals on the metabolism of benzo(a)pyrene by cultured rat colon

The effect of various co- and anti-carcinogens of colon carcinogenesis on the metabolism of benzo(a)pyrene (BP) in cultured rat colon is reported. Rat colon enzymatically converted BP into metabolites which bind to cellular macromolecules i.e., DNA and protein. Activity of aryl hydrocarbon hydroxylase (AHH) activity and binding levels of BP to macromolecules were higher in the descending colon when compared to other segments. The major metabolites of BP, extractable with ethylacetate, were quinones, tetrols, 7,8-diol and a peak containing 9,10-dihydroxy-9,10-dihydrobenzo(a)pyrene and 7,8,9-trihydroxy-7,8-dihydrobenzo(a)pyrene. The binding levels of BP to DNA and protein in the explant was lowered by co-incubation with 7,8-benzoflavone (7,8-BF) (3.6 and 18.0 μM), a known inhibitor of AHH, and with disulfiram (100 μM), an anti-oxidant. The absence of vitamin A in the media also resulted in a lower level of BP binding to DNA and protein and in lower activity of AHH. Pretreatment with known inducers of AHH such as phenobarbital (PB) or benz(a)anthracene (BA), did not have any significant effect on the binding levels of BP to DNA or on the AHH activity. of the bile acids investigated only taurodeoxycholic acid significantly increased the binding level of BP to DNA.     

Reactivity and binding of benzo(a)pyrene diol epoxide to poly(dG-dC).(dG-dC) and poly(dG-m5dC).(dG-m5dC) in the B and Z forms

The physical and covalent binding of the carcinogen benzo(a)pyrene-7,8-diol-9,10-oxide (BaPDE) to poly(dG-dC).(dG-dC) and poly(dG-m5dC).(dG-m5dC) in the B and Z forms were studied utilizing absorbance, fluorescence and linear dichroism techniques. In the case of poly(dG-dC).(dG-dC) the decrease in the covalent binding of BaPDE with increasing NaCl concentration (0.1-4 M) as the B form is transformed to the Z form is attributed to the effects of high ionic strengths on the reactivity and physical binding of BaPDE to the polynucleotides; these effects tend to obscure differences in reactivities with the B and Z forms of the nucleic acids. In the case of poly(dG-m5dC).(dG-m5dC) the B-to-Z transition is induced at low ionic strength (2 mM NaCl + 10 microM Co(NH3)6Cl3) and the covalent binding is found to be 2-3-times lower to the Z form than to the B form. Physical binding of BaPDE by intercalation, which precedes the covalent binding reaction, is significantly lower in the Z form than in the B form, thus accounting, in part, for the lower covalent binding. The linear dichroism characteristics of BaPDE covalently bound to the Z and B forms of poly(dG-m5dC).(dG-m5dC) are consistent with nonintercalative, probably external conformations of the aromatic pyrenyl residues.     

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.     

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.     

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.     

Factors for efficiency of the Salmonella/microsome mutagenicity assay.

Factors were studied which modify the enzymatic capacity of mouse liver microsomal mixed-function oxidase to convert vinylidene chloride (1.1-dichloroethylene) (VDC) into mutagens in the Salmonella/microsome mutagenicity test. A microsomal fraction incorporated in soft agar layer converted VDC into mutagens during 7 h at a constant rate; these were detected with S. typhimurium TA100. In absence of VDC the enzymatic activity declined gradually to nil after 14 h of incubation at 37 degrees C. The presence of EDTA greatly enhanced the microsome-mediated mutagenicity of VDC and led to prolonged enzymatic viability, but only when liver fractions from phenobarbitone (PB) pretreated mice were used. The efficiency of the plate incorporation assay for the detection of mutagens is discussed in comparison with assays in liquid suspension.     

The DNA binding of benzo[alpha]pyrene metabolites catalysed by rat lung microsomes in vitro and in isolated perfused rat lung.

