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PubMed2003

Effect of salinity on the photolysis of chrysene adsorbed to a smectite clay.

The rate of photooxidation (lambda, 300-800 nm) of the polycyclic aromatic hydrocarbon chrysene was significantly enhanced in aqueous suspensions of the smectite clay, Laponite RD, relative to its rate of photolysis in aqueous solution. The photodegradation of chrysene is reported at pH 8.30, at several different ionic strengths that correlate to freshwater and saltwater. The kinetics of chrysene loss are first order in chrysene. The photodegradation products 1,4-chrysenediol, 1,4-chrysenequinone, phthalic acid, and 2-formyl benzoic acid have been positively identified and quantified against analytical standards. The mechanism of chrysene degradation was probed by comparing the effects of added methanol, bicarbonate, diazabicyclooctane, chloride, bromide, and iodide on the rate of chrysene photooxidation. Chrysene photooxidation was suppressed by diazabicylooctane and halide ions but was unaffected by methanol or bicarbonate, implying that 1O2 played a significant role in its removal. The overall rate of chrysene loss was governed by the salinity of the solution and the extent of surface coverage. The steady-state concentration of singlet oxygen was measured and varied positively with chrysene loading but was reduced dramatically at salinities comparable to the marine environment. The relative contributions of Cl-, Br-, and I- to the reduction in [1O2]ss are reported, with I- the most effective 1O2 quencher. The implication of the research is that photoprocessing of particle-bound PAHs may fall off as rapidly as they are transported into marine environments. A predictive kinetic model for the photodegradation of adsorbed chrysene is presented.

Adsorption↗
PubMed1986

Metabolism of the bay-region diol-epoxide of chrysene to a triol-epoxide and the enzyme-catalysed conjugation of these epoxides with glutathione.

Metabolic activation of chrysene in mouse skin appears to involve r-1,t-2-dihydroxy-t-3,4-oxy-1,2,3,4-tetrahydrochrysene (anti-chrysene-1,2-diol 3,4-oxide) and 9-hydroxy-r-1,t-2-dihydroxy-t-3,4-oxy-1,2,3,4-tetrahydrochrysene (anti-9-OH-chrysene-1,2-diol 3,4-oxide). The enzyme-catalysed conjugation of these epoxides with [35S]glutathione has been studied in experiments in which the glutathione conjugates were separated by h.p.l.c. and examined by fluorescence spectrophotometry. Both anti-chrysene-1,2-diol 3,4-oxide and anti-9-OH-chrysene-1,2-diol 3,4-oxide formed conjugates nonenzymically and both were shown to be substrates for rat liver glutathione transferases. When anti-chrysene-1,2-diol 3,4-oxide was incubated with [35S]glutathione and a rat liver microsomal metabolizing system, glutathione conjugates with h.p.l.c. and fluorescence spectral characteristics identical to those of conjugates formed from both anti-chrysene-1,2-diol 3,4-oxide and anti-9-OH-chrysene-1,2-diol 3,4-oxide were detected. This finding provides evidence that anti-chrysene-1,2-diol 3,4-oxide can be further metabolized to the triol-epoxide, anti-9-OH-chrysene-1,2-diol 3,4-oxide by rat liver microsomal systems.

Animals↗
PubMed2003

Metabolism of chrysene by brown bullhead liver microsomes.

We have investigated the regio- and stereoselective metabolism of chrysene, a four-ring symmetrical carcinogenic polycyclic aromatic hydrocarbon (PAH), by the liver microsomes of brown bullhead (Ameriurus nebulosus), a bottom-dwelling fish species. The liver microsomes from untreated and 3-methylcholanthrene (3-MC)-treated brown bullheads metabolized chrysene at the rate of 30.1 and 82.2 pmol/mg protein/min, respectively. Benzo-ring diols (1,2-diol and 3,4-diol) were the major chrysene metabolites formed by liver microsomes from control and 3-MC-treated fish. However, the control microsomes produced a considerably higher proportion of chrysene 1,2-diol (benzo-ring diol with a bay region double bond) plus 1-hydroxychrysene, than 3,4-diol plus 3-hydroxychrysene, indicating that these microsomes are selective in attacking the 1,2- position of the benzo-ring. On the other hand, 3-MC-induced microsomes did not show such a regioselectivity in the metabolism of chrysene. Control bullhead liver microsomes, compared to control rat liver microsomes, produced a considerably higher proportion of chrysene 1,2-diol, the putative proximate carcinogenic metabolite of chrysene. Like rat liver microsomes, bullhead liver microsomes produced only trace amounts of the K-region diol. Chrysene 1,2-diol and 3,4-diol formed by the liver microsomes from both control and 3-MC-treated bullheads consisted predominantly of their R,R-enantiomers. Chrysene is metabolized by bullhead liver microsomal enzymes to its benzo-ring diols with a relatively lower degree of stereoselectivity compared to benzo[a]pyrene (a five-ring PAH), but with a higher degree of stereoselectivity compared to phenanthrene (a three-ring PAH). The data of this study, together with those from our previous studies with phenanthrene, benzo[a]pyrene and dibenzo[a,l]pyrene (a six-ring PAH), indicate that the regioselectivity in the metabolism of PAHs by brown bullhead and rainbow trout liver microsomes does not vary greatly with the size and shape of the molecule, whereas the degree of stereoselectivity in the metabolism of PAHs to benzo-ring dihydrodiols does.

