The impact of lymphocyte isolation on induced DNA damage in human blood samples measured by the comet assay.

The comet assay is frequently used in human biomonitoring for the detection of exposure to genotoxic agents. Peripheral blood samples are most frequently used and tested either as whole blood or after isolation of lymphocytes (i.e. peripheral blood mononuclear cells, PBMC). To investigate a potential impact of lymphocyte isolation on induced DNA damage in human blood samples, we exposed blood ex vivo to mutagens with different modes of genotoxic action. The comet assay was performed either directly with whole blood at the end of the exposure period or with lymphocytes isolated directly after exposure. In addition to the recommended standard protocol for lymphocyte isolation, a shortened protocol was established to optimise the isolation procedure. The results indicate that the effects of induced DNA strand breaks and alkali-labile sites induced by ionising radiation and alkylants, respectively, are significantly reduced in isolated lymphocytes. In contrast, oxidative DNA base damage (induced by potassium bromate) and stable bulky adducts (induced by benzo[a]pyrene-7,8-dihydrodiol-9,10-epoxide; BPDE) seem to be less affected. Our findings suggest that in vivo-induced DNA damage might also be reduced in isolated lymphocytes in comparison with the whole blood depending of the types of DNA damage induced. Because only small genotoxic effects can generally be expected in human biomonitoring studies with the comet assay after occupational and environmental exposure to genotoxic agents, any loss might be relevant and should be avoided. The possibility of such effects and their potential impact on variability of comet assay results in human biomonitoring should be considered when performing or evaluating such kind of studies.

Further characterization of benzo[a]pyrene diol-epoxide (BPDE)-induced comet assay effects.

The present study aims to further characterize benzo[a]pyrene diol-epoxide (BPDE)-induced comet assay effects. Therefore, we measured DNA effects by the comet assay and adduct levels by high-performance liquid chromatography (HPLC) in human lymphocytes and A549 cells exposed to (±)-anti-benzo[a]pyrene-7,8-diol 9,10-epoxide [(±)-anti-BPDE] or (+)-anti-benzo[a]pyrene-7,8-diol 9,10-epoxide [(+)-anti-BPDE]. Both, the racemic form and (+)-anti-BPDE, which is the most relevant metabolite with regard to mutagenicity and carcinogenicity, induced DNA migration in cultured lymphocytes in the same range of concentrations to a similar extent in the alkaline comet assay after exposure for 2h. Nevertheless, (+)-anti-BPDE induced significantly enhanced DNA migration after 16 and 18h post-cultivation which was not seen in response to (±)-anti-BPDE. Combination of the comet assay with the Fpg (formamidopyrimidine-DNA glycosylase) protein did not enhance BPDE-induced effects and thus indicated the absence of Fpg-sensitive sites (oxidized purines, N7-guanine adducts, AP-sites). The aphidicolin (APC)-modified comet assay suggested significant excision repair activity of cultured lymphocytes during the first 18h of culture after a 2 h-exposure to BPDE. In contrast to these repair-related effects measured by the comet assay, HPLC analysis of stable adducts did not reveal any significant removal of (+)-anti-BPDE-induced adducts from lymphocytes during the first 22h of culture. On the other hand, HPLC measurements indicated that A549 cells repaired about 70% of (+)-anti-BPDE-induced DNA-adducts within 22h of release. However, various experiments with the APC-modified comet assay did not indicate significant repair activity during this period in A549 cells. The conflicting results obtained with the comet assay and the HPLC-based adduct analysis question the real cause for BPDE-induced DNA migration in the comet assay and the reliability of the APC-modified comet assay for the determination of DNA excision repair activity in response to BPDE in different cell types.

DNA repair capacity of cultured human lymphocytes exposed to mutagens measured by the comet assay and array expression analysis.

