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Although some types of carbon nanotubes (CNTs) have been described to induce mesothelioma in rodents and genotoxic effects in various cell systems, there are few previous studies on the genotoxicity of CNTs in mesothelial cells. Here, we examined in vitro DNA damage induction by short multi-wall CNTs (MWCNTs; 10-30 nm × 1-2 μm) and single-wall CNTs (SWCNTs; >50% SWCNTs, ~40% other CNTs

In vitro studies have suggested that nanosized titanium dioxide (TiO(2)) is genotoxic. The significance of these findings with respect to in vivo effects is unclear, as few in vivo studies on TiO(2) genotoxicity exist. Recently, nanosized TiO(2) administered in drinking water was reported to increase, e.g., micronuclei (MN) in peripheral blood polychromatic erythrocytes (PCEs) and DNA damage in leukocytes. Induction of micronuclei in mouse PCEs was earlier also described for pigment-grade TiO(2) administered intraperitoneally. The apparent systemic genotoxic effects have been suggested to reflect secondary genotoxicity of TiO(2) due to inflammation. However, a recent study suggested that induction of DNA damage in mouse bronchoalveolar lavage (BAL) cells after intratracheal instillation of nanosized or fine TiO(2) is independent of inflammation. We examined here, if inhalation of freshly generated nanosized TiO(2) (74% anatase, 26% brookite; 5 days, 4 h/day) at 0.8, 7.2, and (the highest concentration allowing stable aerosol production) 28.5 mg/m(3) could induce genotoxic effects in C57BL/6J mice locally in the lungs or systematically in peripheral PCEs. DNA damage was assessed by the comet assay in lung epithelial alveolar type II and Clara cells sampled immediately following the exposure. MN were analyzed by acridine orange staining in blood PCEs collected 48 h after the last exposure. A dose-dependent deposition of Ti in lung tissue was seen. Although the highest exposure level produced a clear increase in neutrophils in BAL fluid, indicating an inflammatory effect, no significant effect on the level of DNA damage in lung epithelial cells or micronuclei in PCEs was observed, suggesting no genotoxic effects by the 5-day inhalation exposure to nanosized TiO(2) anatase. Our inhalation exposure resulted in much lower systemic TiO(2) doses than the previous oral and intraperitoneal treatments, and lung epithelial cells probably received considerably less TiO(2) than BAL cells in the earlier intratracheal study.

This study presents a novel exposure protocol for synthesized nanoparticles (NPs). NPs were synthesized in gas phase by thermal decomposition of metal alkoxide vapors in a laminar flow reactor. The exposure protocol was used to estimate the deposition fraction of titanium dioxide (TiO2) NPs to mice lung. The experiments were conducted at aerosol mass concentrations of 0.8, 7.2, 10.0, and 28.5 mg m−3. The means of aerosol geometric mobility diameter and aerodynamic diameter were 80 and 124 nm, and the geometric standard deviations were 1.8 and 1.7, respectively. The effective density of the particles was approximately from 1.5 to 1.7 g cm−3. Particle concentration varied from 4 × 105 cm−3 at mass concentrations of 0.8 mg m−3 to 12 × 106 cm−3 at 28.5 mg m−3. Particle phase structures were 74% of anatase and 26% of brookite with respective crystallite sized of 41 and 6 nm. The brookite crystallites were approximately 100 times the size of the anatase crystallites. The TiO2 particles were porous and highly agglomerated, with a mean primary particle size of 21 nm. The specific surface area of TiO2 powder was 61 m2 g−1. We defined mice respiratory minute volume (RMV) value during exposure to TiO2 aerosol. Both TiO2 particulate matter and gaseous by-products affected respiratory parameters. The RMV values were used to quantify the deposition fraction of TiO2 matter by using two different methods. According to individual samples, the deposition fraction was 8% on an average, and when defined from aerosol mass concentration series, it was 7%. These results show that the exposure protocol can be used to study toxicological effects of synthesized NPs.

