Search PubMed⌕ Search

SEARCH · Search PubMed

Results for “Chrysenes”

Search indexed PubMed citations on genomics, clinical trials, systematic reviews and public health. Explore titles, authors and supplied subject terms, then open the PubMed record.

Quote a phrase for an exact phrase match. Source license links do not imply unrestricted reuse.

At least 109 records · Page 6Linked to original sources

Vibrational and electronic absorption spectroscopy of dibenzo[b,def]chrysene and its ions.

The vibrational and electronic absorption spectra of dibenzo[b,def]chrysene (DBC) and its ions in argon matrixes have been recorded. Assignment of the observed infrared (IR) bands has been made by comparison with the density functional theory (DFT) computations of harmonic vibrational frequencies (with 6-31G(d,p) or 6-311+G(d,p) basis sets). Extensive time-dependent (TD) DFT calculations of vertical excitation energies have aided in the assignment of the experimental electronic absorption transitions. In general, the theoretical predictions are in good agreement with the observed ultraviolet and visible bands. By correlating IR and UV-visible band intensities (after UV photolysis), it has been shown that both DBC cations and anions are formed. The IR band intensity distributions of the DBC ions differ markedly from neutral DBC. A synthetic spectrum composed of neutral, cationic, and anionic DBC contributions compares reasonably well with the interstellar features of the "unidentified infrared" (UIR) bands from the reflection nebula NGC 7023. Finally, it is shown that the electronic absorption bands of the DBC ions lie in close proximity to several of the diffuse interstellar visible absorption bands (DIBs).

Chrysenes↗

Infrared spectroscopy of matrix-isolated polycyclic aromatic hydrocarbon cations. 4. The tetracyclic PAH isomers chrysene and 1,2-benzanthracene.

The mid-infrared spectra of the polycyclic aromatic hydrocarbon (PAH) cations of the tetracyclic isomers chrysene (C18H12+) and 1,2-benzanthracene (C18H12+) are presented. As with previous PAH cations studied to date, the CC stretching and CH in-plane bending mode absorptions are about an order of magnitude stronger than the aromatic CH out-of-plane bending absorptions and nearly 2 orders of magnitude more intense than the corresponding bands in the neutral molecule. The CH bands arising from the out-of-plane bends in the cation are slightly weaker than the corresponding bands in the neutral species. The strongest cation bands of these species fall between 1300 and 1330 cm-1, close to the peak of the most intense interstellar emission feature in HII regions and reflection nebulae. A strong PAH cation band at slightly higher frequency than 1300 cm-1 may be associated with an asymmetric CC stretching vibration involving rings adjacent to the kink in the chain of aromatic rings.

Argon↗

Identification of an in vivo chrysene diol epoxide adduct in human hemoglobin.

Human blood samples were analyzed by fluorescence and mass spectrometry for the presence of polycyclic aromatic hydrocarbon metabolites covalently bound to hemoglobin. Globin was prepared by HCl-acetone precipitation and enzymatically digested. The polycyclic aromatic alcohols generated from ester adducts during digestion were concentrated by monoclonal antibody immunoaffinity chromatography and separated by C-18 HPLC. Analysis of collected fractions by room temperature fluorescence spectroscopy revealed the presence of the anti-tetrahydrotetrols of benzo[a]pyrene and another component possessing a phenanthrene chromophore. Gas chromatographic-mass spectral analysis of the HPLC fractions revealed that the latter compound was r-1,t-2,t-3,c-4-tetrahydroxy-1,2,3,4-tetrahydrochrysene, arising from a hemoglobin-chrysene diol epoxide adduct.

Chromatography, High Pressure Liquid↗

Reaction with DNA and mutagenic specificity of syn-benzo[g]chrysene 11,12-dihydrodiol 13,14-epoxide.