Repair of mutagen-induced DNA lesions during transportation, storage and cultivation of lymphocytes may have a significant impact on results obtained in human biomonitoring after occupational and environmental exposure of human populations to genotoxic chemicals. Using the comet assay in combination with the repair inhibitor aphidicolin and array gene expression analysis of 92 DNA repair genes, we investigated the repair of DNA lesions induced by methyl methanesulfonate (MMS) and benzo[a]pyrenediolepoxide (BPDE) in phytohaemagglutinin (PHA)-stimulated cultured human lymphocytes in the time segment before replication. The comet assay indicated fast repair of MMS-induced damage during the first hours of cultivation. In contrast, removal of BPDE-induced lesions was slower and significant amounts of damage seem to persist until S-phase. Gene expression analysis revealed that PHA stimulation had a clear effect on gene regulation in lymphocytes already during the first 18h of cultivation. Under the conditions of this study, genotoxic concentrations of MMS did not induce significant changes in gene expression. In contrast, exposure to BPDE led to altered expression of several genes in a time- and concentration-related manner. Of the significantly up-regulated genes, only two genes (XPA and XPC) were directly related to nucleotide excision repair. Our results suggest that PHA stimulation of human lymphocytes influences the expression of DNA repair genes in human lymphocytes. The effect of induced DNA damage on gene expression is comparatively low and depends on the mutagens used. PHA-stimulated lymphocytes repair induced DNA damage before they start to replicate but the repair activity during the first 18h of cultivation is not affected by changes in the expression of DNA repair genes during this period of time.

The comet assay as a tool for human biomonitoring studies: the ComNet project.

The comet assay is widely used in human biomonitoring to measure DNA damage as a marker of exposure to genotoxic agents or to investigate genoprotective effects. Studies often involve small numbers of subjects, and design may be sub-optimal in other respects. In addition, comet assay protocols in use in different laboratories vary significantly. In spite of these difficulties, it is appropriate to carry out a pooled analysis of all available comet assay biomonitoring data, in order to establish baseline parameters of DNA damage, and to investigate associations between comet assay measurements and factors such as sex, age, smoking status, nutrition, lifestyle, etc. With this as its major objective, the ComNet project has recruited almost 100 research groups willing to share datasets. Here we provide a background to this project, discussing the history of the comet assay and practical issues that can critically affect its performance. We survey its diverse applications in biomonitoring studies, including environmental and occupational exposure to genotoxic agents, genoprotection by dietary and other factors, DNA damage associated with various diseases, and intrinsic factors that affect DNA damage levels in humans. We examine in depth the quality of data from a random selection of studies, from an epidemiological and statistical point of view.

The low molecular weight DNA diffusion assay as an indicator of cytotoxicity for the in vitro comet assay.

The low molecular weight DNA diffusion assay (LMW assay) has been recommended as a measure for cytotoxicity for the in vivo comet assay. To better understand the relationship between effects in the LMW assay, DNA migration in the comet assay and effects in established cytotoxicity tests, we performed in vitro experiments with cultured human cell lines (TK6, A549) and comparatively investigated five test substances (methyl methanesulfonate, (±)-benzo[a]pyrene diol epoxide, sodium dodecyl sulphate, menthol and sodium arsenite). We measured DNA migration (tail intensity) in the comet assay and the frequency of 'hedgehogs' (cells with almost all DNA in the tail), DNA diffusion in the LMW assay, cell viability (trypan blue and fluorescein diacetate/ethidium bromide staining) and inhibition of proliferation (relative cell counts). Our in vitro experiments indicate that effects in the LMW assay occur independently from DNA effects in the comet assay and are not related to the occurrence of hedgehogs. Results from the LMW assay are in good agreement with results from viability assays and seem to allow discriminating genotoxic from non-genotoxic substances when appropriate preparation times are considered. Measurements of cytotoxicity by these methods only at an early preparation time after exposure to genotoxic substances may lead to erroneous results.

Investigations on potential co-mutagenic effects of formaldehyde.