The significance of engineered nanomaterials (ENM) and nanotechnologies grows rapidly. Nanotechnology applications may have a positive marked impact on many aspects of on human every day life, for example by providing means for the production of clean energy and pure drinking water. Hundreds of consumer nano-based products are already on the market. However, very little is known of the risks of ENM to occupational safety and health (OSH), even though workers are likely to be at extra risk, as compared with other potentially exposed groups of people, because the levels of exposure are usually higher at workplaces than in other environments. However, knowledge of the exposure to, or effects of, ENM on human health and safety in occupational environments is limited and does not allow reliable assessment of risks of ENM on workers' health. Several issues related to ENM in the workplaces require marked attention. The most topical issues include: (1) improved understanding of ENM metrics associated with ENM toxicity; (2) development of monitoring devices for ENM exposure assessment; (3) understanding the changes of ENM structure and state of agglomeration at different concentrations in aerosols; (4) understanding translocation of ENM in the human body; (5) identifying the key health effects of ENM including pulmonary toxicity, genotoxicity, carcinogenic effects, and effects on circulation; (6) development of tiered approaches for testing of safety of ENM; and (7) utilizing these data for health risk assessment, with a special emphasis on occupational environment. Available data on several ENM - ability to enter the body and reach almost any organ, to cause pulmonary inflammation and fibrosis, and even to cause increased risk of mesotheliomas in animal models, call for immediate action. It is crucial to identify those ENM that may cause occupational health and safety risks from those ENM which are innocent, hence allowing prioritization of regulatory and preventive actions at workplaces at national, regional and global levels. © 2010 Elsevier Ltd.

Despite the increasing industrial use of different nanomaterials, data on their genotoxicity are scant. In the present study, we examined the potential genotoxic effects of carbon nanotubes (CNTs; >50% single-walled, approximately 40% other CNTs; 1.1 nm x 0.5-100 microm; Sigma-Aldrich) and graphite nanofibres (GNFs; 95%; outer diameter 80-200 nm, inner diameter 30-50 nm, length 5-20 microm; Sigma-Aldrich) in vitro. Genotoxicity was assessed by the single cell gel electrophoresis (comet) assay and the micronucleus assay (cytokinesis-block method) in human bronchial epithelial BEAS 2B cells cultured for 24h, 48h, or 72h with various doses (1-100 microg/cm(2), corresponding to 3.8-380 microg/ml) of the carbon nanomaterials. In the comet assay, CNTs induced a dose-dependent increase in DNA damage at all treatment times, with a statistically significant effect starting at the lowest dose tested. GNFs increased DNA damage at all doses in the 24-h treatment, at two doses (40 and 100 microg/cm(2)) in the 48-h treatment (dose-dependent effect) and at four doses (lowest 10 microg/cm(2)) in the 72-h treatment. In the micronucleus assay, no increase in micronucleated cells was observed with either of the nanomaterials after the 24-h treatment or with CNTs after the 72-h treatment. The 48-h treatment caused a significant increase in micronucleated cells at three doses (lowest 10 microg/cm(2)) of CNTs and at two doses (5 and 10 microg/cm(2)) of GNFs. The 72-h treatment with GNFs increased micronucleated cells at four doses (lowest 10 microg/cm(2)). No dose-dependent effects were seen in the micronucleus assay. The presence of carbon nanomaterial on the microscopic slides disturbed the micronucleus analysis and made it impossible at levels higher than 20 microg/cm(2) of GNFs in the 24-h and 48-h treatments. In conclusion, our results suggest that both CNTs and GNFs are genotoxic in human bronchial epithelial BEAS 2B cells in vitro. This activity may be due to the fibrous nature of these carbon nanomaterials with a possible contribution by catalyst metals present in the materials-Co and Mo in CNTs (

