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The evaluation of mutagenicities of 19 structurally related aromatic amines and acetamides in Salmonella typhimurium TA98 and TA100.

19 aromatic amines were assayed for mutagenicity using Salmonella typhimurium strains TA98 and TA100 with and without the addition of S9 from Aroclor-1254-induced rat liver. These included: naphthalenes (1-amino-, 1-acetamido-, 2-amino-, 2-acetamido-, 1-amino-4-nitro- and 2-amino-1-nitro-), biphenyls (2-amino-, 2-acetamido-, 4-amino- and 4-acetamido-), fluorenes (2-amino- and 2-acetamido-), anthracenes (1-amino-, 1-acetamido-, 2-amino- and 2-acetamido-), 3-aminofluoranthene, 1-aminopyrene and 6-aminochrysene. None of the compounds were mutagenic when tested without S9. With S9, 15 of 19 were mutagenic for TA98 and 16 of the 19 were mutagenic for TA100. Overall, 2-aminoanthracene was the most potent mutagen. When compared to the parent amines, the respective acetamido derivatives were consistently less mutagenic.

Acetamides↗

The structure-function relationships of nitrofluorenes and nitrofluorenones in the Salmonella mutagenicity and CHO sister-chromatid exchange assays.

Nitrofluorenes and nitrofluorenones are bacterial mutagens and are detected in a variety of environmental pollution sources. We tested a series of nitrosubstituted fluorenes and fluorenones for their genotoxicity using both Salmonella bacteria and Chinese hamster ovary (CHO) cells to determine if structure-function relationships observed in bacteria for mutation induction are similar to those for mutations and SCE induction in mammalian (CHO) cells. The compounds studied were 2-nitrofluorene (2-NF), 2,7-dinitrofluorene (2,7-DNF), 3-nitrofluorenone (3-NFone), 2-nitrofluorenone (2-NFone), 2,7-dinitrofluorenone (2,7-DNFone), 2,4,7-trinitrofluorenone (2,4,7-TNFone), and 2,4,5,7-tetranitrofluorenone (2,4,5,7-TNFone). In bacteria, the presence of carbonyl group to convert mono-nitrofluorenes to nitrofluorenones and the addition of a second nitro group to either mono-nitrofluorene or fluorenone to form the dinitro compounds increased mutagenic activity in the Ames test. Location of the nitro group relative to the carbonyl group was important in enhancing mutagenic activity as 2-nitrofluorenone was more mutagenic than 3-nitrofluorenone. In CHO cells, the di-, tri- and tetra-nitrofluorenones were cytotoxic and delayed the progression of CHO cells through the cell cycle. The degree of the cytotoxicity could be decreased by the addition of S9. None of the compounds produced mutations when tested in the CHO/HGPRT mutation assay with the addition of S9. Nonetheless, the current study did show that these compounds, both with and without the activation by S9, can interact with the DNA and produce SCE in CHO cells. The addition of a carbonyl group had no influence on SCE frequency since both 2-nitrofluorene and 2-nitrofluorenone induced a similar frequency of SCE either with or without S9. Additional nitro groups, forming di-, tri- or tetra-nitrofluorenones, increased the frequency of SCE induced, especially when tested with S9 which limits cytotoxicity. The addition of a single nitro group to 2-nitrofluorenone did not change the SCE frequency but did cause a large increase in the frequency of mutations in bacteria. In contrast, 2,4,7-TNFone and 2,4,5,7-TNFone were less mutagenic than the 2,7-DNFone in bacteria but were more effective in production of SCE in CHO cells. This study illustrates that structure-function relationships are dependent on both the compounds tested and the type of genetic change induced.

Animals↗

In vitro activation assays with hepatic S9 preparation from wild and laboratory reared woodchucks in the Salmonella mutagenicity test.

The Salmonella mutagenicity assay was utilized to compare hepatic S9 fractions derived from wild and laboratory reared woodchucks (Marmota monax). Two promutagens, 7,12-dimethylbenz[a]anthracence (DMBA) and 2-amino-fluorene (AF) were tested at 5 concentrations with the tester strains TA98 and TA100, against 2 levels of S9 fraction. AF produced similar number of revertants with the S9 fraction from wild and laboratory-reared animals. DMBA produced 2-4 times more revertant colonies at 50 microliter S9/plate with wild woodchuck S9 than with S9 from the laboratory-reared animals with both tester strains. It was concluded that natural inducers in the wild woodchuck diet may have contributed to the increased reversion frequency over laboratory reared woodchucks. Dose-response parameters for the activation of DMBA by S9 fraction from woodchucks and rats were compared with TA100. Woodchuck S9 had 3-40 more revertants/nmol and a 100-fold lower threshold of response than S9 from Aroclor 1254-induced rats.

