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D Warshawsky

Publications and source records attributed to D Warshawsky.

At least 55 records · Page 3Linked to original sources

Influence of particle dose on the cytotoxicity of hamster and rat pulmonary alveolar macrophage in vitro.

Silica and ferric oxide are common industrial exposures. Studies have indicated that all commonly occurring forms of crystalline silica can cause fibrotic lung disease. There is evidence to indicate that crystalline silica is carcinogenic in humans who have not developed silicosis, while amorphous silica is not carcinogenic in humans. An important biological response to particles deposited deep in the lung is their engulfment by pulmonary alveolar macrophages (AM). To assess the role of AM in silica-induced lung disease, particle size distribution and surface area of crystalline, gelled, precipitated, and fumed silica, ferric oxide, and aluminum oxide were characterized; the cytotoxicity of the particles to hamster and rat AM in vitro was measured at 0.0-0.5 mg/1 x 10(6) cells at 24 and 48 h using dye exclusion procedures. The count medium diameter for aluminum oxide, ferric oxide, and amorphous silica was equal to or less than 0.38 microns, while for crystalline silica the value was 0.83 microns. The surface areas for the amorphous silicas and the aluminum oxide ranged from 253 to 125 m2/g with gelled silica having the highest value; the values for crystalline silica and ferric oxide were 4.3 and 10.8 m2/g, respectively. Crystalline silica (1.6%) was detected in the fumed silica, while none was detected in precipitated or gelled silica. With gelled silica, based on the dose of the particle, the viability of the hamster AM decreased to 27% at 0.05 mg and to zero at 0.1 mg at 24 h. At doses of 0.05 and 0.1 mg of crystalline, precipitated, or fumed silica, the percent viability decreased significantly to 76-67% and 51-42%, respectively, and to zero at 0.5 mg. Macrophages viable at 24 h decreased further at 48 h compared with the control culture. The ferric oxide and the aluminum oxide showed minimal to no changes in viability. Similar results for the particles were obtained with rat AM. The results indicate that precipitated and fumed amorphous silica tested at equivalent doses are equally as toxic to AM lavaged from two species of rodents as crystalline silica; gelled silica is more toxic than crystalline. Ferric oxide and aluminum oxide are noncytotoxic in this system. The results of this study indicate that the dose as well as the surface area and surface characterization are important determinants in the cytotoxicity of hamster and rat AM to these particles.

Aluminum Oxide↗

Comparison of blood protein and target organ DNA and protein binding following topical application of benzo[a]pyrene and 7H-dibenzo[c,g]carbazole to mice.

7H-Dibenzo[c,g]carbazole (DBC) induces skin and liver tumors in mice following topical application, whereas benzo[a]pyrene (BP) induces only skin tumors. DBC also binds to liver DNA to a much greater extent than does BP. The present study examined factors that might account for the difference in DNA binding activity. [3H]DBC was applied topically to CD-1 mice at doses of 15, 100 and 1000 nmol/mouse and tissues and blood samples were taken 24 h later. Absorption of DBC from skin into blood and binding to blood proteins occurred linearly with dose. DBC bound to albumin at a 50-fold higher level than to globin and levels of albumin adducts showed good correlation with levels of DNA adducts in liver. Hepatic preference over skin in DNA binding was found to be dose-dependent. For comparison of [3H]BP and [3H]DBC binding, doses of 1000 nmol/mouse were used and the mice were sacrificed at 12, 24 and 48 h. The rate of DBC uptake from skin was 70% higher than for BP over the first 24 h, which was reflected in 40-50% higher plasma levels of DBC radiolabel. Skin protein and DNA binding were 2- to 5-fold higher for BP than DBC. Conversely, total 3H radioactivity levels in liver were 2- to 3-fold higher and liver DNA and protein binding were 15- to 20-fold and 3- to 5-fold higher respectively for DBC. Blood protein adduct levels were similar for both chemicals, suggesting that DBC metabolites formed in the liver were too reactive to re-enter the systemic circulation. Only minor amounts of the radiolabel in the liver were present as the parent compounds by 12 h after dosing. These results indicate that more rapid absorption from skin and selective accumulation in the liver contribute to the greater liver DNA binding seen with DBC, but the types of liver metabolites appear to be the major factor accounting for the binding difference.