Micronuclei are formed from chromosomes and chromosomal fragments that lag behind in anaphase and are left outside daughter nuclei in telophase. They may also be derived from broken anaphase bridges. Nuclear buds, micronucleus-like bodies attached to the nucleus by a thin nucleoplasmic connection, have been proposed to be generated similarly to micronuclei during nuclear division or in S-phase as a stage in the extrusion of extra DNA, possibly giving rise to micronuclei. To better understand these phenomena, we have characterized the contents of 894 nuclear buds and 1392 micronuclei in normal and folate-deprived 9-day cultures of human lymphocytes using fluorescence in situ hybridization with pancentromeric and pantelomeric DNA probes. Such information has not earlier been available for human primary cells. Surprisingly, there appears to be no previous data on the occurrence of telomeres in micronuclei (or buds) of normal human cells in general. Our results suggest that nuclear buds and micronuclei have partly different mechanistic origin. Interstitial DNA without centromere or telomere label was clearly more prevalent in nuclear buds (43%) than in micronuclei (13%). DNA with only telomere label or with both centromere and telomere label was more frequent in micronuclei (62% and 22%, respectively) than in nuclear buds (44% and 10%, respectively). Folate deprivation especially increased the frequency of nuclear buds and micronuclei harboring telomeric DNA and nuclear buds harboring interstitial DNA but also buds and micronuclei with both centromeric and telomeric DNA. According to the model we propose, that micronuclei in binucleate lymphocytes primarily derive from lagging chromosomes and terminal acentric fragments during mitosis. Most nuclear buds, however, are suggested to originate from interstitial or terminal acentric fragments, possibly representing nuclear membrane entrapment of DNA that has been left in cytoplasm after nuclear division or excess DNA that is being extruded from the nucleus.

As micronuclei (MN) derive from chromosomal fragments and whole chromosomes lagging behind in anaphase, the MN assay can be used to show both clastogenic and aneugenic effects. The distinction between these phenomena is important, since the exposure studied often induces only one type of MN. This particularly concerns the use of MN as a biomarker of genotoxic exposure and effects, where differences in MN frequencies between exposed subjects and referents are expected to be small. A specific analysis of the induced type of MN may considerably improve the sensitivity of detecting the exposure effect. MN harbouring chromosomes can be distinguished from those harbouring acentric fragments by the presence of a centromere. The proportion of centromere-positive MN in human lymphocytes increases with age, which primarily reflects an age-dependent micronucleation of the X and Y chromosomes. The X chromosome especially tends to lag behind in female lymphocyte anaphase, being micronucleated more efficiently than autosomes. There is some evidence for an enhanced prevalence of fragments from chromosome 9 in spontaneous human lymphocyte MN and from chromosomes 1, 9 or 16 in MN induced in vitro by some clastogens; the breakage appears to occur in the heterochromatic block of these chromosomes. Although there are indications that centromere identification can improve the detection of clastogenic effects in humans in vivo, smokers have not shown an increase in centromere-negative MN in their cultured lymphocytes, although smoking is known to produce chromosomal aberrations. This may suggest that fragment-containing MN and chromosomal aberrations cover partly different phenomena. Understanding the mechanistic origin and contents of MN is essential for the proper use of this cytogenetic end-point in biomarker studies, genotoxicity testing and risk assessment.

Centromeric FISH was used to investigate the segregation of sex chromosomes in human lymphocytes. The aim of the study was to evaluate the effects of cell culture, cytokinesis block, age and sex on segregation and to compare the behaviour of the X and Y chromosomes. In uncultured T lymphocytes of five elderly women, the mean frequencies of nuclei hyperdiploid and hypodiploid for the X chromosome were not significantly affected by culturing the cells or by cytokinesis block. In cultured binucleate lymphocytes of two age groups of men, the X chromosome showed significantly higher mean frequencies of hyperdiploidy, hypodiploidy and reciprocal gain and loss than the Y chromosome. Reciprocal gain and loss of the Y chromosome was statistically significantly higher in the older than the younger men. In four women, studied in the same series, the rates of X chromosome aneuploidy did not significantly differ from those obtained in men. In conclusion, malsegregation of the X chromosome is common in lymphocytes of both men and women and more frequent than Y chromosome malsegregation. However, there is no clear sex difference for X chromosome reciprocal gain and loss. This would suggest that the high loss of the X chromosome in women, documented in metaphase studies, is due to micronucleation.