The spectroscopic characterization of purine deoxyribonucleoside adducts derived from the fjord-region syn-benzo[g]chrysene 11,12-dihydrodiol 13,14-epoxide and the mutagenic specificity of the latter compound for the supF gene in the pSP189 shuttle vector are described. This dihydrodiol epoxide preferentially forms adducts with deoxyadenosine residues in DNA and is preferentially opened trans in reactions with DNA or with deoxyribonucleotides. In common with other fjord-region syn-dihydrodiol epoxides, the most frequently observed mutational changes were A-->T and G-->T changes. This hydrocarbon dihydrodiol epoxide is structurally similar to syn-benzo[c]phenanthrene 3,4-dihydrodiol 1,2-epoxide but has an additional benzene ring annelated distant from the reaction center. As anticipated, there were some common features in the chemistry and mutagenicities of these two compounds, but there were also substantive differences which indicate factors of importance in controlling reactions of these kinds of compounds with DNA.

Animals↗

Synthesis, in vitro metabolism, cell transformation, mutagenicity, and DNA adduction of dibenzo[c,mno]chrysene.

Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous environmental pollutants. Due to its structural similarity with the potent carcinogen dibenzo[a,l]pyrene (DB[a,l]P) and because of its environmental presence, dibenzo[c,mno]chrysene (naphtho[1,2-a]pyrene, N[1,2-a]P) is of considerable research interest. We therefore developed an efficient synthesis of N[1,2-a]P, and examined its in vitro metabolism by male Sprague Dawley rat liver S9 fraction. Its mutagenic activity in S. typhimurium TA 100 and its morphological cell transforming ability in mouse embryo fibroblasts were evaluated. On the basis of spectral analyses, the in vitro major metabolites were identified as the fjord region dihydrodiol trans-9,10-dihydroxy-9,10-dihydro-N[1,2-a]P (N[1,2-a]P-9,10-dihydrodiol), the K-region diols N[1,2-a]P-4,5-dihydrodiol and N[1,2-a]P-7,8-dihydrodiol, and also the 1-, 3-, and 10-hydroxy-N[1,2-a]P; the structure of N[1,2-a]P-9,10-dihydrodiol was also confirmed by independent synthesis. In assays with S. typhimurium TA 100, N[1,2-a]P-9,10-dihydrodiol was half as mutagenic as (+/-)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene (B[a]P-7,8-dihydrodiol) at > or =4 nmol/plate. N[1,2-a]P-9,10-dihydrodiol was much more mutagenic than N[1,2-a]P at all dose levels, suggesting that the N[1,2-a]P-9,10-dihydrodiol is the likely proximate mutagen of N[1,2-a]P. Evaluation of morphological cell transformation in C3H10T1/2C18 mouse embryo fibroblasts revealed that N[1,2-a]P was comparable to B[a]P. We further examined the pattern of in vitro adduct formation between calf thymus DNA and (+/-)-anti-9,10-dihydroxy-9,10-dihydro-11,12-epoxy-9,10,11,12-tetrahydro-N[1,2-a]P (N[1,2-a]PDE) and found that dG-adduct formation is 2.9-fold greater than dA-adduct formation. On the basis of our results and those reported in the literature, our working hypothesis is that N[1,2-a]P may be added to the list of potent carcinogens that includes DB[a,l]P. This hypothesis is currently being tested in our laboratory.

Animals↗

Synthesis and identification of major metabolites of environmental pollutant dibenzo[c,mno]chrysene.