Acetates↗

Factors affecting carcinogenic potential of mixtures.

Historically, exposure to complex mixtures such as soot, coal tar, mineral oils, and cigarette smoke has been associated with increased cancer mortality. Benzo[a]pyrene (BaP) has been used to predict the carcinogenic potency of mixtures. Two complete carcinogenicity C3H/HEJ mouse skin bioassays were undertaken to determine the effect of low doses of BaP on the carcinogenic potential of mixtures. A toluene solution containing 0.1% each of five noncarcinogenic polycyclic aromatic hydrocarbons (PAHs), anthracene, chrysene, pyrene, fluoroanthene, and phenanthrene, produced tumors in 23% of the mice with a latent period of 73 weeks. With the addition of a 0.001% BaP to the above solution, 47% of the mice produced tumors with a latent period of 66 weeks. In the second study, coal tar in toluene, which was determined to contain 0.0006% BaP, produced tumors in 51% of mice with a latent period of 73 weeks. In both studies the BaP solutions by themselves did not produce tumors. In a third study, the 9-, 2-, and 3-methylbenz[a]-anthracene compounds were noncarcinogenic using toluene as the solvent. With the substitution of n-dodecane for toluene all three compounds produced significant numbers of tumors. The results indicate that (1) low dose levels of BaP can have an impact on the carcinogenic potential of mixtures, (2) the presence or absence of BaP is not always sufficient to account for the observed potency and the synergistic effects of other substances which might be present, and (3) that certain noncarcinogenic methylbenz[a]anthracenes can have their carcinogenic potential altered by a change in the solvent used.

Alkanes↗

32P-postlabeling analysis of dibenz[a,j]acridine DNA adducts in mice: preliminary determination of initial genotoxic metabolites and their effect on biomarker levels.

N-Heterocyclic aromatics (NHA) are widely occurring environmental pollutants formed during the pyrolysis of nitrogen-containing organic chemicals. NHA are found in significant amounts in tobacco condensates, synthetic fuels, gasoline engine exhaust, and effluents from the heating of coal. Dibenz[a,j]acridine (DBA) is an example of NHA. The potency of many carcinogenic compounds is related, at least in part, to the efficiency of their biological activation. We undertook studies to determine which initial metabolites of DBA lead to the formation of high levels of carcinogen-DNA adducts in vivo. DBA and its metabolites, trans-DBA-1,2-dihydrodiol (DBA-1,2-DHD), trans-DBA-3,4-dihydrodiol (DBA-3,4-DHD), and trans-DBA-5,6-dihydrodiol (DBA-5,6-DHD), were applied to the skin of mice. DNA was isolated using enzyme-solvent extraction method. DNA was 32P-postlabeled under conditions of limiting [32P]ATP. In skin, DBA produced two distinct adducts. The same two adducts were seen when DBA-3,4-DHD was applied. In addition the total adduct level elicited by DBA-3,4-DHD was higher than that of parent compound. Two adducts were seen when DBA-5,6DHD was applied, but these were very different from adducts seen with DBA. These results suggested that activation of DBA to DNA-binding compounds in skin includes initial formation of DBA-3,4-DHD. The data support development of biomarkers for the exposure and effect of this compound, and also suggest that specific metabolic susceptibility markers might be able to predict populations at increased risk.

Acridines↗

Influence of the dose levels of cocarcinogen ferric oxide on the metabolism of benzo[a]pyrene by pulmonary alveolar macrophages in suspension culture.

