Clastogenicity of 1-nitropyrene, dinitropyrenes, fluorene and mononitrofluorenes in cultured Chinese hamster cells

The chromosomal aberration test using a Chinese hamster lung cell line (CHL) was carried out on 1-nitropyrene (NP), 3 dinitropyrenes (DNPs), fluorene and 4 mononitrofluorenes with and without metabolic activation (rat S9 mix). The 3 DNPs (1,3-, 1,6- and 1,8-DNP) induced chromosomal aberrations in the absence of S9 mix. The frequencies of cells with aberrations after treatment for 48 h were 43% at 2 micrograms/ml of 1,3-DNP, 55% at 0.1 microgram/ml of 1,6-DNP and 45% at 0.025 microgram/ml of 1,8-DNP, indicating the order of clastogenic potency as 1,8- greater than 1,6- greater than 1,3-DNP. On the other hand, 1-NP, which is known to be a direct-acting mutagen in bacteria, was negative in the chromosomal aberration test without S9 mix, but clearly positive with S9 mix. This effect was dependent on the concentration of the S9 fraction in the reaction mixture. High-pressure liquid chromatography analysis showed that 1-NP was converted by S9 mix to several metabolites, including 1-aminopyrene (AP). The clastogenic activity of 1-AP, however, was equivocal without S9 mix, suggesting that active clastogens other than 1-AP exist. Fluorene induced chromosomal aberrations only in the presence of S9 mix (61.8% at 25 micrograms/ml). 1-, 2-, 3- and 4-nitrofluorene (NF) were more clastogenic in the presence of S9 mix than in the absence of S9 mix, suggesting that NFs were converted to more active clastogens by S9 mix.     

The effectiveness of S9 and microsomal mix on activation of cyclophosphamide to induce genotoxicity in human lymphocytes

Comparative results are presented on the effectiveness of rat-liver S9 or microsomal mix (M mix) in activating cyclophosphamide (CP) and its ability to induce a clastogenic effect in human lymphocytes in vitro. Structural chromosome changes were analysed exclusively in 1st division (M1) metaphases post-exposure. A high genotoxic response was observed for both metabolizing systems used. With an exposure of 2 h to different concentrations of S9 or M mix, the highest aberration yields were always found for the highest protein content. For CP treatment times of 1, 2 or 4 h together with S9 mix (protein content 10 mg/ml) or M mix (4 mg/ml), the latter was more efficient. With both systems, a lower clastogenic effect of CP was found at 4 h exposure than at 1 h or 2 h. Only a weak cytotoxic effect, reflected mainly by the reduction in the percentage of 3rd cycle cells (M3), and measured in terms of the proportion of M1, M2 and M3 cells, was induced by both systems.     

Sister-chromatid exchanges induced by 1.3-butadiene and its epoxides in CHO cells

Sister-chromatid exchanges (SCEs) were analyzed in CHO cells after pulse treatment with 1,3-butadiene, 3,4-epoxy-1-butene (monoepoxybutene) and 1,2:3,4-diepoxybutane (diepoxybutane). A weak dose effect was observed after exposure to 1,3-butadiene but only in the presence of S9 mix. Monoepoxybutene and diepoxybutane were highly effective in inducing SCEs at concentrations of 0.1-1 microM both in the presence and in the absence of S9 mix. At higher concentrations the response was more pronounced without S9 mix.     

Effect of calcium phosphate and alumina C γ gels on the mutagenicity and cytotoxicity of dimethylnitrosamine as studied in the CHO/HGPRT system

