Silica-induced micronuclei and chromosomal aberrations in Chinese hamster lung (V79) and human lung (Hel 299) cells

In vitro adverse effects of iron ore dusts on human lymphoblastoid cells in culture

The aim of this study was to investigate the adverse effects produced by four types of iron (Fe) ore dust using cultured human cells. Genotoxicity and cytotoxicity induced by Fe ore dusts were determined by assays including cytokinesis block micronucleus (CBMN), population growth, and methyl tetrazolium (MTT). Four iron ore dusts were tested, namely, 1002 Limonite & Goethite (1002), HG2 hematite (HG2), HG1 Soutlem Pit (HG1), and HG4. WIL2 -NS cells were incubated for 10 h with extracts from a range of concentrations (0, 75, or 150 μg/ml) of Fe ore dust. Significant decreases in percent cell viability were seen at 150 μg/ml HG2 and 1002 as measured by MTT, with viability that decreased to 75 and 73%, respectively, compared to untreated controls. The cell population regrew to a different extent after Fe ore dust was removed, except for HG1, where population remained declined. An approximately twofold significant increase in the frequency of micronucleated binucleated cells (MNBNC) was seen with 1002, HG2, and HG1 at 150 μg/ml. A significant rise in apoptosis induction was observed at 150 μg/ml HG1. Data indicate that Fe ore dusts at 150 μg/ml produced cytotoxicity and genotoxicity.

Occupational exposure to dusts and risk of renal cell carcinoma

BACKGROUND

Occupational exposures to dusts have generally been examined in relation to cancers of the respiratory system and have rarely been examined in relation to other cancers, such as renal cell carcinoma (RCC). Although previous epidemiological studies, though few, have shown certain dusts, such as asbestos, to increase renal cancer risk, the potential for other occupational dust exposures to cause kidney damage and/or cancer may exist. We investigated whether asbestos, as well as 20 other occupational dust exposures, were associated with RCC risk in a large European, multi-center, hospital-based renal case-control study.

METHODS

General occupational histories and job-specific questionnaires were reviewed by occupational hygienists for subject-specific information. Odds ratios (ORs) and 95% confidence intervals (95% CIs) between RCC risk and exposures were calculated using unconditional logistic regression.

RESULTS

Among participants ever exposed to dusts, significant associations were observed for glass fibres (OR: 2.1; 95% CI: 1.1-3.9), mineral wool fibres (OR: 2.5; 95% CI: 1.2-5.1), and brick dust (OR: 1.5; 95% CI: 1.0-2.4). Significant trends were also observed with exposure duration and cumulative exposure. No association between RCC risk and asbestos exposure was observed.

CONCLUSION

Results suggest that increased RCC risk may be associated with occupational exposure to specific types of dusts. Additional studies are needed to replicate and extend findings.

Studying the genotoxic effects induced by two kinds of bentonite particles on human B lymphoblast cells in vitro

The aim of the present study was to evaluate the genotoxic effects induced by native and active bentonite particles (BPs) on human B lymphoblast cells using comet assay and cytokinesis-block micronucleus (CBMN) assay in vitro. The cells were exposed to BPs at the concentrations of 30, 60, 120 and 240μg/ml for 24, 48 and 72h, respectively. The quartz contents of native and active BPs were 6.80±0.20 and 6.50±0.10%, respectively. Gypsum and DQ-12 quartz served as negative and positive controls. The results of comet assay showed that DNA damage induced by native and active BPs was significantly higher than that induced by gypsum control (P<0.05 or <0.01), and increased with exposure concentration and duration. When the cells were exposed to BPs at the doses of 120 and 240μg/ml for 72h, DNA damage induced by active BPs and native BPs was significantly higher than that induced by DQ-12 quartz (P<0.01), and DNA damage induced by active BPs enhanced significantly, as compared with native BPs (P<0.01). The results of CBMN assay demonstrated that both native BPs and active BPs could induce significant micronuclei, as compared with gypsum control (P<0.05 or <0.01). However, there was no significant difference of micronucleus frequency (MNF) among native BPs, active BPs and DQ-12 quartz. The water-soluble fractions from two kinds of BPs did not induce significant DNA damage and micronuclei. These findings indicated that the genotoxicity induced by active BPs and native BPs could be detected in comet assay and CBMN assay in vitro, the insoluble particle fractions from BPs may play a main role in the genotoxic effects induced by BPs.

