The comet assay with 8 mouse organs: results with 39 currently used food additives

We determined the genotoxicity of 39 chemicals currently in use as food additives. They fell into six categories-dyes, color fixatives and preservatives, preservatives, antioxidants, fungicides, and sweeteners. We tested groups of four male ddY mice once orally with each additive at up to 0.5xLD(50) or the limit dose (2000mg/kg) and performed the comet assay on the glandular stomach, colon, liver, kidney, urinary bladder, lung, brain, and bone marrow 3 and 24h after treatment. Of all the additives, dyes were the most genotoxic. Amaranth, Allura Red, New Coccine, Tartrazine, Erythrosine, Phloxine, and Rose Bengal induced dose-related DNA damage in the glandular stomach, colon, and/or urinary bladder. All seven dyes induced DNA damage in the gastrointestinal organs at a low dose (10 or 100mg/kg). Among them, Amaranth, Allura Red, New Coccine, and Tartrazine induced DNA damage in the colon at close to the acceptable daily intakes (ADIs). Two antioxidants (butylated hydroxyanisole (BHA) and butylated hydroxytoluene (BHT)), three fungicides (biphenyl, sodium o-phenylphenol, and thiabendazole), and four sweeteners (sodium cyclamate, saccharin, sodium saccharin, and sucralose) also induced DNA damage in gastrointestinal organs. Based on these results, we believe that more extensive assessment of food additives in current use is warranted.     

Evaluation of genotoxicity of combined soil pollution by cadmium and imidacloprid

Cadmium (Cd) is one of the important pollutants of soil and the genotoxicity of Cd-contaminated soil was studied in combination with imidacloprid. The single cell gel electrophoresis or comet assay was used to quantify DNA strand breaks as a measure of DNA damage induced by Cd and imidacloprid contamination in soil. The soil was artificially contaminated by Cd 2 h at 25℃ and were used in the comet assay. DNA damage was measured as the values of percentage of nuclei with tails, tail length, tail DNA, tail moment (TM), and Olive tail moment (OTM). DNA damages of root tips of Vicia faba increased after Cd treatment and there were dose-related increases in DNA damage measured as these parameters. However, the addition of imidacloprid further increased the DNA damage. These data confirmed the genotoxic effect of Cd to plants, and that the combined pollution with imidacloprid can enhance the genotoxicity of Cd.     

Genotoxic effects of fumes from asphalt modified with waste plastic and tall oil pitch

As the use of recycled materials and industrial by-products in asphalt mixtures is increasing, we investigated if recycled additives modify the genotoxicity of fumes emitted from asphalt. Fumes were generated in the laboratory at paving temperature from stone-mastic asphalt (SMA) and from SMA modified with waste plastic (90% polyethylene, 10% polypropylene) and tall oil pitch (SMA-WPT). In addition, fumes from SMA, SMA-WPT, asphalt concrete (AC), and AC modified with waste plastic and tall oil pitch (AC-WPT) were collected at paving sites. The genotoxicity of the fumes was studied by analysis of DNA damage (measured in the comet assay) and micronucleus formation in human bronchial epithelial BEAS 2B cells in vitro and by counting mutations in Salmonella typhimurium strains TA98 and YG1024. DNA damage was also assessed in buccal leukocytes from road pavers before and after working with SMA, SMA-WPT, AC, and AC-WPT. The chemical composition of the emissions was analysed by gas chromatography/mass spectrometry. The SMA-WPT fume generated in the laboratory induced a clear increase in DNA damage in BEAS 2B cells without metabolic activation. The laboratory-generated SMA fume increased the frequency of micronucleated BEAS 2B cells without metabolic activation. None of the asphalt fumes collected at the paving sites produced DNA damage with or without metabolic activation. Fumes from SMA and SMA-WPT from the paving sites increased micronucleus frequency without metabolic activation. None of the asphalt fumes studied showed mutagenic activity in Salmonella. No statistically significant differences in DNA damage in buccal leukocytes were detected between the pre- and post-shift samples collected from the road pavers. However, a positive correlation was found between DNA damage and the urinary metabolites of polycyclic aromatic hydrocarbons (PAHs) after work shift, which suggested an association between occupational exposures during road paving and genotoxic effects. Our results indicate that fumes from SMA and SMA-WPT contain direct-acting genotoxic components.     