The genotoxicity and mutagenicity of formaldehyde (FA) has been well-characterized during the last years. Besides its known direct DNA-damaging and mutagenic activity in sufficiently exposed cells, FA at low concentrations might also enhance the mutagenic and carcinogenic effects of other environmental mutagens by interfering with the repair of DNA lesions induced by these mutagens. To further assess potential co-mutagenic effects of FA, we exposed A549 human lung cells to FA in combination with various mutagens and measured the induction and removal of DNA damage by the comet assay and the production of chromosomal mutations by the cytokinesis-block micronucleus assay (CBMN assay). The mutagens tested were ionizing radiation (IR), (±)-anti-B[a]P-7,8-dihydrodiol-9,10-epoxide (BPDE), N-nitroso-N-methylurea (methyl nitrosourea; MNU) and methyl methanesulfonate (MMS). FA (10-75µM) did not enhance the genotoxic and mutagenic activity of these mutagens under the test conditions applied. FA alone and in combination with MNU or MMS did not affect the expression (mRNA level) of the gene of the O(6)-methylguanine-DNA methyltransferase (MGMT) in A549 cells. The results of these experiments do not support the assumption that low FA concentrations might interfere with the repair of DNA damage induced by other mutagens.

Does the recommended lymphocyte cytokinesis-block micronucleus assay for human biomonitoring actually detect DNA damage induced by occupational and environmental exposure to genotoxic chemicals?

This commentary challenges the paradigm that the cytokinesis-block micronucleus assay (CBMN assay) with cultured human lymphocytes, as it is performed currently, is a sensitive and useful tool for detecting genotoxic effects in populations exposed occupationally or environmentally to genotoxic chemicals. Based on the principle of the assay and the available data, increased micronucleus (MN) frequencies in binucleated cells (BNC) are mainly due to MN produced in vitro during the cultivation period (i.e. MN produced in vivo do not substantially contribute to the MN frequency measured in BNC). The sensitivity of the assay for the detection of induced MN in BNC after an in vivo exposure to a genotoxic chemical is limited because cytochalasin B (Cyt-B) is added relatively late during the culture period and, therefore, the BNC that are scored do not always represent cells that have completed one cell cycle only. Furthermore, this delay means that damaged cells can be eliminated by apoptosis and/or that DNA damage induced in vivo can be repaired prior to the production of a MN in the presence of Cyt-B. A comparison with the in vitro CBMN assay used for genotoxicity testing leads to the conclusion that it is highly unlikely that DNA damage induced in vivo is the cause for increased MN frequencies in BNC after occupational or environmental exposure to genotoxic chemicals. This commentary casts doubt on the usefulness of the CBMN assay as an indicator of genotoxicity in human biomonitoring and questions the relevance of many published data for hazard identification and risk assessment. Thus, it seems worthwhile to reconsider the use of the CBMN assay as presently conducted for the detection of genotoxic exposure in human biomonitoring.

Further investigations on the modified comet assay for measuring aphidicolin-block nucleotide excision repair.

The comet assay is increasingly used to measure the repair of various types of DNA damage. Modifications of the standard protocol have been introduced to determine the repair capacity of specific DNA repair pathways by the removal of pathway-specific DNA lesions. Recently, a cellular phenotype assay for nucleotide excision repair (NER) by quantifying the DNA strand breaks after in vitro challenge of peripheral blood mononucleated cells with benzo[a]pyrene diol epoxide (BPDE) in the presence or absence of the DNA polymerase inhibitor aphidicolin (APC) was developed (Vande Loock, K., Decordier, I., Ciardelli, R., Haumont, D. and Kirsch-Volders, M. (2010) An aphidicolin-block nucleotide excision repair assay measuring DNA incision and repair capacity. Mutagenesis, 25, 25-32). Individual repair capacity (RC) was defined as the amount of DNA damage induced by BPDE in the presence of APC minus the damage induced by BPDE and APC alone. This value should mainly reflect the incision capacity of the NER enzymes. Following this approach, we investigated the RC of cultured isolated peripheral blood mononuclear cells of nine donors in repeated experiments. We also performed the same experiments with peripheral whole blood cultures from these donors. Our results indicated considerable intra- and inter-individual variability and substantial differences between the RC of isolated mononuclear cells and whole blood from the same donor. Furthermore, the RC of unstimulated blood did not differ significantly from the repair capacity of stimulated blood but also showed considerable inter-individual variability. Altogether, our results suggest that there is still need for standardisation and validation of this assay before it can be reliably used in human biomonitoring studies.