Genotoxicity of poorly soluble particles

Poorly soluble particles such as TiO2, carbon black, and diesel exhaust particles have been evaluated for their genotoxicity using both in vitro and in vivo assays, since inhalation of these compounds by rats at high concentrations has been found to lead to tumor formation. Two principle modes of genotoxic action can be considered for particles, referred to as primary and secondary genotoxicity. Primary genotoxicity is defined as genetic damage elicited by particles in the absence of pulmonary inflammation, whereas secondary genotoxicity implies a pathway of genetic damage resulting from the oxidative DNA attack by reactive oxygen/nitrogen species (ROS/RNS), generated during particle-elicited inflammation. Conceptually, primary genotoxicity might operate via various mechanisms, such as the actions of ROS (e.g., as generated from reactive particle surfaces), or DNA-adduct formation by reactive metabolites of particle-associated organic compounds (e.g., polycyclic aromatic hydrocarbons). Currently available literature data, however, merely indicate that the tumorigenesis of poorly soluble particles involves a mechanism of secondary genotoxicity. However, further research is urgently required, since (1) causality between pulmonary inflammation and genotoxicity has not yet been established, and (2) effects of inflammation on fundamental DNA damage responses that orchestrate mutagenesis and carcinogenic outcome,that is, cell cycle arrest, DNA repair, proliferation, and apoptosis, are currently poorly understood.

Cytotoxicity and genotoxicity of ultrafine crystalline SiO2 particulate in cultured human lymphoblastoid cells

Respirable crystalline silica has been classified as a human lung carcinogen. Ultrafine (diameter < 100 nm) silica particles may be important in carcinogenesis, although the mechanisms remain unclear. In the present study, WIL2-NS cells were incubated for 6, 24, and 48 hr with 0, 30, 60, and 120 microg/ml ultrafine crystalline SiO(2) (UF-SiO(2)). The cytotoxic and genotoxic effects caused by UF-SiO(2) in cultured human cells were investigated via a set of bioassays. Significant dose- dependent decreases in percent cell viability were seen with increasing dose of UF-SiO(2) in the methyl tetrazolium assay. Significant decreases were seen at 120 microg/ml (58, 38, and 57% for 6, 24, and 48-hr exposure, respectively). During 4 days growth in the flasks, there was a slight recovery observed after washing off UF-SiO(2) as measured by the population growth assay. Significant dose-dependent reduction in the cytokinesis block proliferation index was observed by the cytokinesis block micronucleus assay. Treatment with 120 microg/ml UF-SiO(2) for 24 hr produced a fourfold increase in the frequency of micronucleated binucleated cells (MNBNC). The increase in MNBNC was dose-dependent. The lowest dose that gave a statistically significant increase in MNBNC was 30 microg/ml (24-hr treatment), which had cytotoxicity of less than 10%. There was no significant difference in DNA strand breakage as measured by the Comet assay. A significant increase in induced mutant frequency was found at 120 microg/ml as detected by the hypoxanthine guanine phosphoribosyltransferase mutation assay. The results indicate that UF-SiO(2) is cytotoxic and genotoxic in cultured human cells.