Genotoxicity of vanadium pentoxide evaluate by the single cell gel electrophoresis assay in human lymphocytes

Vanadium compounds are extensively used in modern industry and occupational exposure to high doses of Vanadium is quite common. In this study, the genotoxicity of vanadium pentoxide (V₂O₅) was evaluated directly in whole blood leukocytes and in human lymphocyte cultures using the single-cell gel electrophoresis assay (Comet Assay) to detect DNA damage expressed as DNA strand breaks and alkali labile sites. This chemical produces a clear dose-response in DNA migration in whole blood leukocytes and a significative positive effect only with the highest tested concentration in human lymphocyte cultures. After different recovery times the level of DNA damage returned to the control values. These results indicate that V₂O₅ is capable to induce DNA single-strand breaks and/or alkali-labile damage.     

Inflammatory and genotoxic effects of diesel particles in vitro and in vivo

Recent studies have identified an indirect genotoxicity pathway involving inflammation as one of the mechanisms underlying the carcinogenic effects of air pollution/diesel exhaust particles (DEP). We investigated the short-term effects of DEP on markers of inflammation and genotoxicity in vitro and in vivo. DEP induced an increase in the mRNA level of pro-inflammatory cytokines and a higher level of DNA strand breaks in the human lung epithelial cell line A549 in vitro. For the in vivo study, mice were exposed by inhalation to 20 or 80 mg/m3 DEP either as a single 90-min exposure or as four repeated 90-min exposures (5 or 20 mg/m3) and the effects in broncho-alveolar lavage (BAL) cells and/or lung tissue were characterized. Inhalation of DEP induced a dose-dependent inflammatory response with infiltration of macrophages and neutrophils and elevated gene expression of IL-6 in the lungs of mice. The inflammatory response was accompanied by DNA strand breaks in BAL cells and oxidative DNA damage and increased levels of bulky DNA adducts in lung tissue, the latter indicative of direct genotoxicity. The effect of a large single dose of DEP was more pronounced and sustained on IL-6 expression and oxidative DNA damage in the lung tissue than the effect of the same dose administered over four days, whereas the reverse pattern was seen in BAL cells. Our results suggest that the effects of DEP depend on the rate of delivery of the particle dose. The mutation frequency (MF), after DEP exposure, was determined using the transgenic Muta Mouse and a similar exposure regimen. No increase was observed in MF in lung tissue 28-days after exposure. In conclusion, short-term exposure to DEP resulted in DNA strand breaks in BAL cells, oxidative DNA damage and DNA adducts in lungs; and suggested that DNA damage in part is a consequence of inflammatory processes. The response was not associated with increased MF, indicating that the host defence mechanisms were sufficient to counteract the adverse effects of inflammation. Thus, there may be thresholds for the inflammation-associated genotoxic effects of DEP inhalation.     

Possible repair action of Vitamin C on DNA damage induced by methyl methanesulfonate, cyclophosphamide, FeSO4 and CuSO4 in mouse blood cells in vivo