When CaCl₂ was added in increasing concentrations to a rat liver metabolic activation system (S9) buffered with sodium phosphate, the mutagenic activity and cytotoxicity of dimethylnitrosamine (DMN) in the Chinese hamster ovary cell/hypoxanthine-guanine phosphoribosyl transferase (CHO/HGPRT) system were greatly increased. This effect was not observed with an S9 mix buffered with N-2-hydroxyethylpiperazine-N′-2-ethanesulfonic acid (HEPES). The calcium phosphate gel precipitate of the S9 mix possessed approximately $\text{built1}\text{3}$ of the total activity of the mix, while the supernatant had only slight activity. However, when the calcium phosphate gel precipitate of a solution of S9 salts (without S9 protein) was added to the supernatant, the remaining $\text{2}\text{3}$ of the activity was recovered. Commercially obtained calcium phosphate, tricalcium phosphate, and alumina C γ gels could substitute for CaCl₂ in the S9 mix, but diethylaminoethyl cellulose (DEAE cellulose) could not. Alumina C γ gel can exert its effect in the absence of both CaCl₂ and phosphate in the S9 mix. Increasing the time of contact between the S9 protein and the S9 salts increased the efficacy with which the S9 mix activated DMN; this is indicative of an adsorptive process by calcium phosphate gel.     

Effects of pH in the in vitro chromosomal aberration test

The relation between the pH of the medium and clastogenic activity was studied in Chinese hamster ovary (CHO) K1 cells in vitro. The pH was adjusted with NaOH, KOH, HCl or H2SO4. No clastogenic activity was observed over the initial pH range of 7.3-10.9 without S9 mix, but a few chromosomal aberrations were induced at pH 10.4 with S9 mix. The frequency of aberrations increased with the increase in amount of S9. At acidic pH, many chromatid breaks were induced at initiatial pH 5.5 or below without S9 mix, and aberrations such as chromatid breaks and chromatid exchanges were induced at initial pH 6.2 or below with S9 mix. Using MES and Bis-Tris as buffers instead of sodium bicarbonate, we observed that aberrations of the chromatid break type were inducible at pH 6.2 or below. These results show that the combination of strong alkalinity and S9 is clastogenic to CHO-K1 cells, and also that weakly acidic media are genetically active. The results indicate that incubations at non-physiological pH might give false-positive responses.     

Investigation of the mutagenic activity of tobacco smoke

The genotoxic effect of whole tobacco smoke was studied employing the Salmonella/microsome mutagenicity assay, the micronucleus test in mouse bone marrow and UDS in peripheral human lymphocytes. It was established that tobacco smoke (120-480 cm3 in a 16-1 glass chamber, at 1-10 min exposure time) induced a 3-9-fold increase of spontaneous his+ reversion mutation rate in S. typhimurium TA98, but not in strains TA97a, TA100 and TA102. Addition of S9 mix obtained from the liver of Aroclor 1254-treated rats was necessary to reveal the mutagenic activity of tobacco smoke. Treatment of BDF1 mice placed in a 14-1 glass chamber with tobacco smoke (600 cm3 smoke, 2 exposures of 30 min each, with a 1-min interval between them) caused a 2-fold dose-dependent elevation of the number of micronucleated PCE in bone marrow. No cumulative effect was detected when mice were treated with tobacco smoke during 2-28 consecutive days. The effect observed 24 h after tobacco-smoke exposure was abolished 48 h later. Tobacco smoke (180 or 360 cm3) passed through the culture medium (with or without S9 mix) of human peripheral lymphocytes (the cells were then incubated for 60 min at 37 degrees C) did not increase the spontaneous rate of UDS. Both the Salmonella/microsome mutagenicity assay employing S. typhimurium TA98 strain and the micronucleus test in mouse bone marrow might be useful in studying tobacco smoke-induced mutagenesis.     

Chromosomal effects of newly identified water pollutants PBTA-1 and PBTA-2 and their possible mother compounds (azo dyes) and intermediates (non-ClPBTAs) in two Chinese hamster cell lines