Genotoxicity evaluation of five different dentin bonding agents by chromosomal aberration analysis

Dentin bonding agents became unavoidable in today's aesthetic restorative dentistry. Nevertheless, more and more evidences on their possible cytotoxicity and/or genotoxicity emerge. Still, only limited number of studies has been published on that issue. In our work we evaluated possible genotoxicity of five different adhesives: Adper Single Bond, Adper Single Bond 2 with nanofiller, Excite, OptiBond Solo Plus and Prompt L-pop. Genotoxicity assessment was carried out on human lymphocytes in vitro, using chromosomal aberration analysis. Polymerized adhesives were tested at three different dilutions of the 0.5 g mL(-1) eluate stock (2.5 x 1:10(6), 1:10(6) and 1:10(5)) after 1 h, 24 h and 5 days of elution. Slight but significant increase in the number of chromatid breaks was observed after 24-h elution period, for adhesives Adper Single Bond 2, Excite, and OptiBond Solo Plus at dilutions of 1:10(6) and 1:10(5), and for other two only at dilution of 1:10(5). First three adhesives also appeared to be slightly genotoxic after 1 h of elution but only at 1:10(5). As a bonding agent remains in close contact with living dental tissue over a long period of time, information on their possible genotoxicity and carcinogenicity should be more clearly clarified in the near future.

Inhibition of the mitochondrial respiratory chain function abrogates quartz induced DNA damage in lung epithelial cells

Respirable quartz dust has been classified as a human carcinogen by the International Agency for Research on Cancer. The aim of our study was to investigate the mechanisms of DNA damage by DQ12 quartz in RLE-6TN rat lung epithelial type II cells (RLE). Transmission electron microscopy and flow-cytometry analysis showed a rapid particle uptake (30 min to 4 h) of quartz by the RLE cells, but particles were not found within the cell nuclei. This suggests that DNA strand breakage and induction of 8-hydroxydeoxyguanosine - as also observed in these cells during these treatment intervals - did not result from direct physical interactions between particles and DNA, or from short-lived particle surface-derived reactive oxygen species. DNA damage by quartz was significantly reduced in the presence of the mitochondrial inhibitors rotenone and antimycin-A. In the absence of quartz, these inhibitors did not affect DNA damage, but they reduced cellular oxygen consumption. No signs of apoptosis were observed by quartz. Flow-cytometry analysis indicated that the reduced DNA damage by rotenone was not due to a possible mitochondria-mediated reduction of particle uptake by the RLE cells. Further proof of concept for the role of mitochondria was shown by the failure of quartz to elicit DNA damage in mitochondria-depleted 143B (rho-0) osteosarcoma cells, at concentrations where it elicited DNA damage in the parental 143B cell line. In conclusion, our data show that respirable quartz particles can elicit oxidative DNA damage in vitro without entering the nuclei of type II cells, which are considered to be important target cells in quartz carcinogenesis. Furthermore, our observations indicate that such indirect DNA damage involves the mitochondrial electron transport chain function, by an as-yet-to-be elucidated mechanism.

Genotoxic potential of respirable bentonite particles with different quartz contents and chemical modifications in human lung fibroblasts

Crystalline silica has been classified as a human carcinogen, but there is still considerable controversy regarding its fibrogenic and carcinogenic potential. In the present study, we investigated the genotoxic potential of bentonite particles (diameter < 10 microm) with an a-quartz content of up to 6% and different chemical modifications (alkaline, acidic, organic). Human lung fibroblasts (IMR90) were incubated for 36 h, 48 h, or 72 h with bentonite particles in concentrations ranging from 1 to 15 microg/cm2. Genotoxicity was assessed using the micronucleus (MN) assay and kinetochore analysis. The generation of reactive oxygen species (ROS) caused by bentonite particles via Fenton-like mechanisms was measured acellularly using electron spin resonance (ESR) technique and intracellularly by applying an iron chelator. Our results show that bentonite-induced genotoxic effects in human lung fibroblasts are weak. The formation of micronuclei was only slightly increased after exposure of IMR90 cells to an acidic sample of bentonite dust with a quartz content of 4-5% for 36 h (15 microg/cm2), 48 h (5 microg/cm2), and 72 h (1 microg/cm2), to an alkaline sample with a quartz content of 5% for 48 h and 72 h (15 microg/cm2), and to an acidic bentonite sample with 1% quartz for 72 h (1 microg/cm2). Native (untreated) and organic activated bentonite particles did not show genotoxic effects in most of the experiments. Also, bentonite particles with a quartz content < 1% were negative in the micronucleus assay. Generation of ROS measured by ESR was dependent on the content of transition metals in the sample but not on the quartz content or the chemical modification. Reduction of MN after addition of the iron chelator 2,2'-dipyridyl showed that ROS formation also occurs intracellularly. Altogether, we conclude that the genotoxic potential of bentonite particles is generally low but can be altered by the content of quartz and available transition metals.