Interaction between Vitamin C (VitC) and transition metals can induce the formation of reactive oxygen species (ROS). VitC may also act as an ROS scavenger and as a metal chelant. To examine these possibilities, we tested in vivo the effect of two doses of VitC (1 and 30 mg/kg of mouse body weight) on the genotoxicity of known mutagens and transition metals. We used the alkaline version of the comet assay to assess DNA damage in peripheral white blood cells of mice. Animals were orally given either water (control), cyclophosphamide (CP), methyl methanesulfonate (MMS), cupric sulfate or ferrous sulfate. A single treatment with each VitC dose was administered after treatment with the mutagens or the metal sulfates. Both doses of VitC enhanced DNA damage caused by the metal sulfates. DNA damage caused by MMS was significantly reduced by the lower dose, but not by the higher dose of VitC. For CP, neither post-treatment dose of VitC affected the DNA damage level. These results indicate a modulatory role of Vitamin C in the genotoxicity/repair effect of these compounds. Single treatment with either dose of VitC showed genotoxic effects after 24 h but not after 48 h, indicating repair. Double treatment with VitC (at 0 and 24 h) induced a cumulative genotoxic response at 48 h, more intense for the higher dose. The results suggest that VitC can be either genotoxic or a repair stimulant, since the alkaline version of the comet assay does not differentiate "effective" strand breaks from those generated as an intermediate step in excision repair (incomplete excision repair sites). Further data is needed to shed light upon the beneficial/noxious effects of VitC.     

Genotoxicity of hydroquinone in A549 cells

Hydroquinone (HQ) is found in natural and anthropogenic sources including food, cosmetics, cigarette smoke, and industrial products. In addition to ingestion and dermal absorption, human exposure to HQ may also occur by inhaling cigarette smoke or polluted air. The adverse effects of HQ on respiratory systems have been studied, but genotoxicity HQ on human lung cells is unclear. The aim of this study was to investigate the cytotoxicity and genotoxicity of HQ in human lung alveolar epithelial cells (A549). We found that HQ induced a dose response in cell growth inhibition and DNA damage which was associated with an increase in oxidative stress. Cytotoxicity results demonstrated that HQ was most toxic after 24 h (LC₅₀?=?33 μM) and less toxic after 1 h exposure (LC₅₀?=?59 μM). Genotoxicity of HQ was measured using the Comet assay, H2AX phosphorylation, and chromosome aberration formation. Results from the comet assay revealed that DNA damage was highest during the earlier hours of exposure (1 and 6 h) and thereafter was reduced. A similar pattern was observed for H2AX phosphorylation suggesting that damage DNA may be repaired in later exposure hours. An increase in chromosomal aberration corresponded with maximal DNA damage which further confirmed the genotoxic effects of HQ. To investigate whether oxidative stress was involved in the cytotoxic and genotoxic effects of HQ, cellular glutathione and 8-Oxo-deoguanisone (8-Oxo-dG) formation were measured. A decrease in the reduced glutathione (GSH) and an increase oxidized glutathione (GSSG) was observed during the early hours of exposure which corresponded with elevated 8-Oxo-dG adducts. Together these results demonstrate that HQ exerts its cytotoxic and genotoxic effects in A549 lung cells, probably through DNA damage via oxidative stress.     

Cytogenetic studies of three triazine herbicides. II. In vivo micronucleus studies in mouse bone marrow

Atrazine, simazine, and cyanazine are widely used preemergence and postemergence triazine herbicides that have made their way into the potable water supply of many agricultural communities. Although there are several contradictory genotoxicity studies in the literature, our previous in vitro studies with human lymphocytes showed that atrazine, simazine, and cyanazine did not induce sister chromatid exchanges (SCEs) or chromosome aberrations (CAs) up to the limits of solubility in aqueous medium using 0.5% dimethyl sulfoxide. To expand upon these results and to ensure that our in vitro findings could be replicated in an in vivo system, mice were treated with each triazine by two intraperitoneal injections, 24h apart. The animals were sacrificed and the bone marrow removed for micronucleus (MN) analysis, 24h after the last injection. Two to four independent trials were performed for MN analysis in polychromatic erythrocytes, and in some trials the spleen was removed, cultured, and analyzed for SCEs and CAs. None of the triazines investigated induced MN in the bone marrow, even at doses that caused significant bone marrow suppression and/or death. These results indicate that atrazine, simazine, and cyanazine are not genotoxic as measured by the bone marrow MN assay in mice following high dose exposures.     