Dibenzo[c,mno]chrysene commonly known as naphtho[1,2-a]pyrene (N[1,2-a]P) is an environmental pollutant, recently identified in coal tar extract, in air-borne particulate matter, in marine sediment, and in cigarette-smoke condensate. We recently reported an efficient synthesis of N[1,2-a]P and examined its in vitro metabolism by male Sprague Dawley rat liver S9 fraction, which resulted in a number of dihydrodiol and phenolic metabolites. The synthesis of 10-hydroxy-N[1,2-a]P and fjord region N[1,2-a]P trans-9,10-dihydrodiol, which were identified among the various metabolites, was assigned earlier by comparing with the synthetic standards. The other major metabolites were separated by HPLC and, based on the 1H NMR analysis, were tentatively suggested to be the two K-region dihydrodiols, that is, N[1,2-a]P trans-4,5-dihydrodiol (6) and N[1,2-a]P trans-7,8-dihydrodiol (7), and the hydroxy derivatives of N[1,2-a]P. To unequivocally assign the structure to each of the peaks and to have them in larger amounts for toxicological studies, we have now synthesized the two K-region dihydrodiols and the 1-/3-hydroxy-N[1,2-a]P, short-listed based on the proton NMR of the collected peaks. The K-region dihydrodiols 6 and 7 were prepared by the treatment of N[1,2-a]P with OsO(4) to give a mixture of cis dihydrodiols 2 and 3, followed by pyridinium chlorochromate-assisted oxidation to quinones 4 and 5, and finally reduction with NaBH(4) to afford the dihydrodiols 6 and 7 with the desired trans stereochemistry. The 1-hydroxy-N[1,2-a]P (22) and 3-hydroxy-N[1,2-a]P (23) were synthesized using a photochemical approach. As expected, all the synthesized dihydrodiol and phenolic derivatives of N[1,2-a]P identified with those obtained from in vitro metabolism enabling the assignment of all the major metabolites.

Chromatography, High Pressure Liquid↗

Studies in the biodegradation of 5 PAHs (phenanthrene, pyrene, fluoranthene, chrysene und benzo(a)pyrene) in the presence of rooted poplar cuttings.

Cuttings of Populus nigra L. cv. Loenen were cultivated in sand treated with one of the following PAHs: phenanthrene (Phen), fluoranthene (Flt), pyrene (Pyr), chrysene (Chr) and benzo[a]pyrene (BaP). The PAHs were applied at varying levels of concentration to each test series. After 6 weeks the concentration and the distribution of the PAHs in the substrate of the various sets of tests were compared with the concentration in the substrate of the control. Additionally the substrate and the plant roots were tested for evidence of degradation products of PAHs. The results revealed that the levels of concentration of Phen and Pyr detected in the substrate surrounding the roots was in some cases significantly lower than in the corresponding section of substrate in the unplanted set (= control). This phenomenon did not occur for Flt and BaP and in the case of Chr only in those substrates, which had been treated with the highest levels of concentration. As the presence of lesser amounts of Phen and Pyr in the plant pots cannot only be attributed to their accumulation and metabolism in the roots, it is fair to assume that the chemical transformation of these three PAHs took place outside the roots. The set of tests treated with Phen revealed the presence of 2- or 3-hydroxy-Phen (main components), a hydroxy-methoxy-Phen, 9,10-Phenanthrenequinone and one unidentified compound in metabolite form. Altogether eleven metabolites of Pyr were identified in the root extracts, which can be divided into three groups: 1-Hydroxy-Pyr and derivatives, dihydroxy-Pyr and derivatives and ring fission products (4-Hydroxy-Pyr and a derivative of the 4-Phen-carbonic acid). However, the metabolite mass detected for Phen and Pyr represents only an insignificant percentage in comparison with the lesser amounts of PAHs observed in the planted set of tests. This indicates that the three PAHs were reduced to lower molecular compounds, which are methodically impossible to record, and subsequently translocated to other parts of the plant and integrated into the biomass. Although no lesser amount for Flt and BaP was found in the plant pots, 1-Hydroxy-Flt, an unidentified compound of Flt and 1-Methoxy-BaP were detected. These are presumably end products which were enhanced in the roots. It was not possible to identify any transformation products of Chr. It can be assumed that the majority of metabolites were not synthesised in the roots but are a result of microbial degradation in the rhizosphere. The test plants improved the conditions for the biotransformation of Phen and Pyr significantly and accumulated Flt, Pyr, Chr and BaP in their roots. It can therefore be concluded that the use of plants in the bioremediation of contaminated soils is a promising option.