Inhaled particles and lung cancer. Part A: Mechanisms

Both occupational and environmental exposure to particles is associated with an increased risk of lung cancer. Particles are thought to impact on genotoxicity as well as on cell proliferation via their ability to generate oxidants such as reactive oxygen species (ROS) and reactive nitrogen species (RNS). For mechanistic purposes, one should discriminate between a) the oxidant-generating properties of particles themselves (i.e., acellular), which are mostly determined by the physicochemical characteristics of the particle surface, and b) the ability of particles to stimulate cellular oxidant generation. Cellular ROS/RNS can be generated by various mechanisms, including particle-related mitochondrial activation or NAD(P)H-oxidase enzymes. In addition, since particles can induce an inflammatory response, a further subdivision needs to be made between primary (i.e., particle-driven) and secondary (i.e., inflammation-driven) formation of oxidants. Particles may also affect genotoxicity by their ability to carry surface-adsorbed carcinogenic components into the lung. Each of these pathways can impact on genotoxicity and proliferation, as well as on feedback mechanisms involving DNA repair or apoptosis. Although abundant evidence suggests that ROS/RNS mediate particle-induced genotoxicity and mutagenesis, little information is available towards the subsequent steps leading to neoplastic changes. Additionally, since most of the proposed molecular mechanisms underlying particle-related carcinogenesis have been derived from in vitro studies, there is a need for future studies that evaluate the implication of these mechanisms for in vivo lung cancer development. In this respect, transgenic and gene knockout animal models may provide a useful tool. Such studies should also include further assessment of the relative contributions of primary (inflammation-independent) and secondary (inflammation-driven) pathways.

Monitoring of DNA damage in foundry and pottery workers exposed to silica by the alkaline comet assay

BACKGROUND

Workers in foundry and pottery are exposed to a mixture of chemicals and silica, which is suspected to cause genetic alterations.

METHODS

To investigate the potential hazard associated with the occupational exposure to silica, DNA damage in the peripheral lymphocytes of 30 foundry and 22 pottery workers were examined by the alkaline single-cell gel electrophoresis or Comet Assay, and compared to 52 healthy subjects with no history of occupational silica or chemical exposure.

RESULTS

The DNA damage observed in the lymphocytes of both foundry and pottery workers was significantly higher than that in their controls. Cigarette smoking was also related to DNA damage since the DNA damage observed in smoking silica-exposed workers compared with the non-smoking workers was significantly higher.

CONCLUSIONS

Occupational exposure of silica from foundry and pottery workplaces has been associated with the increased DNA damage and smoking which represents an additional risk factor and must be avoided.

Oxidant-induced DNA damage by quartz in alveolar epithelial cells

Respirable quartz has recently been classified as a human carcinogen. Although, studies with quartz using naked DNA as a target suggest that formation of oxyradicals by particles may play a role in the DNA-damaging properties of quartz, it is not known whether this pathway is important for DNA damage in the target cells for quartz carcinogenesis, i.e. alveolar epithelial cells. Therefore, we determined in vitro DNA damage by DQ12 quartz particles in rat and human and alveolar epithelial cells (RLE, A549) using the single cell gel electrophoresis/comet assay. The radical generation capacity of quartz was analysed by electron spin resonance (ESR) and by immunocytochemical analysis of the hydroxyl radical-specific DNA lesion 8-hydroxydeoxyguanosine (8-OHdG) in the epithelial cells. Quartz particles as well as the positive control hydrogen peroxide, caused a dose-dependent increase in DNA strand breaks in both cell lines. DNA damage by quartz was significantly reduced in the presence of the hydroxyl-radical scavengers mannitol or DMSO. The involvement of hydroxyl radicals was further established by ESR measurements and was also demonstrated by the ability of the quartz to induce formation of 8-OHdG. In conclusion, our data show that quartz elicits DNA damage in rat and human alveolar epithelial cells and indicate that these effects are driven by hydroxyl radical-generating properties of the particles.