The concurrent administration of a cocarcinogenic carrier particle such as ferric oxide (Fe2O3) and the polycyclic aromatic hydrocarbon lung carcinogen benzo[a]pyrene (BaP) results in a decreased latency and an increased incidence in the production of lung tumors in hamsters compared to the administration of BaP alone. The pulmonary alveolar macrophage (AM), the primary lung defense cell, has been shown to endocytize BaP, metabolize BaP to a more biologically active form, and then release the metabolites. Therefore, a study was undertaken to determine in a dose-response manner the effect of AM phagocytosis of a carrier particle (Fe2O3) on the metabolism of a carcinogen (BaP) and on the production of reactive oxygen. The AM were lavaged from hamsters and cultured in suspension (2.5 x 10(6) cells/vial) with BaP (62.5 nmol, 14C labeled) alone or adsorbed onto 0.5, 1.0, or 2.0 mg Fe2O3 in the presence of cytochrome c. Following separate ethyl acetate extractions of the AM and medium, the metabolites were isolated by high-performance liquid chromatography (HPLC) and quantified by liquid scintillation spectrometry. The production of superoxide anions was monitored by the reduction of cytochrome c. Concurrent exposure of AM to BaP-coated Fe2O3 resulted in a significant increase in the amount of BaP metabolites and superoxide anions produced with dose of Fe2O3. The following metabolites were identified in both the medium and the AM: 9,10-dihydrodiol, 7,8-dihydrodiol, 4,5-dihydrodiol, 9-hydroxy, 3-hydroxy, and 3,6-quinone. In general, the 7,8-dihydrodiol, which is considered to be the precursor of the ultimate carcinogenic metabolite of BaP, and superoxide anions, which have been shown to produce localized lipid peroxidation and edema in vivo, were significantly enhanced (p = .05, Duncan's multiple comparison test) in AM exposed to all doses of Fe2O3 when compared to AM exposed to BaP alone. This Fe2O3 dose-related enhancement of superoxide anion production is indicative of increased endocytic capacity resulting in a greater amount of total metabolites being produced, in particular, the dihydrodiols of BaP, which are considered to be products of the active metabolic pathway of BaP.

Animals↗

Comparative metabolism of 7H-dibenzo[c,g]carbazole and dibenz[a,j]acridine by mouse and rat liver microsomes.

The comparative metabolism of the carcinogenic pollutants 7H-dibenzo[c,g]-carbazole (DBC) and dibenz[a,j]acridine (DBA) was investigated in vitro using 3-methylcholanthrene (3MC) induced Sprague-Dawley rat and Hsd:ICR(Br) mouse liver microsomal preparations with benzo[a]pyrene (BaP) as the positive control. Metabolites were isolated and separated by HPLC and identified by spectroscopic and co-chromatographic techniques using synthetic standards. The major metabolites of DBC were the phenols: the 5-OH-DBC, 3-OH-DBC, and 2-OH-DBC. Traces of 1-OH-DBC were also found yet no dihydrodiols were identified. The major metabolites of DBA were the 3,4-diol-DBA and 5,6-diol-DBA, 1,2-diol-DBA, DBA-5,6-oxide and 4-OH-DBA. Treatment of both mice and rats with 3MC resulted in significant (P less than or equal to 0.05) increases relative to control in the microsomal metabolism of DBA to dihydrodiol and phenol metabolites, similar to that observed for BaP. 3MC-induced rat liver microsomes significantly (P less than or equal to 0.05) increased DBC metabolism relative to control microsomes whereas DBC metabolism was not increased with 3MC-induced mouse liver microsomes. These data indicate that different enzymatic pathways are involved in the metabolic activation of DBC in the Hsd:ICR(Br) mouse and Sprague-Dawley rat.

Acridines↗

Comparative tumor-initiating ability of 7H-dibenzo(c,g)carbazole and dibenz(a,j)acridine in mouse skin.

N-heterocyclic aromatics are environmentally important carcinogenic pollutants produced by incomplete combustion of organic material. 7H-Dibenzo-(c,g)carbazole (DBC), is a potent skin and systemic carcinogen, whereas dibenz(a,j)acridine (DBA), is a carcinogen with local effects. Therefore, the overall objective of these studies was to determine the initiating ability of DBC and DBA in mouse skin using an initiation-promotion protocol. Acetone-, TPA- or BaP-treated animals were used as negative and positive controls, respectively. DBC, DBA or BaP (200 nmol) dissolved in acetone was applied once to the backs of thirty shaved Hsd:(ICR)Br female mice, followed 2 weeks later with 2 micrograms of TPA in 50 microliters of acetone applied twice a week for up to 24 weeks. Skin tumors developed in 26, 17 and 27 animals, respectively. DBC plus TPA produced a significant influx of dermal macrophages similar to that seen for BaP. Initiation with BaP, DBC or DBA moderated the effect of TPA on most other dermal parameters, particularly neutrophils. These data indicate that, DBC, with apparently different activation pathways than BaP shows similar tumor initiating ability and morphological changes as BaP.

Acetone↗

Hepatic metabolism of 7,12-dimethylbenz(a)anthracene in male, female, and ovariectomized Sprague-Dawley rats.