Effect of epoxide hydrolase and glutathione S-tranferase genotypes on the induction of micronuclei and DNA damage by styrene-7,8-oxide in vitro

Styrene is one of the most important organic chemicals used worldwide. Its main metabolite, styrene-7,8-oxide (SO), is considered responsible for the genotoxic effects associated with exposure to styrene. SO is detoxified by hydrolysis catalyzed by epoxide hydrolase (EH), or, to a minor extent, by conjugation mediated by glutathione S-transferases (GSTs). The purpose of the present study was to investigate whether EH (exons 3 and 4), GSTP1 (exons 5 and 6), GSTM1 and GSTT1 polymorphisms have any influence on the genotoxicity of SO in human leukocytes. Peripheral leukocytes from 30 healthy donors were exposed to SO (50 and 200 micro M) and genotoxicity was evaluated by means of the micronucleus (MN) test and alkaline comet assay, using 1% DMSO as solvent control. When EH genotypes were classified in low, medium, and high with respect to the expected EH activity, an increase in induced comet tail length was observed with decreasing EH activity in SO-exposed cells. An increase was seen in induced MN frequency in EH low-activity donors. These findings are consistent with the detoxifying activity of this enzyme. In addition, increases in MN frequencies for GSTP1 *A/*B and *A/*C genotypes with regard to the wild-type homozygous *A/*A genotype were detected. This may be due to a low detoxifying activity as a consequence of altered SO affinity of the variant protein, but must be confirmed using homozygote variant individuals, not included in this study. No clear results were obtained for GSTM1 or GSTT1 genotypes, even when performing the analysis after grouping individuals with the same expected EH activity, probably due to the minor role that glutathione conjugation plays in styrene metabolism. The present in vitro findings using human leukocytes suggest that polymorphisms in EH, and, to a lesser extent, in GSTP1, may influence induction of cytogenetic and DNA damage by SO.     

Influence of iron-overload on DNA damage and its repair in human leukocytes in vitro

Iron is an important element that modulates the production of reactive oxygen species, which are thought to play a causative role in biological processes such as mutagenesis and carcinogenesis. The potential genotoxicity of dietary iron has been seldom studied in human leukocyte and only few reports have investigated in human colon tumor cells. Therefore, DNA damage and repair capacity of human leukocytes were examined using comet assay for screening the potential toxicity of various iron-overloads such as ferric-nitrilotriacetate (Fe-NTA), FeSO(4), hemoglobin and myoglobin, and compared with 200μM of H(2)O(2) and HNE. The iron-overloads tested were not cytotoxic in the range of 10-1000 microM by trypan blue exclusion assay. The exposure of leukocytes to Fe-NTA (500 and 1000 microM), FeSO(4) (250-1000 microM), hemoglobin (10 microM) and myoglobin (250 microM) for 30 min induced significantly higher DNA damage than NC. Treatment with 500 and 1000 microM of Fe-NTA showed a similar genotoxic effect to H(2)O(2), and a significant higher genotoxic effect than HNE. The genotoxicity of FeSO(4) (250-1000 microM), hemoglobin (10 microM) and myoglobin (250 microM) was not significantly different from that of H(2)O(2) and HNE. Iron-overloads generated DNA strand break were rejoined from the first 1h. Their genotoxic effect was not observed at 24h. These data from this study provide additional information on the genotoxicity of iron-overloads and self-repair capacity in human leukocytes.     

Genotoxicity studies on the antimicrobial drug sulfamethoxazole in cultured human lymphocytes

The genotoxicity of the antimicrobial drug sulfamethoxazole was evaluated in cultured human peripheral blood lymphocytes. The frequencies of sister-chromatid exchange (SCE) and micronuclei (MN) were scored as genetic endpoints. Both tests cover a wide range of induced genetic damage such as primary DNA damage, clastogenicity and aneugenicity. Cultures were set up with blood samples from two healthy donors and the treatment was done with different sulfamethoxazole concentrations ranging from 10 to 500 microg/ml. From the results obtained it appears that this drug is able to induce weak genotoxic effects, as revealed by the slight increase in the SCE and MN frequencies, at least at one of the two highest concentrations tested. However, the results of the SCE assay should be interpreted with caution because the increase is just significant. In addition, cyotoxic/cytostatic effects of sulfamethoxazole were revealed by a decrease in the proliferative rate index (PRI) and in the cytokinesis block proliferation index (CBPI).     