9,10-Dimethyl-1,2-benzanthracene↗

Structural evidence on DNA carcinogen interactions. N-acetoxy-N-2acetylaminofluorene binding to DNA.

Linear dichroism (LD) gives useful information on the interaction between DNA and the directly acting carcinogen N-acetoxy-N-2acetylaminofluorene (AAAF). In 50% methanol solvent with low ionic strength only a weak complex (van der Waals) appears. However, above 40 degrees C strand separation takes place and a covalent aminofluorene complex forms. After renaturation a characteristic positive LD band is observed at 306 nm. The average angular orientation of the long-axis of the fluorene moiety (47 degrees to the local helix axis) is inconsistent with intercalation. It can be explained for instance by a free rotation around a C(DNA)-N(aminofluorene) bond or by a major groove site. The occupation density was 1--2 aminofluorene residues per 100 bases. With native DNA, AAAF slowly forms a covalent complex which has a negative LD at 307 nm. The orientation (70--90 degrees) is consistent with steric direction by the strand.

Acetoxyacetylaminofluorene↗

Can superoxide organic chemistry be observed within the liposomal bilayer?

--2-(Dimethylamino) fluorene (1a) and 5-benzoyloxy-2,3,7,8,12,13,17,18-octaethylporphyrin (4) react with superoxide anion radical (generated from KO2/18-crown-6 polyether) in aprotic media. Yet, when incorporated into the lipid bilayer of dimyristoyl phosphatidylcholine liposomes, these two substrates are inert to superoxide, generated enzymatically (xanthine oxidase/acetaldehyde) or radiolytically (60Co or 137Cs source/formate solution). On the other hand, 7-acetoxy-4-methylcoumarin (6), which reacts with superoxide in aprotic media yielding the corresponding 4-methylumbelliferone (7), also gives the same product when incorporated within the liposomal bilayer and reacted with radiolytically or enzymatically generated superoxide. In the latter case, the reaction is inhibited by SOD. NMR studies indicate that in contradistinction to the highly lipophilic 1a and 4, which presumably lie well within the lipid bilayer, 7 lies in a highly polar region of the bilayer. These results suggest that superoxide anion does not penetrate deep into the liposomal bilayer; nevertheless, superoxide reactions can, indeed, be observed, provided the active site of the substrate lies at or near the lipid-water interface.

Binding Sites↗

Biocatalysed synthesis of beta-O-glucosides from 9-fluorenon-2-carbohydroxyesters. Part 3: IFN-inducing and anti-HSV-2 properties.

In pursuing research on the antiviral, interferon (IFN)-inducing tilorone congeners, a new series of fluoren-carboxyhydroxyesters has been prepared and biologically explored. These esters have subsequently been used as sugar acceptors in the enzymatic transglycosylation reaction using the 'retaining' beta-glycosidase from the archaeon Sulfolobus solfataricus (Ssbeta-Gly). Both aglycones (1-6) and corresponding beta-glucosides (beta-glu 1-beta-glu 6) have been screened for cytotoxicity, interferon-stimulating and antiviral properties against HSV-2. It was found that the addition of compounds beta-glu 5, beta-glu 6 and beta-glu 4 to HSV-2 infected U937 cells downregulates viral replication and triggers cells to release IFN-alpha/beta. Taken together, the results showed improved pharmacological profiles as a consequence of glycosylation. A molecular modelling study carried out on this series of compounds completed the structural characterisation of the novel compounds.

Antineoplastic Agents↗

Modelling the atmospheric fate and seasonality of polycyclic aromatic hydrocarbons in the UK.

This paper presents the results from an exercise in atmospheric contaminant fate modelling, which had three main objectives: (1) to investigate the balance between estimated national atmospheric emissions of six selected PAHs and observed ambient measurements for the UK, as a means of testing the current emission estimates; (2) to investigate the potential influence of seasonally dependent environmental fate processes on the observed seasonality of air concentrations; and (3) after undertaking the first two objectives, to make inferences about the likely magnitude of seasonal differences in sources. When addressing objective 1 with annually averaged emissions data, it appeared that the UK PAH atmospheric emissions inventory was reasonably reliable for fluorene, fluoranthene, pyrene, benzo[a]pyrene and benzo[ghi]perylene--but not so for phenanthrene. However, more detailed analysis of the seasonality in environmental processes which may influence ambient levels, showed that the directions and/or magnitudes of the predicted seasonality did not coincide with field observations. This indicates either that our understanding of the environmental fate and behaviour of PAHs is still limited, and/or that there are uncertainties in the emissions inventories. It is suggested that better quantification of PAH sources is needed. For 3- and 4-ringed compounds, this should focus on those sources which increase with temperature, such as volatilisation from soil, water, vegetation and urban surfaces, and possible microbially-mediated formation mechanisms. The study also suggests that the contributions of inefficient, diffusive combustion processes (e.g. domestic coal/wood burning) may be underestimated as a source of the toxicologically significant higher molecular weight species in the winter. It is concluded that many signatory countries to the UNECE POPs protocol (which requires them to reduce national PAH emissions to 1990 levels) will experience difficulties in demonstrating compliance, because source inventories for 1990 and contemporary situations are clearly subject to major uncertainties.