We performed the in vitro micronucleus (MN) test on 2-[2-(acetylamino)-4-[bis(2-methoxyethyl)amino]-5-methoxyphenyl]-5-amino-7-bromo-4-chloro-2H-benzotriazole (PBTA-1) and 2-[2-(acetylamino)-4-[N-(2-cyanoethyl)-ethylamino]-5-methoxyphenyl]-5-amino-7-bromo-4-chloro-2H-benzotriazole (PBTA-2), which are newly identified water pollutants from the Nishitakase river in Kyoto, Japan, and on their possible mother compounds (AZO DYE) and intermediates (non-ClPBTAs). We tested these compounds in the absence and presence of S9 mix in two Chinese hamster cell lines CHL and V79-MZ and scored MN, polynuclear and karyorrhectic (PN), and mitotic (M) cells. PBTA-2 in the absence of S9 mix induced the strongest responses in both cell lines. It was also a strong inducer of binucleate cells in PN cells in both cell lines, which suggested that it induced polyploidy. PBTA-1 showed clear positive results only in the absence of S9 mix and only in V79-MZ cells, inducing aneuploidy. In CHL cells AZO DYE-1 significantly induced MN cells in the presence of S9 mix, and AZO DYE-2 induced MN and PN cells, including binucleate cells and cells with a multilobed nucleus, in the absence of S9 mix. In V79-MZ cells, AZO DYE-1 and -2 induced primarily M cells in the presence of S9 mix. 9% of the M cells treated with 50 microg/ml AZO DYE-1 showed endoreduplication. AZO DYE-2 at 200 microg/ml condensed the chromatin in 100% of the cells. The non-ClPBTAs were a bit more cytotoxic than the other compounds and induced a slight increase in MN cells in both cell lines. Some of the chemicals tested induced a characteristic karyomorphology that might reflect abnormal cell division. Abnormalities of cell division could be detected in PN and M cells as well as in MN cells. Structure-activity relationships have also been discussed.     

Reverse mutation tests in Salmonella typhimurium and chromosomal aberration tests in mammalian cells in culture on fluorinated pyrimidine derivatives

Reverse mutation (Ames) tests with Salmonella typhimurium TA98, TA100 and TA1537, and chromosomal aberration tests in vitro with a Chinese hamster fibroblast cell line (CHL), were carried out on fluorinated pyrimidine derivatives, such as 5-fluorouracil (5-FU), 1-(2-tetrahydrofuryl)-5-fluorouracil (FT), 5-fluorodeoxyuridine (FUdR), 1,3-bis(2-tetrahydrofuryl)-5-fluorouracil (FD-1) and a mixture of uracil and FT in the molar ratio 4 : 1 (UFT) (Fujii et al., 1978). For comparison, similar tests were also carried out on 4 anti-metabolic agents, a metabolite of FD-1 and a component of UFT, such as cytosine-1-beta-D-arabinofuranoside (AraC), 6-mercaptopurine (6-MP), 6-thioguanine (6-TG), 8-azaguanine (8-AG), 3-(2-tetrahydrofuryl)-5-fluorouracil (3-FT) and uracil. The anti-bacterial action of 4 fluorinated pyrimidine derivatives such as 5-FU, FT, FD-1 and UFT to TA100 was tested under the condition that buffer, S9 mix, S9 and albumin were present. 6-MP was only positive in the Ames test with TA100 in the system without S9 mix, while all others failed to show mutagenic activity. On the other hand, all compounds tested, except uracil, induced chromosomal aberrations on CHL cells in the system without metabolic activation. FT was degraded by S9, but there was no significant difference in the killing activity of FT among with buffer, S9 mix and albumin. The killing activity of 5-FU was the strongest with buffer, and it was slightly binding to albumin. The killing activity of 5-FU was mostly decreased by S9 mix. FD-1 showed the strongest anti-bacterial action when S9 mix was present but it was degraded by S9. UFT showed no anti-bacterial action in any conditions.     