DNA damage in tissues and organs of mice treated with diphenyl diselenide

Diphenyl diselenide (DPDS) is an organoselenium compound with interesting pharmacological activities and various toxic effects. In previous reports, we demonstrated the pro-oxidant action and the mutagenic properties of this molecule in bacteria, yeast and cultured mammalian cells. This study investigated the genotoxic effects of DPDS in multiple organs (brain, kidney, liver, spleen, testes and urinary bladder) and tissues (bone marrow, lymphocytes) of mice using in vivo comet assay, in order to determine the threshold of dose at which it has beneficial or toxic effects. We assessed the mechanism underlying the genotoxicity through the measurement of GSH content and thiobarbituric acid reactive species, two oxidative stress biomarkers. Male CF-1 mice were given 0.2-200 micromol/kg BW DPDS intraperitonially. DPDS induced DNA damage in brain, liver, kidney and testes in a dose response manner, in a broad dose range at 75-200 micromol/kg with the brain showing the highest level of damage. Overall, our analysis demonstrated a high correlation among decreased levels of GSH content and an increase in lipid peroxidation and DNA damage. This finding establishes an interrelationship between pro-oxidant and genotoxic effects. In addition, DPDS was not genotoxic and did not increase lipid peroxidation levels in any organs at doses < 50 micromol/kg. Finally, pre-treatment with N-acetyl-cysteine completely prevented DPDS-induced oxidative damage by the maintenance of cellular GSH levels, reinforcing the positive relationship of DPDS-induced GSH depletion and DNA damage. In summary, DPDS induces systemic genotoxicity in mammals as it causes DNA damage in vital organs like brain, liver, kidney and testes.     

In vitro studies on chemoprotective effect of purnark against benzo(a)pyrene-induced chromosomal damage in human lymphocytes.

Human lymphocytes were used as an assay system to test chemopreventive activity of natural products. Purnark, a mixture of extracts of turmeric, betel leaf and catechu, was tested for its chemoprotective activity against BP induced DNA damage. Sister chromatid exchange and micronuclei were used as markers to assess the protective activity of Purnark. Purnark gave 50-60 % protection against BP induced SCEs and micronuclei. Purnark at 1000μg dose did not show any genotoxicity.     

Inflammatory response and genotoxicity of seven wood dusts in the human epithelial cell line A549

Exposure to wood dust is common in many workplaces. Epidemiological studies indicate that occupational exposure to hardwood dusts is more harmful than to softwood dusts. In this study, human epithelial cell line A549 was incubated with well-characterized dusts from six commonly used wood species and from medium density fibreboard (MDF), at concentrations between 10 and 300microg/ml. After 3 and 6h of incubation, genotoxicity was assessed by measurement of DNA damage with the single-cell gel electrophoresis (comet) assay and inflammation was measured by the expression of IL-6 and IL-8 mRNA and by the amount of IL-8 protein. There was a 1.2-1.4-fold increase in DNA strand breaks after incubation with beech, teak, pine and MDF dusts compared with the levels in untreated cells, but after 6h only the increase induced by the MDF dust remained. Increased expression of cellular IL-6 and IL-8 mRNA was induced by all of the wood dusts at both times. Similar to IL-8 mRNA expression, the amounts of secreted IL-8 protein were elevated, except after incubation with oak dust, where a marginal reduction was seen. On the basis of the effects on IL-8 mRNA expression, the wood dusts could be divided into three groups, with teak dust being the most potent, MDF, birch, spruce and pine being intermediate, and beech and oak being the least potent. The induction of DNA strand breaks did not correlate well with the interleukin response. In conclusion, all wood dusts induced cytokine responses, and some dusts induced detectable DNA damage. The inflammatory potency seemed intermediate for dusts from the typical softwoods spruce and pine, whereas the dusts from species linked to cancer, beech and oak, were the least inflammatory. The variation of the effects induced by different wood dusts over time indicates that the DNA damage was not secondary to the cytokine response. Although hardwoods are often considered more harmful than softwoods by regulatory agencies, the current experiments do not provide evidence for a clear-cut distinction between toxicities of hardwood and softwood dust.     