Cytotoxic and transforming effects of silica particles with different surface properties in Syrian hamster embryo (SHE) cells

Several crystalline and amorphous silica dusts (two quartz of natural origin, one cristobalite of natural and two of biogenic origin, three amorphous diatomite earths and one pyrogenic amorphous silica) were studied in the SHE cell transformation assay, in order to compare their cytotoxic and transforming potencies and examine the role of the structure and of the state of the surface on these effects. Some samples were modified by grinding, etching and heating with the aim of establishing relationships between single surface properties and biological responses. The results showed that some quartz and cristobalite dusts (crystalline) as well as the diatomaceous earths (amorphous), but not the pyrogenic amorphous silica, were cytotoxic and induced morphological transformation of SHE cells in a concentration-dependent manner. The ranking in cytotoxicity was different from that in transforming potency, suggesting two separate molecular mechanisms for the two effects. The cytotoxic and transforming potencies were different from one dust to another, even among the same structural silicas. The type of crystalline structure (quartz vs cristobalite) and the crystalline vs biogenic amorphous form did not correlate with cytotoxic or transforming potency of silica dusts. Comparison of cellular effects induced by original and surface modified samples revealed that several surface functionalities modulate cytotoxic and transforming potencies. The cytotoxic effects appeared to be related to the distribution and abundance of silanol groups and to the presence of trace amounts of iron on the silica surface. Silica particles with fractured surfaces and/or iron-active sites, able to generate reactive oxygen species, induced SHE cell transformation. The results show that the activity of silica at the cellular level is sensitive to the composition and structure of surface functionalities and confirm that the biological response to silica is a surface originated phenomenon.

Occupational exposure to genotoxic agents

Millions of workers in the United States are potentially exposed each year to hazardous chemicals, dusts, or fibers in occupational settings. Some of these agents are genotoxic and may cause genetic alterations in the somatic or germ cells of exposed workers. Such alterations, if they occur in proto-oncogenes or tumor suppressor genes, which are involved in controlling cell growth or differentiation, may lead to the development of cancer. Genetic alterations in germ cells may also lead to reproductive failure or genetic disorders in subsequent generations. It has been estimated that occupational exposure accounts for 4% of all human cancers and up to 30% of cancer among blue-collar workers. Approximately 20,000 cancer deaths each year are attributable to occupational exposure in the United States. Occupational cancer and reproductive abnormalities have been listed on the National Occupational Research Agenda master list of research priorities as major occupational diseases and injuries.

Effects of uranium ore dust on cultured human lung cells

Effects of uranium ore dust on cell proliferation, lipid peroxidation and micronuclei formation were compared with silica (DQ12) and titanium oxide in normal human distal airway epithelial cells (NHDE), human lung cancer cells (A549) and human lung fibroblast cells. Cell proliferation was significantly inhibited with uranium ore dust and silica but not with titanium oxide. Lipid peroxidation was significantly enhanced only with uranium ore dust. Micronuclei formation was significantly stimulated with uranium ore dust in A549 and NHDE cells, but not in fibroblast cells. Silica stimulated micronuclei formation only in A549 cells. The results showed the outstanding effect of uranium ore dust on lipid peroxidation and micronuclei formation in human lung cells compared to silica and titanium dioxide.