Occupational exposure of floriculturists is characterized by alternating periods of intense pesticide spraying and reduced or no activity. Induction of sister chromatid exchanges (SCE), structural chromosome aberrations (CA) and micronuclei (MN) was investigated in peripheral lymphocytes of a group of 23 Italian floriculturists and 22 matched controls. Blood sampling was performed during and one month after the end of intensive pesticide treatments, in order to cover a period of high and low exposure, respectively. Each donor was genotyped for glutathione S-transferase M1 (GSTM1), T1 (GSTT1), and N-acetyltransferase 2 (NAT2), three polymorphic genes involved in xenobiotic metabolism, to assess their potential role in individual genotoxic response to the pesticide exposure. No effect of the pesticide exposure on the cytogenetic parameters were detected. Smoking, however, was found to increase SCE levels. The only significant influence of phenotype composition on cytogenetic response was an increase in SCE levels in the GSTT1 positive individuals compared with the GSTT1 nulls (P=0.02). This finding was, however, based on only four GSTT1 null donors (n=41 for GSTT1 positive donors). In addition, a possible interaction was observed between smoking and GSTM1 genotype in the CA assay, GSTM1 null smokers, earlier reported to have an elevated risk for lung cancer, showing higher CA frequencies than GSTM1 positive smokers.

It cannot be generally assumed that nanoparticles are genotoxic or that nanoscale size would increase the genotoxicity of the material. The large-scale in vivo genotoxicity testing of the various nanomaterials does not seem realistic. Information on nanoparticle characteristics associated with genotoxicity, carcinogenicity and mechanisms involved can probably be used in risk assessment.

The in-vitro genotoxicity of nanosized TiO2 rutile and anatase was assessed in comparison with fine TiO2 rutile in human bronchial epithelial BEAS 2B cells using the single-cell gel electrophoresis (comet) assay and the cytokinesis-block micronucleus test. BEAS 2B cells were exposed to eight doses (1—100 μg/cm2) of titanium(IV) oxide nanosized rutile (>95%, 2 coating; 10 × 40 nm), nanosized anatase (99.7%; 2 for fine rutile and 10 μg/cm 2 for nanosized anatase. Nanosized rutile showed a significant induction in DNA damage only at 80 μg/cm2 in the 24-h treatment and at 80 and 100 μg/ cm2 in the 72-h treatment (with a dose-dependent effect). Only nanosized anatase could elevate the frequency of micronucleated BEAS 2B cells, producing a significant increase at 10 and 60 μg/cm 2 after the 72-h treatment (no dose-dependency). At increasing doses of all the particles, MN analysis became difficult due to the presence of TiO2 on the microscopic slides. In conclusion, our studies in human bronchial epithelial BEAS 2B cells showed that uncoated nanosized anatase TiO2 and fine rutile TiO2 are more efficient than SiO 2-coated nanosized rutile TiO2 in inducing DNA damage, whereas only nanosized anatase is able to slightly induce micronuclei.