The genotoxic action of uranyl ions on DNA in vitro caused by the generation of reactive oxygen species

8-Oxoguanine (8-OG) is an important biomarker of oxidative DNA damage induced by reactive oxygen species (ROS). By using ELISA with monoclonal antibodies against 8-OG, the formation of 8-OG in DNA by the action of uranyl ions, gamma-irradiation, and heating at 37 degrees C and their combined action was investigated in view of environmental pollution by uranium oxides as a result of the use of armor piercing shells with depleted uranium. The content of 8-OG in DNA induced by the action of gamma-irradiation, 5 microM uranyl ions and heating changes with time in a complicated manner. These results suggest that, by the action of uranyl ions, an additional generation of ROS occurs, which leads both to the formation of 8-OG in DNA and its further oxidation. Uranyl ions at a conceptration of 5 microM increase the thermal deamination of cytosine in DNA several times but do not influence DNA thermal depurination. It is shown that uranyl ions essentially increase the production of hydrogen peroxide and hydroxyl radicals by the action of heat on water. The results indicate a high chemical genotoxicity of uranyl ions and their enhancing effect on DNA base damage by the action of heat and gamma-irradiation.     

Genotoxicity of N-acryloyl-N'-phenylpiperazine, a redox activator for acrylic resin polymerization.

N-Acryloyl-N'-phenylpiperazine is a promoter of redox reactions synthesized recently, and proposed as an activator for the polymerization of acrylic resins for biomedical use. The chemical was analyzed for different genotoxicity endpoints, to obtain both information on its possible mutagenic/carcinogenic potential and a model analysis of a tertiary arylamine, which belongs to a class of chemicals commonly used as polymerization accelerators in the biomaterial field. The genotoxicity endpoints considered were: gene mutation in the Salmonella test; structural and numerical chromosome alterations in Chinese hamster V79 cells, evaluated by the micronucleus test together with an immunofluorescent staining specific for kinetochore proteins; in vitro and in vivo DNA damage, evaluated in V79 cells and in mouse liver by the alkaline DNA elution technique. On the whole, the results indicate that N-acryloyl-N'-phenylpiperazine is to be regarded not so much as a DNA-damaging agent, but as a genomic mutagen. Indeed, it was not mutagenic in Salmonella (though its toxicity did not allow testing concentrations over 70 micrograms/plate), and it was weakly positive in inducing chromosomal fragmentation in vitro (one positive, not dose-related, result out of five different doses tested) and in vivo DNA damage (increases in DNA elution rate never doubling control values). The chemical was, however, clearly positive (with dose-dependent effects up to about 25 times the control value) in causing numerical chromosome alterations, at the maximal non-toxic doses.     

Analysis of oxidative DNA damage and HPRT mutations in humans after hyperbaric oxygen treatment

DNA damage induced by reactive oxygen species (ROS) seems to play an important role in the induction of mutations and cancer. We have recently shown that hyperbaric oxygen (HBO) treatment of volunteers (i.e., exposure to 100% oxygen at a pressure of 2.5 ATA) induces DNA damage detected in leukocytes with the comet assay. Using formamidopyrimidine-DNA glycosylase (FPG protein) we provided indirect evidence for the induction of oxidative DNA base damage. We now comparatively evaluated FPG-sensitive sites with the comet assay and 7,8-dihydro-8-oxo-deoxyguanosine (8-OHdG) with HPLC analysis after a single HBO. As 8-OHguanine (8-OHgua) is one of the major DNA modifications induced by ROS and a pre-mutagenic lesion, we looked for HBO-induced mutations at the HPRT locus with the T cell cloning test. We also determined the genotypes for glutathione transferases (GST) and tested a possible influence of the GSTM1 and GSTT1 genotypes on the sensitivity of subjects against HBO-induced genotoxicity. Our results indicate that despite a clear induction of FPG-sensitive sites no increased levels of 8-OHdG and no induction of HPRT mutations was detected in lymphocytes after HBO. Furthermore, the DNA effects in the comet assay and the mutant frequencies in the HPRT test seem to be unrelated to the GST genotypes of the test subjects.     