Animals↗
PubMed1991

Metabolism of chrysene, 5-methylchrysene, 6-methylchrysene and 5,6-dimethylchrysene in rat liver cytosol, in vitro, and in rat subcutaneous tissue, in vivo.

The polynuclear aromatic hydrocarbon chrysene undergoes a bioalkylation substitution reaction in vitro, in rat liver cytosol preparations, and in vivo, in rat dorsal subcutaneous tissue to yield 6-methylchrysene as a metabolite. In addition, both 5-methyl- and 6-methylchrysene were found to undergo a dealkylation reaction in these tissues to yield chrysene as well as both a biooxidation reaction to yield the corresponding hydroxyalkyl substituted chrysene and a bioalkylation reaction to give a dimethyl substituted chrysene. 5-Methylchrysene enzymatically cyclized to the 4,5-methylenechrysene derivative, an analog of benzo[a]pyrene in these tissues. 5,6-Dimethylchrysene was metabolized to monomethyl chrysenes, chrysene, and the hydroxyalkyl substituted chrysenes. The results suggest that chemical or biochemical substitution of a methyl group at the center of highest biochemical reactivity may be a necessary step in the metabolic activation and carcinogenicity of these compounds and their methylene bridged metabolites.

Alkylation↗
PubMed1986

Stereoselective metabolism of chrysene by rat liver microsomes. Direct separation of diol enantiomers by chiral stationary phase h.p.l.c.

The direct enantiomeric resolution of non-K region trans-1,2-dihydrodiol, 1,2,3,4-tetrahydro-trans-1,2-diol, trans-3,4-dihydrodiol and 1,2,3,4-tetrahydro-trans-3,4-diol, K region trans- and cis-5,6-dihydrodiols and their monomethyl ethers of chrysene was studied by chiral stationary phase high-performance liquid chromatography (CSP-h.p.l.c.). The chiral stationary phase columns were packed with gamma-aminopropylsilanized silica to which either (R)-N-(3,5-dinitrobenzoyl)-phenylglycine or (S)-N-(3,5-dinitrobenzoyl)leucine was bonded either ionically or covalently. Enantiomers of all dihydrodiol derivatives were resolved by one or more, but not all, of the chiral stationary phases utilized. Enantiomeric resolutions were substantially improved when the non-K region dihydrodiols were converted to tetrahydrodiols. The absolute configurations of the K region trans- and cis-5,6-dihydrodiols were established by the exciton chirality circular dichroism method. The (R,R):(S,S) enantiomer ratios, determined by CSP-h.p.l.c., of the 1,2-, 3,4- and 5,6-trans-dihydrodiols formed in the metabolism of chrysene by liver microsomes from untreated male rats of the Sprague--Dawley strain were found to be 51:49, 99:1 and 86:14, respectively; from phenobarbital-treated rats, 41:59, 99:1 and 87:13, respectively; from 3-methylcholanthrene-treated rats, 96:4, 99:1 and 92:8, respectively. The absolute configurations of chrysene 5,6-epoxide enantiomers, resolved by CSP-h.p.l.c., were elucidated by the determination of the structures and absolute configurations of their methoxylation products. Both enantiomers of chrysene 5,6-epoxide were hydrated by microsomal epoxide hydrolase to chrysene trans-5,6-dihydrodiol enriched (67-92%) in the 5R,6R enantiomer. Chrysene 5R,6S-epoxide was hydrated to trans-5,6-dihydrodiol at a rate approximately 6-fold faster than chrysene 5S,6R-epoxide.