Studies on potential toxicity of engineered nanoparticle (ENP) in biological systems require a proper and accurate particle characterization to ensure the reproducibility of the results and to understand biological effects of ENP. A full characterization of ENP should include various measurements such as particle size and size distribution, shape and morphology, crystallinity, composition, surface chemistry, and surface area of ENP. It is also important to characterize the state of ENP dispersions. In this study, four different ENPs, rutile and anatase titanium dioxides and short single- and multi-walled carbon nanotubes, were characterized in two dispersion media: bronchial epithelial growth medium, used for bronchial epithelial BEAS cells, and RPMI-1640 culture media with 10% of fetal calf serum (FCS) for human mesothelial (MeT-5A) cells. The purpose of this study was to determine the characteristics of ENPs and their dispersions as well as to compare dispersion additives suitable for toxicity tests and thus establish an appropriate way to prepare dispersions that performs well with the selected ENP. Dispersion additives studied in the media were bovine serum albumin (BSA) as a protein resource, dipalmitoyl phosphatidylcholine (DPPC) as a model lung surfactant, and combination of BSA and DPPC. Dispersions were characterized using optical microscopy and transmission electron microscopy. Our results showed that protein addition, BSA or FCS, in cell culture media generated small agglomerates of primary particles with narrow size variations and improved the stability of the dispersions and thus also the relevance of the in-vitro genotoxicity tests to be done.

The objective of our study was to develop a micronucleus (MN) assay for detecting genotoxic damage after inhalation exposure in mouse alveolar Type II and Clara cells, potential target cells for lung carcinogens. Ten male C57BL/6J mice were exposed to ethylene oxide (630 mg/m(3)) for 4 hr via inhalation; 10 unexposed mice serving as controls. 72 hr after the exposure, Clara cells and alveolar Type II cells were isolated using two different methods. Method 1 included a 15-min trypsin lavage and a 2-hr incubation of cell suspension. Method 2 involved a 30-min trypsin lavage, Percoll gradient centrifugation, and a 48-hr incubation for cell attachment. Nitro blue tetrazolium (NBT) -staining was applied to distinguish Clara cells. The frequency of micronuclei (MNi) was scored in NBT-negative cells (defined as Type II cells in Method 2) and NBT-positive cells (Clara cells). To detect possible differences between the techniques, MNi in Clara cells were analyzed from samples prepared by both methods. With Method 2, a clear increase in the mean frequency of micronucleated cells was seen in the exposed mice as compared with the controls, for both alveolar Type II and Clara cells. However, no significant increase in MN frequency was seen in Clara cells analyzed from samples prepared by Method 1. Based on our findings, mouse alveolar Type II and Clara cells seem to be suitable for MN analysis in studies aimed at identifying genotoxic lung carcinogens. Both alveolar Type II and Clara cells can be isolated using Method 2.

Complex chemical mixtures are transported by train from Russia to Finland for further shipment. Here, we studied if exposure to genotoxic components among these substances could affect chromosomal aberrations (CAs) in peripheral lymphocytes of workers handling the tank cars. An initial survey among 48 railroad workers and 39 referents (male smokers and nonsmokers) showed an elevation of CAs. A campaign was started to reduce exposures through preventive measures. Five years later, 51 tank car workers and 40 age-matched referents (all nonsmoking men) were studied for CAs and genetic polymorphisms of xenobiotic metabolism (EPHX1, GSTM1, GSTP1, GSTT1, NAT1, NAT2), DNA repair (ERCC2, ERCC5, XPA, XPC, XRCC1, XRCC3), and folate metabolism (MTHFR, MTR). No increase in CAs was seen in the exposed group, suggesting that the preventive measures had been successful. However, a positive association existed between exposure duration and CA level among the exposed subjects. The level of chromosome-type breaks was actually lower in the exposed workers than the referents, particularly among MTHFR wild-type homozygotes or XRCC3 codon 241 variant allele carriers, suggesting modulation of CA frequency by folate metabolism and DNA repair. An interaction was observed between the occupational exposure and MTHFR, EPHX1, and MTR genotypes in determining CA level. The NAT2, ERCC2 exon 10, and XRCC1 codon 194 polymorphisms also affected CA frequency. Our findings suggest that handling of tank cars containing complex chemical mixtures poses a genotoxic risk, which may be reduced by preventive measures. Several genetic polymorphisms seem to modify the genotoxic effect or baseline CA level. Environ. Mal. Mutagen. 2009. © 2009 Wiley-Liss, Inc.