Benzo(a)pyrene↗

Mammary carcinogenicity in female CD rats of fjord region diol epoxides of benzo[c]phenanthrene, benzo[g]chrysene and dibenzo[a,l]pyrene.

We compared the mammary carcinogenicity in female CD rats of three fjord region diol epoxides to test our hypothesis that such sterically hindered molecules would be potent carcinogens. The diol epoxides tested were racemic anti-3,4-dihydroxy-1,2-epoxy-1,2,3,4-tetrahydrobenzo[c]phenanthrene (BcPDE), anti-11,12-dihydroxy-13,14-epoxy-11,12,13,14-tetrahydrobenzo[g]chrysene (BgCDE) and anti-11,12-dihydroxy-13,14-epoxy-11,12,13,14-tetrahydrodibenzo[a,l ]pyrene (DB[a,l]PDE). Each diol epoxide was dissolved in dimethylsulfoxide (DMSO) and injected under the six nipples on the left side of the rat, with DMSO only being injected under the nipples on the right side. The total dose of each diol epoxide was 1.2 mumol/rat and there were 20 rats/group. The experiment was terminated 41 weeks after treatment. All three diol epoxides were potent mammary carcinogens, with activity greater than previously observed for a bay region diol epoxide, anti-7,8-dihydroxy-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BPDE). DB[a,l]PDE induced tumors most rapidly, followed by BcPDE and BgCDE. However, different types of tumors were induced. For induction of adenomas and adenocarcinomas, BcPDE and BgCDE had comparable potency; both were more active than DB[a,l]PDE. In contrast, for induction of sarcomas, DB[a,l]PDE was significantly more active than BcPDE and BgCDE. The results of this study support our hypothesis that sterically hindered fjord region diol epoxides are potent mammary carcinogens in the rat.

7,8-Dihydro-7,8-dihydroxybenzo(a)pyrene 9,10-oxide↗

Metabolic activation of chrysene by hamster embryo cells: evidence for the formation of a 'bay-region' diol-epoxide-N2-guanine adduct in RNA.

Ribonucleoside-hydrocarbon adducts present in hydrolysates of RNA isolated from hamster embryo cells treated with 3H-labelled chrysene were examined by chromatography on Sephadex LH20 and by h.p.l.c. on Zorbax ODS. Two adducts formed in cells had chromatographic properties identical to those of two synthetic adducts formed when r-1,t-2-dihydroxy-t-3,4-oxy-1,2,3,4-tetrahydrochrysene (antichrysene 1,2-diol 3,4-oxide) reacted with poly G in vitro. Another adduct formed in cells had chromatographic properties identical to those of a synthetic adduct formed when antichrysene 1,2-diol 3,4-oxide reacted with poly A. In addition to the characterized adducts, other minor adducts were detected whose structures are not known. The structure of the more abundant guanosine--hydrocarbon adduct formed in cells was investigated by determining its pK values and stability in 1 M KOH. The structures of the synthetic guanosine--hydrocarbon adducts were investigated by 1H-n.m.r. spectroscopy. The data show that, in the hydrocarbon--guanosine adducts studied, the hydrocarbon moiety is attached to the exocyclic amino group of guanine.

Animals↗

Tumorigenicity of nitrated derivatives of pyrene, benz[a]anthracene, chrysene and benzo[a]pyrene in the newborn mouse assay.