Hyperthermia-induced genotoxic effects in human A549 cells.

Genotoxic effects of hyperthermia in vitro and in vivo have repeatedly been reported. Short-duration heat shocks and elevated temperature over longer time periods have been shown to induce DNA damage, chromosomal damage and to inhibit DNA repair. Using the comet assay and the micronucleus test, we now investigated temperature- and time-related effects on DNA damage and chromosomal effects of hyperthermia on the A549 human lung cell line. We also related the genotoxic effects to cytotoxic effects and the induction of apoptosis. Our results indicate that exposure to hyperthermia (42-48°C for 30-120min) induced genotoxic effects in a temperature- and time-related manner. Interestingly, hyperthermia-induced DNA damage measured by the comet assay was not rapidly removed by post-incubation at 37°C but even increased after exposure to 48°C for 60min. Cytotoxic effects occurred in parallel to the genotoxic effects but apoptosis was not significantly induced under these experimental conditions.

Genotoxic effects of exposure to radiofrequency electromagnetic fields (RF-EMF) in HL-60 cells are not reproducible.

Conflicting results have been published regarding the induction of genotoxic effects by exposure to radiofrequency electromagnetic fields (RF-EMF). Various results indicating a genotoxic potential of RF-EMF were reported by the collaborative EU-funded REFLEX (Risk Evaluation of Potential Environmental Hazards From Low Energy Electromagnetic Field Exposure Using Sensitive in vitro Methods) project. There has been a long-lasting scientific debate about the reliability of the reported results and an attempt to reproduce parts of the results obtained with human fibroblasts failed. Another part of the REFLEX study was performed in Berlin with the human lymphoblastoid cell line HL-60; genotoxic effects of RF-EMF were measured by means of the comet assay and the micronucleus test. The plausibility and reliability of these results were also questioned. In order to contribute to a clarification of the biological significance of the reported findings, a repeat study was performed, involving scientists of the original study. Comet-assay experiments and micronucleus tests were performed under the same experimental conditions that had led to genotoxic effects in the REFLEX study. Here we report that the attempts to reproduce the induction of genotoxic effects by RF-EMF in HL-60 cells failed. No genotoxic effects of RF-EMF were measured in the repeat experiments. We could not find an explanation for the conflicting results. However, the negative repeat experiments suggest that the biological significance of genotoxic effects of RF-EMF reported by the REFLEX study should be re-assessed.

Characterization of formaldehyde's genotoxic mode of action by gene expression analysis in TK6 cells.

Gene expression analysis has been established as a tool for the characterization of genotoxic mechanisms of chemical mutagens. It has been suggested that expression analysis is capable of distinguishing compounds that cause DNA damage from those that interfere with mitotic spindle function. Formaldehyde (FA) is known to be a DNA-reactive substance which mainly induces chromosomal damage in cultured mammalian cells. However, there has been concern that FA might also induce leukemia-specific aneuploidies, although recent cytogenetic studies excluded a relevant aneugenic potential of FA. We now investigated whether gene expression profiling can be used as a molecular tool to further characterize FA's genotoxic mode of action and to differentiate between clastogenic and aneugenic activity. TK6 cells were exposed to FA for 4 and 24 h, and changes in gene expression were analyzed using a whole-genome human microarray. Results were compared to the expression profiles of two DNA-damaging clastogens (methyl methanesulfonate and ethyl methanesulfonate) and two aneugens (colcemid and vincristine). The genotoxic activity of FA, MMS and EMS under these conditions was confirmed by comet assay experiments. The gene expression profiles indicated that clastogens and aneugens induce discriminable gene expression patterns. Exposure of TK6 cells to FA led to a discrete gene expression pattern, and all toxicogenomics analyses revealed a closer relationship of FA with clastogens than with aneugens.