Animals↗
PubMed1993

Mutagenicity of chrysene, its methyl and benzo derivatives, and their interactions with cytochromes P-450 and the Ah-receptor; relevance to their carcinogenic potency.

The genotoxicity in the Ames test of chrysene, of its six methyl and of two benzo-derivatives, and their ability to induce rat hepatic CYP1A and epoxide hydrolase activities, and stimulate their own bioactivation were determined. The primary objective is to provide a rationale for the higher carcinogenic potency of 5-methylchrysene when compared to that of the parent compound and the other methyl isomers. In the presence of Aroclor 1254-induced hepatic microsomes chrysene, its 5- and 4-methyl derivatives and to a lesser extent the 2- and 3-methyl derivatives and benzo[c]chrysene elicited a positive mutagenic response. Chrysene, all derivatives studied and especially benzo[c]chrysene were potent inducers of rat hepatic CYP1A1 activity as exemplified by the O-deethylation of ethoxyresorufin (30-180-fold when activities are expressed per nmol of total cytochrome P-450). All compounds studied displaced [3H]TCDD from the cytosolic Ah receptor at a concentration of 10(-10)-10(-9) M. Benzo[c]chrysene and to a lesser extent 6-methylchrysene were the only compounds capable of stimulating epoxide hydrolase activity, but the effect was modest. None of the compounds studied could induce its own activation to mutagens in the Ames test. The present findings indicate that the higher carcinogenic potency of 5-methylchrysene cannot be related to its mutagenic potential or its ability to enhance its own activation through induction of CYP1A1 and epoxide hydrolase activities.

Animals↗
PubMed1983

Metabolic activation of chrysene in mouse skin: evidence for the involvement of a triol-epoxide.

All three possible dihydrodiols of chrysene and a chrysene triol, formed from the further metabolism of the chrysene-1,2-diol, were detected when ether extracts of mouse skin that had been treated with 3H-labelled chrysene were examined by h.p.l.c. The major deoxyribonucleoside-hydrocarbon adducts present in hydrolysates of DNA isolated from the mouse skin were examined by chromatography on Sephadex LH20 and by h.p.l.c. on Zorbax ODS. One adduct had chromatographic properties identical to those of the major adduct formed when r-1,t-2-dihydroxy-t-3,4-oxy-1,2,3,4-tetrahydrochrysene reacts with DNA. A second major adduct was present that had chromatographic properties that were indistinguishable from those of an adduct that was formed when either chrysene-1,2-diol or 3-hydroxychrysene were incubated with DNA in a rat liver microsomal metabolising system. The results provide evidence that this new adduct is formed via the reaction of a 'triol-epoxide', that appears to be 9-hydroxy-chrysene-1,2-diol 3,4-oxide, with DNA in mouse skin.

Animals↗
PubMed1988

Further metabolism of diol-epoxides of chrysene and dibenz[a,c]anthracene to DNA binding species as evidenced by 32P-postlabelling analysis.

Incubation of r-1,t-2-dihydroxy-t-3,4-oxy-1,2,3,4-tetrahydrochrysene (anti-chrysene-1,2-diol 3,4-oxide), the bay-region diol-epoxide of chrysene, with rat liver microsomes in the presence of NADP+ and DNA, followed by 32P-postlabelling analysis of the DNA, revealed the presence of at least two adducts not detected when anti-chrysene-1,2-diol 3,4-oxide was incubated with DNA alone. The formation of these adducts was not blocked by the epoxide hydrolase inhibitor 1,1,1-trichloropropane-2,3-oxide. One of the adducts cochromatographed with the adduct spot obtained when authentic 9-hydroxy-r-1,t-2-dihydroxy-t-3,4-oxy-1,2,3,4-tetrahydrochrysene (anti-9-OH-chrysene-1,2-diol 3,4-oxide) was reacted with DNA. Evidence suggested that a second adduct could also be formed by further metabolism of anti-9-OH-chrysene-1,2-diol 3,4-oxide. In addition, evidence was obtained for the further metabolism of the syn-isomer of chrysene 1,2-diol 3,4-oxide and the anti-isomer of a non-bay-region diol-epoxide of dibenz[a,c]anthracene to DNA binding species, but not for that of either the anti- or syn-isomers of the bay-region diol-epoxide of benzo[a]pyrene, the anti-isomers of the bay-region or a non-bay-region diol-epoxide of benz[a]anthracene, or the anti-isomer of the bay-region diol-epoxide of benzo[b]fluoranthene.