Eight nitropolycyclic aromatic hydrocarbons (PAHs), including 1- and 4-nitropyrene, 1,3-, 1,6- and 1,8-dinitropyrene, 7-nitrobenz[a]anthracene, 6-nitrochrysene and 6-nitrobenzo-[a]pyrene and their parent PAHs were tested fro tumorigenicity in the newborn mouse model by i.p. administration at 1, 8, and 15 days after birth. Both pyrene and 1-nitropyrene induced similar incidences of hepatic tumors in males, yielding a 12-15% and a 21-28% tumor incidence at total doses of 700 and 2800 nmol per mouse, respectively. Liver tumors did not occur in females and the 3-10% lung tumor yield in both sexes was similar to that found in solvent-treated controls. The presumed proximate carcinogen, 1-nitrosopyrene, administered at 700 nmol per mouse, caused liver tumors in 45% of the males and in 9% of the females. 4-Nitropyrene was more tumorigenic than pyrene or 1-nitropyrene; at a dose of 2800 nmol, it induced liver tumors in 83% of the males and 7% of the females, with a lung tumor yield of 38 and 31%, respectively. Female mice treated with 200 nmol of 1,3-, 1,6- or 1,8-dinitropyrene did not develop liver tumors but the hepatic tumor incidence in males was 20, 32 and 16%, respectively, which was significantly greater than that found in mice treated with pyrene. In male mice administered 2800 nmol of benz[a]anthracene, the hepatic tumor incidence was 79%, while treatment with 7-nitrobenz[a]anthracene showed an incidence of only 28%. Similarly, 560 nmol of benzo[a]pyrene caused a 49% liver tumor yield in males while those given 6-nitrobenzo[a]pyrene had a 28% incidence. Treatment with benzo[a]pyrene also induced a 35 and 48% lung tumor incidence in males and females while the comparable values in 6-nitrobenzo[a]pyrene-treated mice were 14 and 2%. Chrysene administered at 2800 nmol per mouse induced hepatic and lung tumors in 41% and 21% of the males, respectively; at the 700-nmol dose, it induced only liver tumors in 29% of the males and in none of the females. In contrast, treatment with 6-nitrochrysene at 700 nmol per mouse resulted in a 76 and 23% hepatic tumor incidence in males and females, respectively.(ABSTRACT TRUNCATED AT 400 WORDS)

Animals↗

Synthesis and mutagenicity of 5-alkyl-substituted chrysene-1,2-diol-3,4-epoxides.

In order to explore the relationship between structure and mutagenicity of bay region diol-epoxides of chrysene substituted with an alkyl group in the bay region, we compared the mutagenicity in Salmonella typhimurium TA 100 of anti-1,2-dihydroxy-3,4-epoxy-1,2,3,4-tetrahydrochrysene with its 5-methyl, 5-ethyl and 5-propyl derivatives. The results showed that anti-1,2-dihydroxy-3,4-epoxy-1,2,3,4-tetrahydro-5-methylchrysene (7400 revertants/nmol) was the most mutagenic of these diol-epoxides followed by anti-1,2-dihydroxy-3,4-epoxy-1,2,3,4-tetrahydrochrysene and its 5-ethyl derivative (1100 revertants/nmol). The 5-propyl substituted diol-epoxide was inactive at the doses tested. The results demonstrate that steric factors are dominant in the expression of methylchrysene diol-epoxide mutagenicity in S. typhimurium and suggest that the molecular shape of the 5-methyl substituted diol-epoxide leads to a unique reaction with DNA associated with high mutagenicity and tumorigenicity.

Chrysenes↗

6-Amino-chrysene, a potent inhibitor of transferase activity in single living RTG2 cells.

Previous reports on the inhibitory effect of 6-amino-chrysene (6AC) on benzo(a)pyrene (BP) metabolism using single living cells have suggested that aryl hydrocarbon hydroxylase (AHH) is not the only pathway for 6AC metabolism. We present here results demonstrating that direct glucuronidation may constitute an alternative pathway for 6AC elimination. First, we describe the conjugate of 6AC to UDP-glucuronic acid (UDPGA) in solution. We performed competition experiments between 6AC and monohydroxy BP, which are known to be good substrates for glucuronic transferase (GT), in RTG2 cells, using microspectrofluorimetry. Because of intracellular accumulation of fluorescent metabolites during BP metabolism, RTG2 cells can be used as a tool for simultaneous study of AHH and GT activities. When RTG2 cells have been simultaneously treated with BP and 6AC, GT appeared to be a more specific target for 6AC than AHH in these cells. Therefore, 6AC can be expected to act as a more specific inhibitor for GT than for AHH activity.