Dimethylbenz(a)anthracene (DMBA) is a potent inducer of mammary tumors in intact female Sprague-Dawley rats, but not in males or ovariectomized females (OVX). Qualitative and quantitative aspects of hepatic metabolism of DMBA were examined in these three groups of rats, using the nonrecirculating perfused liver, to determine whether the production of proximate carcinogenic metabolites of DMBA by the liver differed among these groups in the same manner as does sensitivity to tumor induction. DMBA was infused into the liver at a constant rate for 60 min. Rates of appearance of DMBA and its metabolites were measured in perfusate and bile during the infusion period and the first 60 min thereafter. The maximum rate of appearance of total metabolites in the perfusate, seen at the end of the infusion period, was highest in the intact female [2.6 +/- 0.3 nmol/(g x min)], slightly lower in the OVX [2.3 +/- 0.2 nmol/(g x min)] and significantly lower in the male [1.0 +/- 0.1 nmol/(g x min)]. The rates of appearance of metabolites in the bile showed the same order as those seen in the perfusate. The major metabolites extracted from the perfusate in all three groups were dihydrodiols, hydroxymethyl metabolites, and several unidentified metabolites. The 3,4-dihydrodiol, a proximate carcinogenic metabolite, appeared in the perfusate at higher rates in the intact female and OVX than in the male. Hydrolysis of bile samples showed that glucuronidation was a major pathway in the excretion of DMBA metabolites in bile. High performance liquid chromatographic analysis indicated that hydrolysis of DMBA glucuronides yielded the 7- and 12-hydroxymethyl metabolites and an unidentified metabolite designated X. The major hydrolysis product in the male was 12-hydroxymethyl while X was found to be the major product in the intact female and OVX. Under the conditions of this study, there were differences in the metabolic activation of DMBA by male and female rat liver. Ovariectomy, followed by DMBA perfusion 7 days later, did not result in significant changes in DMBA metabolism relative to the intact female, except for a decreased rate of excretion of metabolites in bile.

9,10-Dimethyl-1,2-benzanthracene↗

Comparative metabolism of 7,12-dimethylbenz[a]anthracene by the perfused liver and liver microsomal preparations from Sprague-Dawley rats.

The metabolism of DMBA by microsomes and various cell cultures has been widely studied. However, the biotransformation of this compound by intact organs has not been well characterized. In order to compare the metabolism of DMBA in the whole liver with that in subcellular preparations, we used an in situ single-pass rat liver perfusion system and rat liver microsomes. [14C]DMBA was infused into the livers of Sprague-Dawley rats during the first 60 min of a 120 min perfusion. HPLC analysis of extracts of perfusate samples indicated that DMBA was rapidly oxidized in this system to a series of metabolites. The major products were polar metabolites including the trans-5,6- and the trans-10,11-dihydrodiols (46%), the trans-3,4-dihydrodiol (5%) and the 7-OHM-12-MBA and the 12-OHM-7-MBA metabolites (12%) of DMBA. Microsomes prepared from livers of corn oil treated rats were incubated with [14C]DMBA for 60 min, then extracted. In the microsomal system the major DMBA metabolites were the trans-8,9-dihydrodiol (6%), the 7- and 12-hydroxymethyl (20%), and the 3- and 4-hydroxy (11%) of DMBA with the more polar metabolites and the trans-3,4-dihydrodiol present at lower levels (12 and 3% respectively). This is the first report of DMBA metabolism in a whole liver preparation and the results are clearly different from those obtained in subcellular preparations in our laboratory and in cell culture systems elsewhere. These results have important implications for understanding DMBA biotransformation in vivo.

9,10-Dimethyl-1,2-benzanthracene↗

Indigenous and enhanced mineralization of pyrene, benzo[a]pyrene, and carbazole in soils.