Animals↗
PubMed1987

Stereoselective formations of K-region and non-K-region epoxides in the metabolism of chrysene by rat liver microsomal cytochrome P-450 isozymes.

The K-region 5,6-epoxide and non-K-region 1,2- and 3,4-epoxides of chrysene were isolated by normal phase high performance liquid chromatography (HPLC) from a mixture of products formed in the metabolism of chrysene by liver microsomes from untreated (control), phenobarbital-treated, or 3-methylcholanthrene-treated rats in the presence of an epoxide hydrolase inhibitor, 3,3,3-trichloropropylene 1,2-oxide. Epoxides were characterized by ultraviolet, mass, and circular dichroism spectral and chiral stationary phase HPLC analyses. Each of the metabolically formed epoxides was hydrated by rat liver microsomal epoxide hydrolase to a trans-dihydrodiol. The metabolically formed chrysene 5,6-epoxides were determined by chiral stationary phase HPLC and were found to contain (5S,6R):(5R,6S) enantiomer ratios of 68:32 (control), 71:29 (phenobarbital), and 5:95 (3-methylcholanthrene), respectively. The enantiomers of chrysene 1,2-epoxide and 3,4-epoxide were also resolved by chiral stationary phase HPLC. However, the enantiomeric compositions of the metabolically formed chrysene 1,2- and 3,4-epoxides, which racemized rapidly at room temperature, could not be directly determined. By using molecular oxygen-18 in the in vitro incubation of chrysene and by mass spectral analyses of the resulting oxygen-18-containing dihydrodiol metabolites and their acid-catalyzed dehydration (phenolic) products, both 1,2-epoxide and 3,4-epoxide were found to be converted by microsomal epoxide hydrolase-catalyzed water attack at predominantly (greater than or equal to 97%) the allylic carbons.

Animals↗
PubMed1985

The effect of chrysene and some polycyclic aromatic hydrocarbons on the elimination of theophylline in rats.

The investigations of the effect of some compounds belonging to the group of polycyclic aromatic hydrocarbons (PAH), e. g. benzo[a]pyrene, chrysene, fluorene and pyrene, on the elimination of theophylline injected i. v. into rats have shown that benzo[a]pyrene and chrysene accelerate the elimination of this drug (elimination rate constant in control group: 0.2504 h-1; after benzo[a]pyrene: 0.3626 h-1; after chrysene: 0.3582 h-1). The increase of theophylline elimination rate constant by chrysene depends on its dose, and this relationship is of sigmoid type in the dose range of 1-20 mg X kg-1. Besides, dependence of theophylline elimination rate constant on the time of chrysene dosing was also shown. After oral administration of theophylline the decrease of its amount reaching the circulation by 11% was also observed, which was caused by the influence of chrysene on the first-pass effect, beside its influence on the elimination rate.

Animals↗
PubMed1997

Gas chromatographic-mass spectrometric determination of benzo[a]pyrene and chrysene diol epoxide globin adducts in humans.