Structures of mutagens produced by the co-mutagen norharman with o- and m-toluidine isomers

Norharman, abundantly present in cigarette smoke and cooked foods, is not mutagenic to Salmonella typhimurium strains. However, norharman shows mutagenicity to S. typhimurium TA98 and YG1024 in the presence of S9 mix when coexisting with aromatic amines, including aniline, o- and m-toluidines. We previously reported that the mutagenicity from norharman and aniline in the presence of S9 mix was due to the formation of a mutagenic compound, 9-(4'-aminophenyl)-9H-pyrido[3,4-b]indole (aminophenylnorharman). In the present study, we analyzed the mutagens produced by norharman with o- or m-toluidine in the presence of S9 mix. When norharman and o-toluidine were reacted at 37 degrees C for 20 min, two mutagenic compounds, which were mutagenic with and without S9 mix, respectively, were produced, and these were isolated by HPLC. The former mutagen was deduced to be 9-(4'-amino-3'-methylphenyl)-9H-pyrido[3,4-b]indole (amino-3'-methylphenylnorharman) on the basis of various spectral data, and this new heterocyclic amine was confirmed by its chemical synthesis. The latter mutagen was identified to be the hydroxyamino derivative. Amino-3'-methylphenylnorharman induced 41,000 revertants of TA98, and 698,000 revertants of YG1024 per microg with S9 mix. Formation of the same DNA adducts was observed in YG1024 when amino-3'-methylphenylnorharman or a mixture of norharman plus o-toluidine was incubated with S9 mix. These observations suggest that norharman reacts with o-toluidine in the presence of S9 mix to produce amino-3'-methylphenylnorharman, and this compound is metabolically activated to yield its hydroxyamino derivative. After activation by O-acetyltransferase, it might bind to DNA and exert mutagenicity in S. typhimurium TA98 and YG1024. When norharman and m-toluidine were reacted in the presence of S9 mix, 9-(4'-amino-2'-methylphenyl)-9H-pyrido[3,4-b]indole (amino-2'-methylphenylnorharman) was identified as a mutagen. Thus, the mutagenicity of norharman with m-toluidine may follow a mechanism similar to that with o-toluidine.     

Mutagenic activity of 2-phenylbenzotriazole derivatives related to a mutagen, PBTA-1, in river water.

A mutagen, 2-[2-(acetylamino)-4-[bis(2-methoxyethyl)amino]-5-methoxyphenyl]5-ami no-7-bromo-4-chloro-2H-benzotriiazole (PBTA-1), isolated from water of the Nishitakase River in Kyoto exhibits potent mutagenic activity in Salmonella typhimurium TA98 with S9 mix and has characteristic moieties, including bromo, chloro, acetylamino, bis(2-methoxyethyl)amino and primary amino groups on a 2-phenylbenzotriazole skeleton. The mutagenicities of PBTA-1, its congeners and five related 2-phenylbenzotriazoles were examined in S. typhimurium TA98 with S9 mix in order to elucidate the structure-activity relationships. The data obtained suggest that a primary amino group plays an essential role in the mutagenic activity as do aromatic amines including heterocyclic amines in cooked foods. The effect of planarity of the 2-phenylbenzotriazole ring was significant, and in addition, halogen groups of PBTA-1 influenced the enhancement of the mutagenic activity.     

Mutagenic properties of 2-amino-N6-hydroxyadenine in Salmonella and in Chinese hamster lung cells in culture

The mutagenicity of the base analogue, 2-amino-N6-hydroxyadenine (AHA), was tested in Salmonella typhimurium TA100 and TA98 and in Chinese hamster lung (CHL) cells. AHA showed very potent mutagenicity in TA100 without S9 mix, inducing 25,000 revertants/micrograms. The mutagenicity increased about 2-fold upon addition of S9 mix containing 10 microliters S9. AHA was found to be one of the strongest mutagens for TA100. Addition of S9 mix containing 100 microliters S9 induced no significant increase of revertants with AHA at amounts up to 50 ng per plate. AHA was also mutagenic for the frameshift mutant, TA98, without S9 mix, the mutagenicity for TA98 being about 1/1000 of that for TA100. When the mutagenicity of AHA was tested in CHL cells, with diphtheria toxin resistance (DTr) as a selective marker in the absence of S9 mix with a 3-h treatment of cells, DTr mutants increased dose-dependently at concentrations of 2.5-15 micrograms/ml. When cells were incubated with AHA for 24 h, a 200-fold increase in the number of DTr mutants was observed; the mutagenicity was 500-fold higher than that of ethyl methanesulfonate. This marked increase of mutagenicity by prolonged incubation may indicate that AHA induces mutations mainly after incorporation into DNA. The addition of a small amount of S9 increased the mutagenicity obtained with a 3-h treatment 2-fold, but a larger amount of S9 decreased the mutagenicity as was found with S. typhimurium TA100.     