We studied the mineralization of pyrene, carbazole, and benzo[a]pyrene in soils obtained from three abandoned coal gasification plants in southern Illinois. The soils had different histories of past exposure to hydrocarbon contamination and different amounts of total organic carbon, microbial biomass, and microbial activity. Mineralization was measured by using serum bottle radiorespirometry. The levels of indigenous mineralization of 14C-labeled compounds ranged from 10 to 48% for pyrene, from undetectable to 46% for carbazole, and from undetectable to 25% for benzo[a]pyrene following long-term (greater than 180-day) incubations. Pyrene and carbazole were degraded with short or no lag periods in all soils, but benzo[a]pyrene mineralization occurred after a 28-day lag period. Mineralization was not dependent on high levels of microbial biomass and activity in the soils. Bacterial cultures that were capable of degrading pyrene and carbazole were isolated by enrichment, grown in pure culture, and reintroduced into soils. Reintroduction of a pyrene-degrading bacterium enhanced mineralization to a level of 55% within 2 days, compared with a level of 1% for the indigenous population. The carbazole degrader enhanced mineralization to a level of 45% after 7 days in a soil that showed little indigenous carbazole mineralization. The pyrene and carbazole degraders which we isolated were identified as a Mycobacterium sp. and a Xanthamonas sp., respectively. Our results indicated that mineralization of aromatic hydrocarbons can be significantly enhanced by reintroducing isolated polycyclic aromatic hydrocarbon-degrading bacteria.

Bacteria↗

Conjugation of benzo[a]pyrene metabolites by freshwater green alga Selenastrum capricornutum.

Benzo[a]pyrene (BaP) undergoes metabolic transformation in mammals via oxidative, hydrolytic, and conjugative processes; however, little is known concerning BaP conjugation in freshwater algae. It has been shown in this laboratory that BaP is metabolized by Selenastrum capricornutum via a dioxygenase pathway. This study describes the conjugation of BaP metabolites by a green alga, Selenastrum capricornutum. Cultures were exposed to 1160 micrograms/l [14C]BaP for 4 days at 23 degrees C under gold fluorescent lights on a diurnal cycle of 16 h light, 8 h dark. Of the total metabolites in the algal culture, 89% were present in media. BaP and non-conjugated metabolites were separated from conjugated metabolites by chromatography on neutral alumina columns using solvents of increasing polarity. Seventy-one percent of the BaP metabolites were conjugates of which 12.2%, 12.0% and 12.4% were sulfate ester and alpha- and beta-glucose conjugates, respectively. Conjugates that coeluted with sulfate esters were hydrolyzed with arylsulfatase, alpha- or beta-glucosidase; high performance liquid chromatography (HPLC) analysis indicated that the major product of each enzymatic hydrolysis was the 4,5-dihydrodiol (87.2, 69 and 53%, respectively). Eighty-six percent of the conjugates were acid labile following incubation for 2 h in 4 N HCl at 37 degrees C. To our knowledge this is the first demonstration of the metabolism of a polynuclear aromatic hydrocarbon by a freshwater green alga through a dioxygenase pathway and subsequent conjugation and excretion.

Acid Phosphatase↗

Influence of the carcinogenic pollutant benzo[a]pyrene on plant development: fern gametophytes.

Polycyclic aromatic hydrocarbons (PAHs), ubiquitous environmental pollutants, are known to be biologically active in mammalian systems and are accumulated by plants. A few reports suggest that PAHs stimulate growth in plants and induce morphogenesis in plant tissue in culture. To investigate the growth altering abilities of PAHs in plants, polypodiaceous fern gametophytes were grown under sterile conditions on media containing a biologically active PAH, benzo[a]pyrene (BaP), at doses ranging from 0.1 to 10.0 micrograms/ml. The growth pattern of polypodiaceous fern gametophytes enables alterations in growth and morphogenesis to be observed at the cellular level in an intact plant. Doses of BaP in the range 0.1--3.2 micrograms/ml enhanced the onset of the morphological transitions from 1-dimensional (1D) to 2-dimensional (2D) growth. This transition for BaP treated plants occurred after fewer cell divisions than the corresponding solvent and untreated controls. The low (0.1 and 0.32 micrograms) and high (1.0 and 3.2 micrograms) doses of BaP were found to accelerate and inhibit cell proliferation, respectively. The 10.0 microgram dose was toxic and resulted in decreased germination of spores and reduced survival of plants. A slight but significant decrease in survival was also observed in ferns treated with 3.2 micrograms. This is the first example of PAH influencing cell differentiation in a whole plant system.

Benzo(a)pyrene↗

Binding of 7H-dibenzo[c,g]carbazole to polynucleotides and DNA in vitro.