Evaluation of DNA damage in radiotherapy-treated cancer patients using the alkaline comet assay

The aim of this study was to evaluate primary DNA damage and the dynamics of the repair of radiotherapy-induced DNA lesions in non-target cells of cancer patients. This study included patients diagnosed with different solid tumors who received radiotherapy. The levels of DNA damage were evaluated using the alkaline comet assay on peripheral blood leukocytes. Altogether four blood samples per patient were collected: before and after receiving the first dose of radiotherapy, in the middle of radiotherapy cycle, and after the last dose of radiotherapy. The results indicate that after the first radiation dose significantly increased levels of DNA damage were recorded in almost all cancer patients compared to their baseline values. Specific patterns of DNA damage were recorded in samples analyzed in the middle of radiotherapy and after receiving the last dose, indicating the possibility of adaptive response in some patients. Our results indicate that persistence of post-irradiation damage in peripheral blood leukocytes (and possibly in other non-target cells) of cancer patients that are strong determinants for the secondary cancer risk. Moreover, the alkaline comet assay was confirmed as a rapid and sensitive assay for the assessment of genome damage after in vivo irradiation.     

Inverse response of leukocyte heat shock proteins and DNA damage to exercise and heat

Elevated ambient temperature may exert an additional impact on the exercise-induced expression of heat shock proteins (HSP) and DNA damage in leukocytes. The protective functions of HSP include antioxidative and antiapoptotic effects and may prevent damage to DNA. Twelve athletes completed a continuous run (75% VO2max) on the treadmill, six at 28 degrees C and six at 18 degrees C room temperature. Leukocyte expression of HSP27 and inducible HSP70 was analyzed on mRNA- (RT-PCR) and protein-level (flow cytometry), while DNA damage was quantified by the comet assay. High ambient temperature induced an additional accumulation of HSP-mRNA and -protein in leukocytes compared with the exercise-induced expression at 18 degrees C. HSP27 showed a special heat sensitivity. Surprisingly, the increase of DNA damage was less pronounced after exercise at 28 degrees C compared to 18 degrees C although heat shock in vitro clearly induced DNA damage. The inverse relation between HSP and DNA damage may indicate functions of HSP which protect against exercise-induced DNA-damage in terms of thermotolerance or apoptosis.     

Evaluation of genotoxicity of combined soil pollution by cadmium and imidacloprid

Cadmium (Cd) is one of the important pollutants of soil and the genotoxicity of Cd-contaminated soil was studied in combination with imidacloprid. The single cell gel electrophoresis or comet assay was used to quantify DNA strand breaks as a measure of DNA damage induced by Cd and imidacloprid contamination in soil. The soil was artificially contaminated by Cd (0.0, 0.2, 0.5, 1.0, 2.0 mg· kg^?1 dry soil) or Cd (0.0, 0.2, 0.5, 1.0, 2.0 mg · kg^?1 dry soil) and imidacloprid (0.5 mg · kg^?1 dry soil). Roots ofVicia faba were exposed to the contaminated soil for 2 h at 25°C and were used in the comet assay. DNA damage was measured as the values of percentage of nuclei with tails, tail length, tail DNA, tail moment (TM), and Olive tail moment (OTM). DNA damages of root tips ofVicia faba increased after Cd treatment and there were dose-related increases in DNA damage measured as these parameters. However, the addition of imidacloprid further increased the DNA damage. These data confirmed the genotoxic effect of Cd to plants, and that the combined pollution with imidacloprid can enhance the genotoxicity of Cd.