The efficacy of a newly developed gas chromatography-negative ion chemical ionization-mass spectrometry-selected ion monitoring (GC-NICI-MS-SIM) assay for measuring globin adducts of benzo[a]pyrene (B[a]P) and chrysene diol epoxides in human was evaluated. In this pilot study, smokers and nonsmokers were selected as exposed and nonexposed groups. Using [2H12]r-7,t-8,9,c-10-tetrahydroxy-7,8,9,10-tetrahydrobenzo[a]pyren e ([2H12]trans,anti-B[a]P-tetraol) as an internal standard, B[a]P-tetraols released from globin after hydrolysis and derivatization were quantified by GC-NICI-MS-SIM. Levels of trans-1,2-dihydroxy-3,4-epoxy-1,2,3,4-tetrahydrochrysene (chrysene-DE)-globin adducts were estimated by assuming that the recovery and the MS response of the perdeuterated B[a]P-tetraol internal standard reflected the recovery and MS response of chrysene tetraols. The assay was found to be reproducible and sensitive enough to detect both analytes in all samples. The mean levels of B[a]P-tetraols released from the corresponding benzo[a]pyrene diol epoxide (BPDE) globin adducts in smokers were significantly higher than those in nonsmokers, i.e., 2.6 +/- 0.6 SE fmol/mg globin (ranging from 1.2 to 7.8 fmol/mg globin) in smokers and 0.97 +/- 0.05 SE fmol/mg globin (ranging from 0.7 to 1.3 fmol/mg globin) in nonsmokers (P < 0.01). Interestingly, estimated levels of chrysene-DE-globin adducts in the same subjects were about two orders of magnitude higher than those of the globin adducts of BPDE. The mean of the chrysene-DE adducts in smokers was estimated to be 310 +/- 30 SE fmol/mg globin (ranging from 190 to 460 fmol/mg globin) and that in nonsmokers was 250 +/- 25 SE fmol/mg globin (ranging from 110 to 380 fmol/mg). Although the estimated mean of chrysene-DE adducts with globin in smokers appeared to be about 25% higher than in nonsmokers, the difference was not significant (P = 0.06). The results of this study demonstrate the feasibility of the GC-NICI-MS-SIM method for measurement of BPDE globin adducts in humans.

Benzopyrenes↗
PubMed2002

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.

Journal Article↗
PubMedDate not supplied

Lethality and EROD-inducing potency of chlorinated chrysene in chick embryos.

Chrysene was non-specifically chlorinated and the toxic potency of the mixture formed was studied. The chlorinated mixture was considerably more potent than the parent compound in terms of embryolethality and EROD and AHH induction in a 2-week test in chick embryos. The chlorinated chrysene caused anomalies, including edema and beak defects, similar to those previously found after treatment of chick embryos with coplanar PCBs. Chlorinated chrysene was also much more potent than chrysene as an inducer of EROD in a 72-hour test in chick embryos in ovo and in chick embryo liver in vitro. It seems that the mechanism of toxicity of chlorinated chrysene in chick embryos is similar to that of the coplanar PCBs and other Ah receptor ligands. The effects of the chlorinated mixture were mainly accounted for by 6- chlorochrysene and 6,12-dichlorochrysene.

Animals↗
PubMed1985

Methylene-bridged bay region chrysene and phenanthrene derivatives and their keto-analogs: mutagenicity in Salmonella typhimurium and tumor-initiating activity on mouse skin.

A series of methylene-bridged and keto-bridged bay region derivatives of chrysene and phenanthrene were prepared and evaluated for mutagenic activity in Salmonella typhimurium TA100 and for tumor-initiating activity on CD-1 mouse skin. The compounds included in this series were 4H-cyclopenta[def]phenanthrene, 4H-cyclopenta[def]phenanthrene-4-one, 1-methyl-4H-cyclopenta[def]phenanthrene, 1-methyl-4H-cyclopenta[def] phenanthren-4-one, 4H-cyclopenta[def] chrysene, and 4H-cyclopenta[def] chrysen-4-one. Among these compounds only 4H-cyclopenta[def]phenanthrene and 1-methyl-4H-cyclopenta[def]phenanthren-4-one were not significantly mutagenic when assayed with metabolic activation using Aroclor-induced rat liver homogenate. None of the compounds assayed were active without metabolic activation. 4H-Cyclopenta[def]chrysene was the most tumorigenic of the methylene-bridged bay region PAH tested on mouse skin. At a dose of 1.0 mg this compound resulted in 100% of the animals bearing papillomas with 5.63 papillomas/animal. 4H-Cyclopenta[def]chrysen-4-one and 1-methyl-4H-cyclopenta[def]phenanthrene displayed weak tumorigenic activity at a total initiating dose of 1.0 mg.

Animals↗
PubMed1985

Comparative studies of the metabolic activation of chrysene in rodent and human skin.

Metabolism and activation of chrysene was examined in mouse, rat and human skin using a short-term organ culture technique. Mouse skin released larger quantities of free dihydrodiols into the culture medium than either rat or human skin and greater quantities of chrysene metabolites became covalently bound to the DNA of mouse skin. The stereochemistry of the chrysene-1,2-diol that was formed by each skin type was examined using high-performance liquid chromatography (HPLC) with a chiral stationary phase to resolve the enantiomers. It was found that in each case the (-)-enantiomer predominated. When hydrolysates of DNA extracted from rodent or human skin that had been treated with 3H-labelled chrysene were chromatographed on Sephadex LH-20 columns, the elution profiles of the hydrocarbon-DNA adducts were found to vary between the species studied. Further examination using HPLC showed that some of the adducts formed in skin had the chromatographic characteristics of adducts formed when the anti-isomer of the 'bay-region' diol-epoxide of chrysene (r-1,t-2-dihydroxy-t-3,4-oxy-1,2,3,4-tetrahydrochrysene) reacted with DNA and that others had the characteristics of triol-epoxide adducts.