Micronuclei (MN), used as a biomarker of effect in exposure to genotoxic carcinogens, derive from chromosomes and chromosomal fragments lagging behind in anaphase. The two types of MN are usually distinguished from each other by centromeric fluorescence in situ hybridization (FISH), centromere-positive (C(+)) MN representing entire chromosomes and centromere-negative (C(-)) MN chromosomal fragments. The incorporation of various types of chromosomal fragments and chromosomes and chromatids to MN is still poorly understood. We used directly labelled pancentromeric and pantelomeric DNA probes to examine the contents of MN in cultured binucleate lymphocytes of four unexposed, healthy subjects (two men and two women) 35-56 years of age. The presence and number of telomeric and centromeric signals was evaluated in 200 MN (50 MN per subject). These data were used to estimate the proportion of MN harbouring terminal/interstitial fragments, acentric/centric fragments, chromatid-type/chromosome-type fragments and entire chromatids/chromosomes. The majority of the C(+) MN (96% in men and 86% in women) found contained telomeric (T(+)) sequences. Most of the C(+) T(+) MN had one centromere and two or one telomere signals, suggesting that single chromatids were more frequently involved in MN than both sister chromatids. Among the C(-) MN, telomere signals were found in 91% (men) and 79% (women), showing that fragments in MN were mostly terminal. Most C(-) T(+) MN had one telomere signal, indicating higher prevalence for chromatid-type than chromosome-type terminal fragments. Combined centromeric and telomeric FISH is expected to increase the sensitivity of detecting exposure-related effects, when the exposure induces specific types of MN and its effect is low. This approach could particularly have use in discriminating between MN harbouring chromatid- and chromosome-type fragments in studies of human exposure to chemical clastogens and ionizing radiation.

In the biomonitoring of human genotoxic effects, micronuclei (MN) usually are scored in phytohaemagglutinin-stimulated cultured lymphocytes. MN also can be examined in uncultured lymphocytes, which facilitates the analysis of genotoxic damage incurred in vivo. Characterization of MN in cultured lymphocytes by fluorescence in situ hybridization (FISH) has shown a clear over-representation of the X and Y chromosomes in the MN of males. However, it is not known if this phenomenon also occurs in vivo. The purpose of the present study was to assess the frequency and composition of MN formed in vivo from immunomagnetically isolated uncultured T-lymphocytes of men. To evaluate the possible effects of genotoxic exposure on in vivo MN, we examined 17 railroad workers occupationally exposed to complex chemical mixtures and 14 referents, all nonsmokers. The results showed similar total frequencies of micronucleated cells among the exposed workers and the referents. When the MN were characterized by FISH, there were no significant differences between the exposed and referents with regards to the frequency of centromere-positive or centromere-negative MN. Centromeric label was observed in 69% of all MN, indicating that most of the MN contained whole chromosomes (or chromatids). 80% of the centromere-positive MN harbored autosomes, 12% Y chromosomes, and 8% X chromosomes. The occurrence of the Y- and X-chromosomes in MN was, respectively, 5.5- and 3.8-times greater than would be expected assuming an equal contribution by all chromosomes. Thus, sex chromosomes appear to be over-represented in lymphocyte MN of men in vivo, confirming previous results obtained in vitro.

Summary Pancentromeric FISH and X-chromosome painting were used to characterize anaphase aberrations in 2,048 cultured lymphocytes from a healthy 62-year-old woman. Of 163 aberrant anaphases, 66.9% contained either chromosomes or their fragments that lagged behind. Characterization of 200 laggards showed that 49% were autosomes, 33.5% were autosomal fragments, and 17.5% were X chromosomes. The X chromosome represented one-fourth of all lagging chromosomes and was involved much more often than would be expected by chance (1/23). Labeling of the late-replicating inactive X chromosome with 5-bromo-2′-deoxyuridine revealed that both X homologues contributed equally to the laggards. Among 200 micronuclei examined from interphase cells, the proportion of the X chromosome (31%) and autosomal fragments (50%) was higher than among anaphase laggards, whereas autosomes were involved less often (19%). These findings may reflect either selection or the fact that lagging autosomes, which were more proximal to the poles than were lagging X chromosomes, were more frequently included within the main nucleus. Our results suggest that the well-known high micronucleation and loss of the X chromosome in women's lymphocytes is the result of frequent distal lagging behind in anaphase and effective micronucleation of this chromosome. This lagging appears to affect the inactive and active X chromosomes equally.