Mutagenicity of cigarette smoke condensate in Neurospora crassa

The mutagenicity of cigarette smoke condensate (CSC) was investigated in Neurospora crassa in the presence and absence of S9 mix prepared from Aroclor-1254-induced rat liver. CSC from the University of Kentucky Reference Cigarette 1R1 was assayed in a forward-mutation test at the adenine-3 (ad-3) region in resting conidia of 2-component heterokaryons. In the absence of S9 mix, CSC exhibited direct-acting mutagenicity. CSC was also mutagenic in the presence of S9 mix, but higher doses were required than in the absence of S9 mix. The dose range, survival curves, and mutation-induction curves were not significantly different when CSC was used in the presence of unheated or heat-inactivated S9. There was a positive association between killing and mutagenicity, and CSC killed conidia of N. crassa by a cytoplasmic, rather than by a nuclear, mechanism. The mutagenic potency of CSC was similar in a repair-sufficient and a nucleotide excision repair-deficient heterokaryon of N. crassa. CSC did not exhibit a photodynamic effect for killing, and CSC caused more killing at high pH than at low pH. In addition, CSC caused more killing at 37 degrees C than at 25 degrees C and also caused more killing in higher concentrations (20%) of solvent (DMSO) than in low concentrations (1%). This is the first report of the presence of potent direct-acting mutagens in CSC.     

Indirect mutagen assay in human lymphocyte in the presence of a metabolic activation system

Chromosome aberrations in cultured human lymphocytes were examined after exposures to various concentrations (from 1 X 10(-6) to 1 X 10(-3) mol X l-1) of cyclophosphamide (CP) in the presence or absence of a metabolic activation system (S9 mix). With metabolic activation, increases in the frequency of aberrant cells (AB. C.) produced by CP were significant and dose-dependent. At a concentration of 5 X 10(-4) mol X l-1, activated CP induced 29% AB. C. versus 6% AB. C. detected after exposures to CP without metabolic activation. The freshly prepared S9 mix did not virtually differ in its activation potency from the S9 mix stored for 3 weeks at -20 degrees C. CP preincubated for 100 min with S9 mix caused little or no increase in AB. C. frequency above the control level.     

Genotoxic effects of o-phenylphenol metabolites in CHO-K1 cells

The effects of microsomal activation and/or deactivation on the induction of chromosomal aberrations and sister-chromatid exchanges (SCEs) in cultured Chinese hamster ovary cells (CHO-K1 cells) by o-phenylphenol (OPP) were studied, and concurrently the metabolites were determined. After a 3-h incubation in the presence of 15% S9 mix (45 microliters/ml of S9), OPP (25-150 micrograms/ml) dose-independent SCEs and chromosomal aberrations were induced, while the amount of phenylhydroquinone (PHQ) metabolite produced from OPP did not increase linearly in the higher doses. The maximum induction of chromosomal aberrations was 18% at the 150 micrograms/ml dose, and of SCEs 13.8/cell at 75 micrograms/ml. The corresponding control values were 3% and 5.8/cell. The lowest dose required to induce SCEs in the presence of S9 mix was 25 micrograms/ml. Changing the percent of S9 mix (0-50%) while holding the OPP dose constant (100 micrograms/ml) produced a correlation between SCEs and the production of PHQ. PHQ caused cytogenetic effects both with and without S9 mix, however, in the absence of S9 mix it was more lethal and was oxidized to phenylbenzoquinone (PBQ). These results suggest that the enhanced cytogenetic effects of OPP by the addition of S9 mix correlated with the amount of PHQ produced or with the further oxides of PHQ such as phenylsemiquinone and/or PBQ which are capable of being produced from PHQ spontaneously or by the mixed-function oxidase system.     