When [³H]benzo[a]pyrene is incubated in vitro together with DNA, NADPH and rat lung microsomes, covalent binding of benzo[a]pyrene (BP) metabolites to DNA occurs. These metabolite-nucleoside complexes can be resolved into several distinct peaks by elution of a Sephadex LH-20 column with a water-methanol gradient. 3-Methylcholanthrene (MC) pretreatment of animals induces the total covalent binding in vitro several-fold and increases the amounts of at least five metabolite-nucleoside complexes associated with the 7,8-diol-9,10-epoxidcs, the 7,8-oxide or quinones oxygenated further, the 4,5-oxide and phenols oxygenated further. These increases correspond well with the increases in the production of both non-K-region and K-region metabolites of BP by lung microsomes, as determined by highpressure liquid chromatography (HPLC). On the other hand, when [³H]BP is metabolized in isolated perfused rat lung, only the peak representing the 7,8-diol-9,10-epoxide bound to nucleoside(s) is readily detectable and then only in lungs from MC-treated animals. The extent of binding of BP metabolites to lung DNA is very low, about 0.0004% of the total dose applied to the perfusion medium; more than 60% of this can be accounted for by the binding of the 7,8-diol-9,10-epoxides to nucleoside(s). It is suggested that the further metabolism leading to metabolites not available to covalent binding, (e.g. conjugation) of primary BP metabolites in the intact tissue is responsible for the differences in the metabolite-nucleoside patterns observed in vivo, as compared with microsomal metabolism in vitro.     

Differences in the repair of DNA strand breaks induced by 9-hydroxy-benzo(a)pyrene and trans-7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene in cultured human fibroblasts

Two benzo(a)pyrene metabolites were found to induce DNA strand breaks in cultured human fibroblasts. DNA strand breaks induced by the non- or weakly carcinogenic 9-hydroxy-benzo(a)pyrene were repaired within two hours, while those induced by the strongly carcinogenic trans-7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene were repaired at a much slower rate.     

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.     

Analysis of fish bile with HPLC — fluorescence to determine environmental exposure to benzo(a)pyrene

Brown bullhead from the Black River, Ohio, have a high incidence of liver neoplasia which is associated with elevated concentrations of polynuclear aromatic hydrocarbons (PAHs) in the sediment. We evaluated the use of biliary concentrations of benzo(a)pyrene [B(a)P] equivalents as a means for determining PAH exposure. Bile was collected from 16 brown bullheads and 8 common carp taken from each of two Lake Erie tributaries in Ohio, the industrialized Black River and the non-industrialized Old Woman Creek. Hatchery bullhead (n = 8) were used to determine base levels of PAHs. A high performance liquid chromatography (HPLC) — fluorescence technique was used to determine the concentration of B(a)P equivalents in the bile samples. The area of all peaks fluorescing at 380/430 nm was summed to give a single value for B(a)P equivalents in each sample. Concentrations of B(a)P equivalents generally reflected concentrations of PAH in sediment where fish were collected. Bile taken from Black River carp contained the highest concentration of B(a)P equivalents and was significantly different from all other groups. The value obtained for Black River bullhead was also high and was found to be significantly different from hatchery bullhead. B(a)P equivalents varied between carp and bullhead from the same habitat possibly because of differing food habits or metabolic pathways. However, our results indicate that relative levels of B(a)P equivalents in the bile of fish correspond well to B(a)P levels in sediment and may offer a means of determining environmental exposure of fish to the parent compound.     

乳杆菌吸附苯并芘的特性

[目的]探讨植物乳杆菌(Lactobacillus plantarum)121和戊糖乳杆菌(Lactobacillus pentosus)ML32的苯并芘吸附作用与机制.[方法]采用高效液相色谱检测菌体对苯并芘的吸附率.[结果]菌株121和ML32对苯并芘的吸附率分别为65.9%和64.9%,这种吸附特性与菌体活力无关,随培养时间延长、温度提高以及细胞浓度的上升而增加.菌株121和ML32的吸附率在pH 4和5时达到最大,分别为87.6%和89.0%.当培养液中Ca2+或Mg2+浓度大于0.05mol/L时,菌体吸附率与盐离子浓度呈正相关.苯洗脱会导致乳杆菌所吸附的苯并芘减少90%.经碱性蛋白酶、中性蛋白酶、溶菌酶及TCA和SDS等方法处理后,菌体吸附率上升,且不易被苯去除.在胆盐及胃酸环境下,两株菌的吸附率均提高至70%以上,而胰蛋白酶的存在仅对菌株121的吸附率有较大影响.[结论]两株乳杆菌可以通过吸附作用从环境中清除苯并芘,其吸附效果与细菌细胞壁的结构和组成有关.     