Detection of mineral-dust-induced DNA damage in two mammalian cell lines using the alkaline single cell gel/comet assay

It has been estimated that over three million workers in the USA are potentially exposed to silica or other mineral dusts. Results of epidemiological studies evaluating whether silica or glass fibers increase lung cancer risk to the exposed workers are inconclusive. Detection of DNA damage in cells exposed to genotoxic agents is being used to assess the carcinogenic potential of environmental agents. The alkaline (pH > 13) single cell gel/comet (SCG) assay was used to determine and compare DNA damage in cultured Chinese hamster lung fibroblasts (V79 cells) and human embryonic lung fibroblasts (Hel 299 cells) exposed to crystalline silica (Min-U-Sil 5), amorphous silica (Spherisorb), carbon black, and glass fibers (AAA-10). V79 or Hel 299 cells were exposed to these mineral dusts for 3 h at various concentrations. Min-U-Sil 5 and AAA-10, at almost all concentrations tested, caused a significant increase in DNA migration measured as tail length in both V79 and Hel 299 exposed cells. However, the increase was much higher in V79 then in Hel 299 cells for Min-U-Sil 5. Tail length was also increased relative to controls after amorphous silica treatment, but not to the same extent as that induced by crystalline silica. Exposure to carbon black did not induce DNA migration at any of the concentrations tested. These results indicate that silica and glass fibers, but not carbon black, can induce DNA damage in mammalian cells, and that crystalline silica has a higher DNA-damaging activity than amorphous silica. For glass fibers, induction of DNA damage in both V79 and Hel 299 cells was observed even at a concentration 10 times lower than silica and the response was similar in both cell lines. These results suggest that the SCG/comet assay is useful for the detection of DNA damage caused by occupationally related dusts/particles.

Studies on the relationship between treatment condition and micronucleus induction in V79 cells exposed to silica and glass fibers

Studies have been carried out to determine the relationship between treatment condition and frequencies of micronucleated cells (MNC) and multinucleated cells (MTC) in Chinese hamster lung fibroblasts (V79 cells) exposed to dusts and fibers. Cells were treated with Min-U-Sil 5 silica or Owens Corning AAA-10 glass fibers under three different conditions: 24-h exposure (24E), 24-h exposure followed by 24-h post-incubation in fresh medium (24E-24P), and 48-h exposure (48E). Results showed that the frequency of MNC increased in a concentration-related manner in silica-treated V79 cells only under the condition of 24E-24P. The increase in MNC frequency after 24-h exposure was not concentration-related. No significant increase in MNC was detected in cells sampled after 48-h treatment. The frequencies of MTC in the treatment groups were higher than that in the control group. However, the increase was not statistically significant. Compared with silica, glass fibers were more active for MTC and MNC induction on a mass basis. The highest response was also observed under the condition of 24E-24P. These results indicate that 24-h exposure followed by 24-h post-incubation is a suitable treatment condition for the micronucleus assay on mineral dusts and fibers.

Lack of induction of chromosome aberrations and micronuclei by N-(1,3-dimethylbutyl)-N-phenylparaphenylenediamine in mouse bone marrow cells

N-(1,3-Dimethylbutyl)-N-phenylparaphenylenediamine (DMPPD) is a derivative of phenylenediamine (PPD) which is widely used in the rubber industry as an antioxidant. DMPPD which is a strong allergen, is least studied for its clastogenic potency. This study evaluated the genotoxic property of DMPPD in Swiss albino mice bone marrow cells by using chromosomal aberration and micronuclei assay. Three concentrations of DMPPD, i.e., 100, 150 and 200 mg/kg body wt. did not significantly increase the micronuclei in polychromatic erythrocytes or the ratio of poly to normochromatic erythrocytes. Chromosome aberration studies using 100 mg and 200 mg/kg body wt. showed that DMPPD is a non-inducer of chromosome aberrations. The results indicated non-clastogenicity of DMPPD in mice marrow cells up to a concentration of 200 mg/kg body wt. under our experimental conditions.