Induction of chromosome aberrations and sister-chromatid exchanges by caprolactam in vitro

Caprolactam (CAP) induced chromosome aberrations in whole-blood cultures of human lymphocytes at 50 mM without metabolic activation (24-h treatment) and at 200 mM in the presence of rat liver S9 mix (1-h treatment). CAP also produced a dose-dependent increase in polyploid cells, the effect being statistically significant at 25 and 50 mM without S9 mix and at 100 and 200 mM with S9 mix. Without metabolic activation, there was an increase in hypodiploid cells at 50 mM and hyperdiploid cells at 12.5 mM. In Chinese hamster ovary cells, CAP produced a marginal elevation of sister-chromatid exchanges at 125 mM in the presence of S9 mix (4-h treatment). The results show that CAP is able to induce cytogenetic changes in vitro at very high toxic concentrations.     

Mutagenicity of rat-liver S9 to L5178Y mouse lymphoma cells

Rat-liver S9 preparations became highly mutagenic to cultured L5178Y mouse lymphoma cells when the exposure period was increased to 18-24 h or when S9 mix was preincubated in Fischer's medium at 37 degrees C for 19 h and then used to treat the cells for 4 h. Five different S9 preparations (from untreated and Aroclor 1254-treated Fischer 344 or Sprague-Dawley male rats) behaved similarly. S9 mix, which contained 1 mM NADP and 5 mM isocitrate as cofactors, was more mutagenic than S9 alone. Heat treatment of S9 did not destroy its mutagenic activity, but the addition of cofactors no longer stimulated an increase in mutagenicity, as observed with native S9. Treatment with cofactors was not mutagenic. These results implied the involvement of both energy-independent and NADPH-dependent enzymatic changes in S9 mix in producing mutagenic substances. The mutagenic treatments with S9 or S9 mix induced predominantly small TFT-resistant mutant colonies, which suggested that these treatments should be clastogenic to cultured mammalian cells. A warning was given that test chemicals evaluated as mutagenic only in the presence of S9 mix may instead be accelerating the decomposition of S9 mix into mutagens, and it may become necessary to experimentally distinguish between these two mechanisms before a chemical can be regarded as mutagenic.     

Mutagenicity of 8-ethoxycaffeine in vitro : Induction of point mutations in the salmonella/microsome test and of sister-chromatid exchanges as well as chromosomal aberrations in Chinese hamster ovary cells (CHO line)

The caffeine derivative 8-ethoxycaffeine (EOC) was tested in 3 different test systems in vitro. Each experiment was carried out with and without S9 mix. Incubation temperatures were 20 and 37 degrees C. (1) In the Salmonella/microsome test, EOC behaved as a pro-mutagen in the Salmonella typhimurium strain TA1535. No mutagenic activity was found in experiments without S9 mix. The influence of temperature was negligible. The mutagenic activity of EOC depended mainly on the mammals used to prepare the S9 fraction and on the agents given to them to induce liver enzymes. (2) EOC did not induce sister-chromatid exchanges in cell cultures, either at 20 or at 37 degrees C. (3) On the other hand, EOC induced chromosomal aberrations when the cells were incubated at 37 degrees C without S9 mix.     

Diethylstilbestrol and 11 derivatives: a mutagenicity study with Salmonella typhimurium.

Diethylstilbestrol was tested for mutagenicity with his- S. typhimurium strains under 10 different matabolic situations (no exogenous metabolizing system; S9 mix from liver homogenate of rats induced with Aroclor 1254, with or without inhibition of epoxide hydratase; liver and/or kidney S9 mix from control or hamsters treated with Aroclor 1254; horse-radish peroxidase + H2O2). Under none of these conditions did diethylstilbestrol give any indication of a mutagenic effect. Furthermore, 11 metabolites and other derivatives of diethylstilbestrol, 2 of them potent inducers of sister-chromatid exchange in cultured fibroblasts, were not mutagenic with any of the 4 tester strains (S. typhimurium TA100, TA98, TA1537, TA1535) in the presence or absence of S9 mix from liver homogenate of rats induced with Aroclor 1254. Thus, one of the few known human carcinogens is very resistant to detection by the mammalian enzyme-mediated Salmonella typhimurium mutagenicity test (Ames test). This is especially remarkable since the metabolizing systems used included: (1) some of very high metabolic activity (S9 mix from liver homogenate of rats and hamsters induced with Aroclor 1254); (2) metabolizing systems from organs susceptible to the carcinogenic activity of diethylstilbestrol (hamster kidney); as well as (3) a mixture of (1) and (2) in case both activities are required for the carcinogenic effect in the whole animal.     