The N-heterocyclic aromatic pollutant, 7H-dibenzo[c,g]carbazole (DBC), is a potent carcinogen having both local and systemic effects. The overall objective of this research was to investigate the nature of the covalent binding of DBC with nucleic acids in vitro. DBC was shown to bind to polynucleotides, RNA and DNA in an in vitro rat or hamster microsomal enzyme assay, exhibiting a preferential binding to polyguanylic acid (poly[G]). Benzo[a]pyrene (BaP) binding to these same nucleic acids was determined simultaneously and was approximately 10-fold higher than DBC binding under identical experimental conditions. DBC-nucleic acid binding was shown to be dependent upon the presence of a microsomal activating system, the results being similar for rat or hamster liver microsomes. This microsome-dependent binding was unaffected by the addition of epoxide hydrase activity modifiers but was almost completely inhibited by alpha-naphthoflavone. The nature of DBC-nucleic acid binding was investigated using fluorescence spectroscopy. Benzo[c]carbazole and 5,5,6,6-tetrahydrodibenzo[c,g]carbazole were synthesized as representatives of the effect of disruption of the DBC pi-electron system on fluorescence excitation and emission. DBC-poly[G] adducts were isolated from binding assay mixtures and separated by HPLC. Results indicated that there are at least three different DBC-poly[G] adducts formed in vitro. The emission spectra of isolated adducts were similar in shape to that of DBC; however, the adduct spectra were shifted 5-10 nm toward longer wavelengths. This suggests that the bound DBC species have intact pi-electron systems. Results are consistent with binding through the nitrogen position as well as binding through the 1,2,3,4-ring of the molecule.

Animals↗

The chemistry and biology of 7H-dibenzo[c,g]carbazole: synthesis and characterization of selected derivatives, metabolism in rat liver preparations and mutagenesis mediated by cultured rat hepatocytes.

Authentic stable standards of 7H-dibenzo[c,g]carbazole (DBC), a potent environmental carcinogen, were synthesized in order to study the compound's metabolism and mutagenesis in whole cell systems. Complete characterization of 2-OH-DBC, 3-OH-DBC, 4-OH-DBC, 13c-OH-DBC and N-methyl-DBC was accomplished by UV, IR, fluorescence and high resolution NMR spectra, and by high resolution mass spectrometric procedures. Metabolites of DBC were isolated and separated by HPLC from extracts of rat liver microsomal incubations and the medium of primary cultures of rat liver cells. Identification of metabolites was accomplished by comparisons between the authentic standards and isolated metabolites by UV and fluorescence spectroscopy, mass spectral analyses, and by co-chromatographic techniques. 2-OH-DBC and 3-OH-DBC were found in all rat liver preparations as well as three other unidentified phenols. 4-OH-DBC, 13c-OH-DBC or N-methyl-DBC were not isolated under any conditions. The rates of appearance of DBC metabolites in cultures of rat liver cells were compared to those for benzo[a]pyrene (BaP) at 10, 25, 50 and 100 microM substrate. At 25 microM substrate or greater, DBC metabolites appeared in the culture medium at significantly faster rates than those of BaP. At 100 microM substrate, DBC metabolites appeared at a rate approximately 4-times the rate observed for BaP. When the mutagenic potential of DBC was compared to that of BaP under identical conditions in a co-cultivation system of rat liver cells and an epithelial cell line, DBC was found to produce significantly higher rates of mutagenesis than BaP at concentrations of 0.4, 4.0 and 40.0 microM in the culture medium. The mutagenic potential of DBC was compared to that of several derivatives of the parent compound. 3-OH-DBC, 13c-OH-DBC and N-methyl-DBC were found to be mutagenic in the co-cultivation system at 40 microM, with mutation frequencies of 4.4 +/- 0.8, 8.0 +/- 3.1 and 12.9 +/- 5.4 mutants per 10(5) survivors, respectively. The parent compound induced 8.0 +/- 2.8 mutants per 10(5) survivors at the same concentration. 2-OH-DBC and 4-OH-DBC were not mutagenic under the same conditions. The studies have shown that metabolism of 7H-DBC leads predominantly to phenols in rat liver cells. The results of the mutagenesis experiments indicate that, of the derivatives studied, those associated by induction to the nitrogen are mutagenic. The latter studies suggest that the nitrogen is involved in the activation of the parent compound through inductive mechanisms.