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.     

Protective effect of vanillic acid against benzo(a)pyrene induced lung cancer in Swiss albino mice

Vanillic acid (VA) is found in high concentrations in various plants and used as traditional medicine for various diseases. The aim of the existing study is to illustrate the protective effects of VA against benzo(a)pyrene (B(a)P)‐induced lung cancer in Swiss albino mice. B(a)P (50 mg/kg b.wt.) was given orally to induce lung cancer in mice. The body weight, tumor incidence, carcinoembryonic antigen (CEA), neuron‐specific enolase (NSE), and enzymatic/nonenzymatic antioxidants (superoxide dismutase, catalase, glutathione reductase, glutathione peroxidase, and glutathione) were estimated. Further histochemical investigation through hematoxylin and eosin staining was also carried out. B(a)P administered groups showed increased levels of serum pathological markers CEA, NSE along with reduced final body weight as well as decreased tissue enzymatic and nonenzymatic antioxidants activities, whereas VA treatment (200mg/kg/b.wt) along with B(a)P showed significantly reverted the above changes, which proves as prominent anticancer effects in experimentally induced lung cancer. Overall, these results suggest that VA has an efficient preventive action against B(a)P‐induced lung cancer, and this is attributed to its free‐radical scavenging antioxidant activities.     

Biodegradation of benzo(a)pyrene by a newly isolated Fusarium sp

Benzo(a)pyrene (BaP) is a five-ring polycyclic aromatic hydrocarbon produced by the incomplete combustion of organic materials. It is one of the priority pollutants listed by the US Environmental Protection Agency. This study describes a fungal isolate that is able to biodegrade benzo(a)pyrene. The filamentous fungus, isolated from leaves of Pterocarpus macrocarpus Kurz., was identified as a Fusarium sp. (strain E033). Fusarium sp. E033 was able to survive in the presence of benzo(a)pyrene concentrations up to 1.2 mM (300 mg L(-1)). Biodegradation experiments using 0.4 mM (100 mg L(-1)) benzo(a)pyrene demonstrated that Fusarium sp. E033 was able to degrade 65-70% of the initial benzo(a)pyrene provided, and two transformation products, a dihydroxy dihydro-benzo(a)pyrene and a benzo(a)pyrene-quinone, were detected within 30 days of incubation at 32 degrees C. The factors affecting biodegradation efficiency were also investigated. While increasing aeration promoted better fungal growth and benzo(a)pyrene biodegradation, increasing the glucose concentration from 5 to 50 mM had an adverse effect on biodegradation. Ethanol and methanol, provided at 5 mM to increase benzo(a)pyrene water solubility, increased the fungal biomass yield but did not promote degradation. The Fusarium sp. E033 isolated in this study can tolerate and degrade relatively high concentrations of benzo(a)pyrene, suggesting its potential application in benzo(a)pyrene bioremediation.     

乳杆菌在模拟肉制品条件下结合苯并芘的效果

【背景】乳杆菌对众多致癌物具有吸附作用,但关于乳杆菌结合吸附苯并芘特性的研究并不多。【目的】探讨戊糖乳杆菌(Lactobacillus pentosus) ML32和植物乳杆菌(Lactobacillus plantarum)121对加工肉制品中苯并芘的吸附能力与吸附机制。【方法】基于HPLC检测菌体对不同模拟加工处理方式肉品中的苯并芘的吸附率。【结果】植物乳杆菌121和戊糖乳杆菌ML32对模拟油炸、烟熏或烧烤方式处理肉中苯并芘的吸附率均在30%以上。菌株121对直接烟熏肉中的苯并芘吸附率为41.21%,直接油炸肉中吸附率为38.71%,直接烧烤肉中吸附率为37.51%;菌株ML32对间接烟熏肉中的苯并芘吸附率为40.02%,间接烧烤肉中吸附率为38.01%。植物乳杆菌121适合于去除高温长时间加工肉中的苯并芘,戊糖乳杆菌ML32则相反。另外,乳杆菌细胞壁中的肽聚糖或许在吸附过程中发挥了主要作用。【结论】两株乳杆菌121和ML32具有吸附某些加工肉制品中苯并芘的效果,或许可以作为一种方法用于消除某些肉制品中因苯并芘过量带来的风险。     

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.