Air Pollutants↗

Solubilization, solution equilibria, and biodegradation of PAH's under thermophilic conditions.

Biodegradation rates of PAHs are typically low at mesophilic conditions and it is believed that the kinetics of degradation is controlled by PAH solubility and mass transfer rates. Solubility tests were performed on phenanthrene, fluorene and fluoranthene at 20 degrees C, 40 degrees C and 60 degrees C and, as expected, a significant increase in the equilibrium solubility concentration and of the rate of dissolution of these polycyclic aromatic hydrocarbons (PAHs) was observed with increasing temperature. A first-order model was used to describe the PAH dissolution kinetics and the thermodynamic property changes associated with the dissolution process (enthalpy, entropy and Gibb's free energy of solution) were evaluated. Further, other relevant thermodynamic properties for these PAHs, including the activity coefficients at infinite dilution, Henry's law constants and octanol-water partition coefficients, were calculated in the temperature range 20-60 degrees C. In parallel with the dissolution studies, three thermophilic Geobacilli were isolated from compost that grew on phenanthrene at 60 degrees C and degraded the PAH more rapidly than other reported mesophiles. Our results show that while solubilization rates of PAHs are significantly enhanced at elevated temperatures, the biodegradation of PAHs under thermophilic conditions is likely mass transfer limited due to enhanced degradation rates.

Bacillaceae↗

Poly(ADP-ribose) glycohydrolase inhibitor as chemosensitiser of malignant melanoma for temozolomide.

Disruption of poly(ADP-ribose) polymerase (PARP) pathways by inhibitors of PARP catalytic domain has been shown to increase the anti-tumour activity of temozolomide (TMZ). Since PARP is inhibited by poly(ADP)ribosylation, herein we tested whether inhibition of poly(ADP-ribose) glycohydrolase (PARG) might enhance TMZ efficacy. The PARG inhibitor N-bis-(3-phenyl-propyl)9-oxo-fluorene-2,7-diamide (GPI 16552) was administered in combination with TMZ to mice injected subcutaneously or intracranially with B16 melanoma cells. The ability of treatment to reduce melanoma metastatic spreading and invasion of the extracellular matrix was also tested. The results indicated that combined treatment with GPI 16552 and TMZ significantly reduced melanoma growth, increased life-span of mice bearing tumour at the CNS site, and decreased the ability of melanoma cells to form lung metastases and to invade the extracellular matrix. In conclusion, PARG inhibition represents an alternative strategy to enhance TMZ efficacy against melanoma in peripheral as well as at CNS site.

Animals↗

Poly(ADP-ribose) glycohydrolase as a target for neuroprotective intervention: assessment of currently available pharmacological tools.

Poly(ADP-ribose) glycohydrolase (PARG) is being considered as a therapeutic target for the prevention of neurodegeneration. Here, we assessed the pharmacological tools available for target validation. The tannic acid derivative gallotannin inhibited PARG in a cell-free assay but had no detectable effect on PARG function in intact cells. Its cytoprotective actions were associated rather with the radical-scavenging potential of the compound. In astrocytes exposed to high concentrations of the nonoxidative DNA-damaging agent N-methyl-N'-nitro-N-nitrosoguanidine (MNNG), Poly(ADP-ribose) polymerase (PARP) inhibitors were fully protective, while gallotannin enhanced the damage. The compound N-bis-(3-phenyl-propyl)9-oxo-fluorene-2,7-diamide (GPI 16552), considered a potentially specific PARG inhibitor, had no effect in the different astrocyte death models compared with PARP inhibitors. In an in vitro PARG activity assay, the maximal inhibition that could be achieved with GPI 16552 was only 40% at a drug concentration of 80 microM. We conclude that neither GPI 16552 nor gallotannin are suitable for the evaluation of PARG in cellular death models, and that previous conclusions drawn from the use of these compounds should be interpreted with caution.