Animals↗
PubMed1979

Induction of aryl hydrocarbon hydroxylase in human peripheral blood lymphocytes by chrysene.

Many of the polycyclic aromatic hydrocarbons (e.g., benzo[a]pyrene (B[a]P), benzanthracene (BA), 3-methylcholanthrene (3-MC)) are not only carcinogenic, but also induce AHH in human tissues. Recently, chrysene has been implicated as an etiologic determinant of chemical carcinogenesis. Here we describe the ability of chrysene to induce AHH in cultured human lymphocytes. Lymphocytes were obtained from 9 healthy subjects, divided into 2 sets, and cultured in duplicate, triplicate, or quadruplicate for 48 h. Chrysene (25 microM final concentration) in acetone was then added to the induced culture set and the control set received acetone alone. Lymphocytes were then cultured an additional 24 h before harvesting. AHH was quantitated by a fluorometric analysis of the phenolic metabolites produced by incubating the lymphocytes with B[a]P for 35 min. A significant increase in enzyme induction occurred in the chrysene-induced cultures compared with control (non-induced) cells (one-tailed student t-test; P less than 0.001). It was also observed that the interindividual variation in AHH inducibility seen with other PAHs is also observed with chrysene.

Aryl Hydrocarbon Hydroxylases↗
PubMed2006

Mobilization of chrysene from soil in a model digestive system.

Accurate estimates for the oral bioavailability of hydrophobic contaminants bound to solid matrices are challenging to obtain because of sorption to organic matter. The purpose of this research was to measure the bioavailability of [14C]chrysene sorbed to soil using an in vitro model of gastrointestinal digestion and absorption to a surrogate intestinal membrane, ethylene vinyl acetate (EVA) thin film. The [14C]chrysene moved rapidly from soil into the aqueous compartment and reached steady state within 2 h. Equilibrium was reached in the EVA film within 32 h. Aging the spiked soil for 6 or 12 months had no effect on chrysene mobilization. This was supported by the finding that the data best fit a one-compartment model. Despite significant decreases in [14C]chrysene mobilization when water or nonneutralized gastrointestinal fluids were used in place of the complete medium, the equilibrium concentration of [14C]chrysene in EVA film remained the same in all conditions. Thus, the driving force for uptake was the fugacity gradient between the aqueous phase and the EVA film. Cultured human enterocytes (human colorectal carcinoma cell line [Caco-2 cells]) had a higher lipid-normalized fugacity capacity than EVA film, but the elimination rate constants were the same, suggesting that the rate was controlled by the resistance of the unstirred aqueous layer at the membrane-water interface.

Caco-2 Cells↗
PubMed1998

DNA adduct levels associated with p53 induction and delay of MCF-7 cells in S phase after exposure to benzo[g]chrysene dihydrodiol epoxide enantiomers.

Optically active isomers of a mammary carcinogen, anti-benzo[g]chrysene 11, 12-dihydrodiol 13, 14-epoxide, react to different extents with DNA and generate DNA adducts that differ in their stereochemistry. In the study reported here, the effect of these two enantiomers on the progress of human breast carcinoma MCF-7 cells through the cell cycle was investigated. Each enantiomer caused the cells to accumulate in the S phase, but a higher dose of the benzo[g]chrysene 11S, 12R-dihydrodiol 13R, 14S-epoxide than of its enantiomer was required to induce this effect. Similarly, induction of p53 also required a higher dose of benzo[g]chrysene 11S, 12R-dihydrodiol 13R, 14S-epoxide. Postlabeling studies indicated that the latter enantiomer also caused less modification of MCF-7 cell DNA for a given level of exposure than did benzo[g]chrysene 11R, 12S-dihydrodiol 13S, 14R-epoxide. These results suggest that p53 induction and delay in the S phase are similarly related to DNA binding and that a level of binding of the order of 1 adduct per 10(5) nucleotides is associated with these effects.

Chrysenes↗