The frequency of micronuclei (MN) in cultured peripheral lymphocytes was used as a biomarker of genotoxic effects in 34 Italian pesticide-exposed greenhouse workers and 33 unexposed referents matched with the exposed workers for age and smoking habits. The possible influence of the genetic polymorphisms of xenobiotic metabolizing enzymes glutathione S-transferase M1 (GSTM1), T1 (GSTT1), and N-acetyltransferase 2 (NAT2) was also evaluated. To restrict the analysis primarily to cells that have divided once in vitro, MN were scored only in cells showing label after a 42-h incubation with bromodeoxyuridine (BrdU), as detected by immunofluorescence (anti-BrdU technique). Two different concentrations of BrdU (0.5 and 1 microg/ml) were compared. Individual frequencies of micronucleated cells (MNCs) obtained with the two concentrations of BrdU significantly correlated with each other (r=0.55, P0.001). Higher mean MNCs frequencies (per 1000 cells) were detected among exposed smokers (9.0 at 0.5 microg/ml BrdU and 7.8 at 1 microg/ml BrdU) than in smoking referents (6.3 and 5.9, respectively). In multiple regression analysis controlling for age, sex, smoking and genotypes, a significant elevation of MNC frequency (P=0.004 at 1 microg/ml BrdU; P=0.052 at 0.5 microg/ml BrdU) was observed in greenhouse workers with a work history of extensive pesticide spraying (n=17). Increased MNC frequencies were also associated with ageing at 0.5 microg/ml BrdU, with the GSTM1-positive genotype at both 1 (P=0.028) and 0.5 (P=0.056) microg/ml BrdU in all subjects, and with the NAT2 fast acetylator genotype in smokers at 0.5 microg/ml BrdU (P=0.043). The results indicate that MN rates are increased in greenhouse workers, especially in those involved in pesticide spraying. The GSTM1 positive and NAT2 fast genotypes appear to be associated with elevated MNC frequencies, which contradicts with earlier results on elevated chromosomal aberration rates in GSTM1 null smokers and NAT2 slow subjects.

The effects of culture time (52, 64 and 76 h) and cytochalasin B (Cyt-B, 3 μg/ml) on the frequency of micronuclei (MN) harbouring whole chromosomes and acentric fragments was investigated in purified lymphocyte cultures of five nonsmoking male donors aged 41–50 years. Centromere-positive (C + ) MN were identified by fluorescence in situ hybridization, using an alphoid DNA oligomer probe (SO- α AllCen) hybridizing to all human centromeres. For each culture time, 2000 cells and 60 MN were scored per donor, both with and without Cyt-B, making a total of 60 000 cells and 1800 MN. The frequency of MN and the proportion of C + MN were higher at 64 h and 76 h than at 52 h, irrespective of Cyt-B. The culture time-dependent increase in MN frequency was mainly due to C + MN which were about 1.5-times more frequent at 64 h and 72 h than at 52 h. The frequencies of C + MN, expressed per 1000 nuclei, were similar with and without Cyt-B, although the prevalence of C + MN was consistently about 10 percent units higher in the former type of culture. This effect was due to a decreased frequency of centromere-negative (C − ) MN in the binucleate cells, possibly reflecting, e.g. increased inclusion of acentric chromosomal fragments within the main nuclei of such cells, enhanced expulsion of C − MN, or selection against binucleate cells carrying such MN. In conclusion, the present findings indicate that MN harbouring whole chromosomes become more frequent at long culture times with and without Cyt-B and that Cyt-B-induced binucleate cells show a reduced frequency of MN containing acentric fragments. Due to the high background of whole-chromosome-containing MN (mean C + MN proportions ranged from 42.3% to 62.7%), it may be recommended that centromeric fluorescence in situ hybridization is routinely applied when lymphocyte MN are used as a biomarker of human exposure to clastogens.