The mutagenic and clastogenic activity of tobacco smoke

Employing the Salmonella/microsome mutagenicity assay it was established that the mutagenic effect of tobacco smoke (TS) (240 cm3 in a 16-l glass chamber, at 1 min or 5 min exposure time) in S. typhimurium TA98 depended on the type of S9 mix used. Addition of S9 mix obtained from the liver of 3-methylcholanthrene- or Aroclor-1254-pretreated rats but not from the liver of phenobarbital-pretreated or untreated rats was required to demonstrate the mutagenic activity of TS. One might suggest that polycyclic aromatic hydrocarbons were involved in TS-induced mutagenesis in S. typhimurium TA98. In addition, treatment of BDF1 mice with TS (600 cm3 TS in a 14-l glass chamber, 2-6 exposures of 30 min each with a 1-min interval between them during which a total change of the air was made) caused an up to 3.5-fold increase of the number of micronucleated polychromatic erythrocytes (PCE) in mouse bone marrow detected 24 h after the TS exposure. Furthermore, a stable 2-5-fold elevation of the number of micronucleated normochromatic erythrocytes (NCE) was detected in the peripheral blood of mice treated daily (2 x 30 min) with TS, starting 48 h after the first TS exposure. The application of the micronucleus test in mouse peripheral blood, a more convenient and useful approach for detecting the chronic clastogenic activity of TS, allowed us to establish the cumulative genotoxic effect of TS in mice.     

Comparison of two extraction procedures for the assessment of sediment genotoxicity: implication of polar organic compounds

Four sediment samples (Va?ne Airport VA, Va?ne Center VC, Va?ne North VN and Reference North RN) were collected in the Berre lagoon (France). Sediments were analyzed for polycyclic aromatic hydrocarbons (PAHs) by use of pressurized fluid extraction with a mixture of hexane/dichloromethane followed by HPLC with fluorescence detection analysis. Organic pollutants were also extracted with two solvents for subsequent evaluation of their genotoxicity: a hexane/dichloromethane mixture intended to select non-polar compounds such as PAHs, and 2-propanol intended to select polar contaminants. Sediment extracts were assessed by the Salmonella/microsome mutagenicity test with Salmonella typhimurium TA98+S9 mix and YG1041±S9 mix. Extracts were also assessed for their DNA-damaging activity and their clastogenic/aneugenic properties by the comet assay and the micronucleus test with Chinese Hamster ovary (CHO) cells. The PAH concentrations were 611ngg(-1)dw, 1341ngg(-1) dw, 613ngg(-1)dw and 482ngg(-1)dw for VA, VC, VN and RN, respectively. Two genotoxic profiles were observed, depending on the extraction procedure. All the non-polar extracts were mutagenic for TA98+S9 mix, and VA, VC, VN sediment samples exerted a significant DNA-damaging and clastogenic activity in the presence of S9 mix. All the polar extracts appeared mutagenic for TA98+S9 mix and YG104±S9 mix, and VA, VC, VN were genotoxic and clastogenic both with and without S9 mix. These results indicate that the genotoxic and mutagenic activities mainly originated from PAHs in the non-polar extracts, while these activities came from other genotoxic contaminants, such as aromatic amines and nitroarenes, in the polar extracts. This study focused on the important role of uncharacterized polar contaminants such as nitro-PAHs or aromatic amines in the global mutagenicity of sediments. The necessity to use appropriate extraction solvents to accurately evaluate the genotoxic hazard of aquatic sediments is also highlighted.