Animals↗

Activity of benflumetol and its enantiomers in fresh isolates of Plasmodium falciparum from East Africa.

Benflumetol, a novel antimalarial compound belonging to the fluorenes (2,3-benzindenes), has high blood schizontocidal activity, in vitro and in vivo, against mammalian plasmodia, including chloroquine-resistant Plasmodium falciparum. Due to its molecular structure benflumetol occurs in the dextrorotatory and the laevorotatory form. Normal synthesis yields the racemate of both enantiomers. Enantiomers of some antimalarial drugs possess different specific activity. It was therefore of interest to compare the response of P. falciparum to the enantiomers and the racemate of benflumetol in a variety of fresh, natural isolates. Measuring the concentration-specific inhibition of schizont maturation, the parallel investigation of 29 isolates produced no evidence of substantial activity differences between (+)-benflumetol, (-)-benflumetol and racemic benflumetol, the mean EC-50 values being 8.87, 9.71 and 12.44 nmol/l blood-medium-mixture, respectively.

Animals↗

Dioxin catabolic genes are dispersed on the Terrabacter sp. DBF63 genome.

Reverse transcription-PCR of the dbfA1A2, dbfBC, and pht genes, encoding oxygenase component of multicomponent dioxygenase, meta cleavage enzyme and hydrolase, and phthalate-degrading enzymes, respectively, revealed their role in the aromatic compound degradation by Terrabacter sp. strain DBF63. The specific expression in strain DBF63 cells grown on dibenzofuran (the model compound of dioxin; DF) and/or fluorene (FN) indicated that the DbfA1A2 and DbfBC catalyze the conversion of DF to salicylate, and that the DbfA1A2 and Pht enzymes are involved in FN degradation. Pulsed-field gel electrophoresis analyses revealed that the dbfA1A2 cistron and pht operon were located on the two linear plasmids, pDBF1 (160 kb) and pDBF2 (190 kb), while dbfBC genes were located on the chromosome. Because the pht operon is located immediately upstream of the dbfA1A2 cistron, the dioxin-catabolic genes were dispersed on the genome of strain DBF63, while FN-catabolic genes were gathered on the plasmids.

Actinomycetales↗

Open channel block and alteration of N-methyl-D-aspartic acid receptor gating by an analog of phencyclidine.

We investigated inhibition of the N-methyl-D-aspartic acid (NMDA) receptor-channel complex by N-ethyl-1,4,9, 9alpha-tetrahydro-4alphaR-cis-4alphaH-fluoren-++ +4alpha-amine (NEFA), a structural analog of phencyclidine (PCP). Using the whole-cell recording technique, we demonstrated that NEFA inhibits NMDA responses with an IC50 of 0.51 microM at -66 mV. We determined that NEFA binds to the open channel, and subsequently the channel can close and trap the blocker. Once the channel has closed, NEFA is unable to dissociate until the channel reopens. Single-channel recordings revealed that NEFA reduces the mean open time of single NMDA-activated channels in a concentration-dependent manner with a forward blocking rate (k+) of 39.9 microM-1 s-1. A computational model of antagonism by NEFA was developed and constrained using kinetic measurements of single-channel data. By multiple criteria, only models in which blocker binding in the channel causes a change in receptor operation adequately fit or predicted whole-cell data. By comparing model predictions and experimental measurements of NEFA action at a high NMDA concentration, we determined that NEFA affects receptor operation through an influence on channel gating. We conclude that inhibition of NMDA receptors by PCP-like blockers involves a modification of channel gating as well as block of current flow through the open channel.

Animals↗

Studies on surface properties of asbestos. III. Interactions between asbestos and polynuclear aromatic hydrocarbons.

The purpose of this study is to reveal the nature of the physicochemical interactions between asbestos and polynuclear aromatic hydrocarbons (PAH) in an organic liquid medium, and to assist in the understanding of synergistic effects between asbestos and PAH in bronchopulmonary cancers. The adsorption curves of three PAH (phenanthrene, fluorene, dimethyl-7,12-benzanthracene) on chrysotile and crocidolite are multistep isotherms and show the formation of bidimensional condensed layers (2D) of PAH. This phenomenon is observed with solids having a dominant basic character (asbestos, magnesia) but is not detected with acidic solids (alumina, silica-alumina). The elimination of water and dissolved gases (O2, CO2) in the liquid medium increased the affinity of asbestos for PAH. The coadsorption CO2-phenanthrene on the substrate decreased the adsorbed quantities of solute but did not inhibit the formation of layers (2D). The adsorption is weaker on leached chrysotile, than on original chrysotile; the amorphous silica coating the fibers has no affinity for PAH; the adsorption is only due to some active sites present on the surface of residual chrysotile which is accessible to phenanthrene. The formation of layers (2D) is due to strong interactions between PAH having an induced or permanent dipole moment and the active electron donor sites present on the mineral surface. The equilibrium equation between the adsorbed layer and the PAH in solution is established by reference to theoretical studies, and the results allowed us to classify the charge density of the mineral surface. The interactions between PAH and asbestos allowed us to explain the differences introduced in the kinetics of PAH uptake toward the cells when PAH is preadsorbed on asbestos. This fact could, in part, explain the synergistic effects observed in carcinogenesis.