The influence of polymorphic glutathione S -transferases μ ( GSTM1 ) and θ ( GSTT1 ) on the rate of chromosome aberrations (CA) in peripheral lymphocytes of 30 pesticide-exposed floriculturists and 32 control subjects was studied. Pesticide exposure was not associated with elevated frequencies of CA. Among cigarette smokers, a statistically significant ( p =0.026) increase in baseline CA frequencies was observed in subjects with a homozygous deletion of the GSTM1 gene ( GSTM1 null, n =36) in comparison with those having at least one copy of the gene ( GSTM1 positive, n =26). This effect was mainly due to an excess of chromatid-type aberrations ( p =0.006). In addition, the few individuals ( n =5) deficient for both GSTM1 and GSTT1 showed significantly higher ( p =0.012) CA counts than GSTM1 positive GSTT1 nulls. Despite the limited number of subjects genotyped, the results seem to indicate an association between smoking induced CA frequencies and GSTM1 polymorphism, and a possible interaction between the GSTM1 and GSTT1 genotypes. The findings may be explained by the reduced detoxification capacity of GSTM1 null and GSTT1 null individuals.

FISH analysis of micronuclei in uncultured human T lymphocytes provides a convenient new possibility to assess structural and numerical chromosome damage in vivo. In women, T-cell micronuclei mostly contained whole chromosomes (71.6 %), especially the X chromosome (28.5%). Cell culture (72 h) enhanced the frequency of micronuclei harboring sacentric fragments 2.9 fold and the X chromosome 1.5 fold. X-chromosome-positive micronuclei were particularly prevalent (42.0%) in binucleate cells produced by cytochalasin B, a cytokinesis inhibitor used to identify cells that have divided in vitro. This was explained by a decrease in autosome-containing and an increase in X-positive micronuclei.

We used pancentromeric fluorescence in situ hybridization and X chromosome painting to characterize late anaphase aberrations in cultured (72 h) female lymphocytes in the presence of cytochalasin B (Cyt-B). Aberrant cells, mostly containing laggards, were very common (34.5%) among multipolar anaphases but fewer (5.4%) among bipolar anaphases. Characterization of the laggards showed that 75% were autosomes, 15% autosomal fragments and 10% X chromosomes in bipolar divisions; similar figures were obtained in multipolar cells. The X chromosome lagged behind more often than would be expected by chance (1/23), representing 12 and 7% of all lagging chromosomes in bipolar and multipolar divisions, respectively. Bipolar divisions contained more lagging autosomes but fewer lagging fragments and X chromosomes with Cyt-B than without it. Comparison of the frequencies of anaphase laggards and interphase micronuclei (MN) showed that lagging autosomes seldom form MN in bipolar divisions, 11% being micronucleated without Cyt-B and 8% with Cyt-B. In multipolar divisions, autosome laggards produced MN more often (35%) and were mainly responsible for the excessive MN frequency of multinucleate cells. Lagging acentric fragments frequently formed MN, with a higher efficiency in the presence of Cyt-B (65% bipolar, 58% multipolar) than in its absence (41%). X chromosome laggards were very easily micronucleated, half of them forming MN in untreated cells and seemingly all after Cyt-B treatment. Our findings suggest that most autosome laggards are merely delayed in their poleward movement, eventually being engulfed by the nucleus. Lagging fragments and X chromosomes are probably detached from the spindle and, therefore, preferentially form MN. X laggards are particularly efficiently micronucleated in Cyt-B-treated cells, perhaps because they stay further away from the poles in round cytokinesis-blocked anaphases than in normally elongated non-blocked anaphases.