Animals↗

Mono- and diglucuronide formation from chrysene and benzo(a)pyrene phenols by 3-methylcholanthrene-inducible phenol UDP-glucuronosyltransferase (UGT1A1).

Mono- and diphenols of chrysene and benzo(a)pyrene are suspected substrates of a 3-methylcholanthrene (MC)-inducible phenol UDP-glucuronosyltransferase (UGT1A1). Mono- and diglucuronide formation from these compounds was studied in two systems, (a) livers of MC-treated rats (homologous expression) and (b) a Chinese hamster lung fibroblast cell line (V79) containing rat UGT1A1 cDNA and stably expressing this isozyme (heterologous expression). In liver microsomes of MC-treated rats, glucuronidation of 6-hydroxychrysene was stimulated 11-fold by MC treatment. With 3,6-dihydroxychrysene, formation of its 3-hydroxy-6-monoglucuronide and of the diglucuronide was increased 24- and 310-fold, respectively. Induction factors obtained for monoglucuronide formation (but not for diglucuronide formation) were in line with published data on the increase of immunodetectable UGT1A1 protein and of its mRNA. It is suggested that the high induction factors for diglucuronide formation are the result of a combination of the induction of UGT1A1 and facilitated interaction of neighboring UGT1A1 molecules in endoplasmic reticulum membranes. Glucuronidation of 6-hydroxychrysene, 3-hydroxybenzo(a)pyrene, and 3,6-dihydroxybenzo(a)pyrene to their mono- and diglucuronides was clearly detectable in V79 cells expressing UGT1A1. However, conjugation of 3,6-dihydroxychrysene to its monoglucuronides was low and diglucuronide formation was not detectable, suggesting that UGT isozymes other than UGT1A1 are responsible for these reactions.

Animals↗

Studies on sex related differences in elimination of theophylline in the rat after pretreatment with phenobarbital, chrysene, Aroclor 1254 or lindane.

Cytochrome P-450 in liver microsomes plays a central role as a drug metabolizing enzyme. The sex-dependent differences in the properties of cytochrome P-450 have been extensively studied using liver microsomes, and marked differences have been found in microsomal metabolism of xenobiotic. Effect of pretreatment with phenobarbital, chrysene, lindane and polychlorinated biphenyls (Aroclor 1254) on the theophylline elimination in male and female rats was studied. Levels of theophylline were measured spectrophotometrically.

Aminophylline↗

Evaluation of the mutagenicity of compounds of known carcinogenicity, belonging to the benz[a]anthracene, chrysene, and cyclopenta[a]phenanthrene series, using Ames's test.

Fifty-four polycyclic compounds, 29 of the cyclopenta[a]phenanthrene series, 11 chrysenes, and 14 benz[a]anthracenes, have been tested for mutagenicity by Ames's method, using Salmonella typhimurium TA100. Without exception all 37 carcinogens and a known initiator were mutagens. Of the 16 noncarcinogens 7 were mutagenic, but none of these has yet been tested for initiating, as opposed to carcinogenic, activity. There appeared to be little quantitative correspondence between carcinogenic and mutagenic potency, however, and possible reasons for this are discussed. The aryl hydrocarbon hydroxylase inhibitor 7,8-benzoflavone strongly inhibited the mutagenicity of certain compounds when it was added to the incubations.

Animals↗

Correlations between topological resonance energy of methyl-substituted benz[c]acridines, benzo[a]phenothiazines and chrysenes, and their carcinogenic or antitumor activities.

In order to clarify the effects of methyl substitution on the carcinogenic activity, each resonance energy (RE) of benz[c]acridines, benzo[a]phenothiazines, chrysene, and their methyl derivatives was calculated by Aihara's TRE theory. Some correlations seem to exist between the values of resonance energy per pi-electron for the cationic species-with the lack of the atom having the highest approximate superdelocalizability (Sr'(E)) from their parents skeleton-and carcinogenic activity.

Acridines↗