9,10-Dimethyl-1,2-benzanthracene↗

Evaluation of photometric high-performance liquid chromatographic data for the determination of benflurone metabolites in biological materials with and without concomitant use of a standard.

The results produced by a new method of calculation based on the knowledge of the absorption coefficient and instrumental parameters without the concomitant use of a standard were compared with those calculated by the routine external standard method for a model system utilizing the quantification of benzofluorene derivatives. These were present in the incubation mixture of 5-[2-(dimethylamino)ethoxy]-7-oxo-7H-benzo[c]fluorene (benflurone) with the microsomal fraction of rat liver homogenate. Reasonable agreement between the two methods was observed. The potential utility of the new method of calculation is discussed.

Animals↗

Photolysis of polycyclic aromatic hydrocarbons in water.

The decomposition of benzo[a]pyrene (BAP), chrysene (CHR) and fluorene (FLU) in an aqueous solution by means of photolysis has been studied. The influence of initial polycyclic aromatic hydrocarbons' (PAHs) concentration, pH of the reaction mixture, temperature, presence of oxygen and tert-butyl alcohol (t-BuOH) on the degradation rate has been observed. BAP and CHR are decomposed by a mechanism different than FLU. Quantum yields of the photolytic decomposition of BAP, CHR and FLU were determined and equal 0.014, 0.0031 and 0.0038, respectively.

Benzo(a)pyrene↗

Biodegradation of phenanthrene in river sediment.

The aerobic biodegradation potential of phenanthrene (a polycyclic aromatic hydrocarbon [PAH]) in river sediment was investigated in the laboratory. Biodegradation rate constants (k1) and half-lives (t1/2) for phenanthrene (5 microg/g) in sediment samples collected at five sites along the Keelung River in densely populated northern Taiwan ranged from 0.12 to 1.13 l/day and 0.61 to 5.78 day, respectively. Higher biodegradation rate constants were noted in the absence of sediment. Two of the sediment samples were capable of biodegrading phenanthrene at initial concentrations 5-100 microg/g; lower biodegradation rates occurred at higher concentrations. Optimal biodegradation conditions were determined as 30 degreesC and pH 7.0. Biodegradation was not significantly influenced by the addition of such carbon sources as acetate, pyruvate, and yeast extract, but was significantly influenced by the addition of ammonium, sulfate, and phosphate. Results show that anthracene, fluorene, and pyrene biodegradation was enhanced by the presence of phenanthrene, but that phenanthrene treatment did not induce benzo[a]pyrene biodegradation during a 12-day incubation period.

Adsorption↗

Cytotoxicity of xenobiotics in adult rat hepatocytes in primary culture.

Primary cultures of hepatocytes isolated by collangenase perfusion of adult rats were used as an in vitro system for assessing cytotoxicity of xenobiotics. The leakage of two intracellular enzymes, lactate dehydrogenase (LDH) and glutamic oxaloacetic transaminase (GOT) were compared as indicators of cell damage. Although some differences in sensitivity were detected, either enzyme could be used to evaluate the cytotoxic potential of a chemical. Release of LDH was also compared with determination of cell viability by trypan blue uptake. For cultures exposed to 2-aminofluorene or alpha-naphthylisothiocyanate both endpoints gave comparable results. The cytotoxicities of benzo(a)pyrene, 2-aminofluorene, 3,2'-dimethyl-4-aminobiphenyl, methylene-bis-2-chloroaniline, aflatoxin B1, pyrene, aflatoxin G2, fluorene, methapyrilene, and alpha-naphthylisothiocyanate were monitored by the release of LDH and were found to be related to the length of exposure and concentration of the chemical. For chemicals that elicited DNA repair, little or no cytoxicity was observed at genotoxic concentrations in the hepatocyte primary culture/DNA repair test. Thus, measurement of enzyme release provides a means of quantifying cytotoxicity. Moreover, the use of hepatocyte primary cultures permits identification of genotoxic effects versus general cytotoxic effects of chemicals.

1-Naphthylisothiocyanate↗