Animals↗

Metabolism of benzo(a)pyrene by a dioxygenase enzyme system of the freshwater green alga Selenastrum capricornutum.

The green alga Selenastrum capricornutum was incubated with benzo(a)-pyrene under an atmosphere of 20% (18)O2: 80% N2. The cis-11,12-dihydro-11,12-dihydroxybenzo(a)pyrene, cis-7,8-dihydro-7,8-dihydroxybenzo(a)pyrene and cis-4,5-dihydro-4,5-dihydroxybenzo(a)pyrene, were isolated by HPLC and analyzed by mass spectrometry. The metabolites produced molecular ions at m/z 290 and 286. Elemental analysis of the ion at m/z 290 gave an elemental composition of C20H14(18)O2 with 13% (18)O2 incorporation. The results indicate that S. capricornutum produces cis vicinal dihydrodiols from molecular oxygen via a dioxygenase enzyme pathway. The dioxygenase enzymes are characteristic of the bacterial metabolic pathway and unlike those of eukaryotic organisms which involve monooxygenase enzymes.

Benzo(a)pyrene↗

Metabolism of mutagenic polycyclic aromatic hydrocarbons by photosynthetic algal species.

Polycyclic aromatic hydrocarbons (PAH) known to produce carcinogenic and mutagenic effects have been shown to contaminate waters, sediments and soils. While it is accepted that metabolites of these compounds are responsible for most of their biological effects in mammals, their metabolism, and to a large extent their bioactivity, in aquatic plants have not been explored. Cultures of photosynthetic algal species were assayed for their ability to metabolize benzo[a]pyrene (BaP), a carcinogenic PAH under conditions which either permitted (white light) or disallowed (gold light) photooxidation of the compound. Growth of Selenastrum capricornutum, a fresh-water green alga, was completely inhibited when incubated in white light with 160 micrograms BaP/l medium. By contrast concentrations at the upper limit of BaP solubility in aqueous medium had no effect on algal growth when gold light was used. BaP quinones and phenol derivatives were found to inhibit growth of Selenastrum under white light incubation. BaP phototoxicity and metabolism were observed to be species-specific. All 3 tested species of the order Chlorococcales were growth-inhibited by BaP in white light whereas neither the green alga Chlamydomonas reinhardtii nor a blue-green, a yellow-green or an euglenoid alga responded in this fashion. Assays of radiolabeled BaP metabolism in Selenastrum showed that the majority of radioactivity associated with BaP was found in media as opposed to algal cell pellets, that the extent of metabolism was BaP concentration dependent, and that the proportion of various metabolites detected was a function of the light source. After gold light incubation, BaP diols predominated while after white light treatment at equal BaP concentrations, the 3,6-quinone was found in the highest concentration. Extracted material from algal cell pellets and from media was tested for mutagenicity in a forward mutation suspension assay in Salmonella typhimurium using resistance to 8-azaguanine for selection. Direct-acting mutagens were detected in extracted media from incubation of Selenastrum with 400 micrograms BaP/l for 1 day in gold light. Extracts of media from algae incubated in gold light from 1 to 4 days with 1200 micrograms BaP/l were found to have direct-acting mutagens as well as those requiring further metabolism. Media extracts from white light incubations of BaP were mutagenic upon addition of rat liver homogenates. Activity of these materials from white light treatment are largely attributable to unmetabolized BaP.

Benzo(a)pyrene↗

Mutagenicity of 7H-dibenzo[c,g]carbazole and metabolites in Salmonella typhimurium.

7H-Dibenzo[c,g]carbazole (DBC) is a potent carcinogen of environmental import. Reverse-mutation plate-incorporation assays for mutagenicity were undertaken in Salmonella typhimurium strains TA98 and TA100. Results were negative when no exogenous activation system was used, as well as when assays incorporated liver homogenates (S9) from rats, mice and rabbits. By contrast DBC was mutagenic in a forward mutation assay in Salmonella strain TM677 using resistance to 8-azaguanine for selection. Metabolites of DBC were generated by incubation with rat-liver microsomes and separated by HPLC. Two of these metabolites were directly mutagenic for Salmonella strain TM 677 while two others were mutagenic upon addition of S9. Synthetic phenolic derivatives of DBC were also mutagenic in this assay when further metabolized. It is likely that metabolites of DBC phenols constitute the biologically active forms.

Animals↗