Insensitivity of the in vitro cytokinesis-block micronucleus assay with human lymphocytes for the detection of DNA damage present at the start of the cell culture.

The cytokinesis-block micronucleus assay (CBMN assay) with cultured human lymphocytes is a well-established assay in genotoxicity testing and human biomonitoring. For both approaches, human lymphocytes are stimulated by phytohaemagglutinin (PHA) and cultured for about 72 h; 44 h after PHA stimulation, cytochalasin B (CytB) is added and micronuclei (MN) are scored in binucleated cells. The main difference between these two applications is the way lymphocytes are exposed to mutagens. In order to maximise the probability of detecting a mutagen, the OECD guideline 487 recommends starting the exposure to the test substance at 44-48 h after PHA stimulation. In human biomonitoring, blood samples are taken from subjects exposed to environmental mutagens in vivo and lymphocytes with induced DNA damage at the start of the cell culture are investigated with regard to potentially increased MN frequencies in binuclear lymphocytes. We compared the sensitivity of these two protocols by either treating lymphocyte cultures for 2h with known DNA-damaging mutagens at the start of the culture or 42 h after PHA stimulation. The mutagens used were methyl methanesulfonate (MMS), ethyl methanesulfonate (EMS), N-nitroso-N-ethylurea (ethyl nitrosourea; ENU), styrene oxide (SO), (±)-anti-B[a]P-7,8-dihydrodiol-9,10-epoxide (BPDE) and mitomycin C (MMC). All substances induced MN under the conditions of the standard in vitro CBMN assay but only MMC clearly induced MN in lymphocytes exposed at the start of the culture. All mutagens (except MMC, a known crosslinker) were tested by the comet assay with blood cultures exposed at the start of the culture and clearly induced DNA migration. The nuclear division index (NDI) indicated that damaged lymphocytes proliferated well in these experiments. The lack of increased MN frequencies despite increased damage levels and good proliferation suggests that the CBMN assay is rather insensitive for the detection of mutagens/clastogens when damage is induced at the start of the blood cultures. Potential consequences for the interpretation of human biomonitoring studies are discussed in this article.

Re-evaluation of a reported increased micronucleus frequency in lymphocytes of workers occupationally exposed to formaldehyde.

A replicate evaluation of increased micronucleus (MN) frequencies in peripheral lymphocytes of workers occupationally exposed to formaldehyde (FA) was undertaken to verify the observed effect and to determine scoring variability. May-Grünwald-Giemsa-stained slides were obtained from a previously performed cytokinesis-block micronucleus test (CBMNT) with 56 workers in anatomy and pathology laboratories and 85 controls. The first evaluation by one scorer (scorer 1) had led to a highly significant difference between workers and controls (3.96 vs 0.81 MN per 1000 cells). The slides were coded before re-evaluation and the code was broken after the complete re-evaluation of the study. A total of 1000 binucleated cells (BNC) were analysed per subject and the frequency of MN (in ‰) was determined. Slides were distributed equally and randomly between two scorers, so that the scorers had no knowledge of the exposure status. Scorer 2 (32 exposed, 36 controls) measured increased MN frequencies in exposed workers (9.88 vs 6.81). Statistical analysis with the two-sample Wilcoxon test indicated that this difference was not significant (p=0.17). Scorer 3 (20 exposed, 46 controls) obtained a similar result, but slightly higher values for the comparison of exposed and controls (19.0 vs 12.89; p=0.089). Combining the results of the two scorers (13.38 vs 10.22), a significant difference between exposed and controls (p=0.028) was obtained when the stratified Wilcoxon test with the scorers as strata was applied. Interestingly, the re-evaluation of the slides led to clearly higher MN frequencies for exposed and controls compared with the first evaluation. Bland-Altman plots indicated that the agreement between the measurements of the different scorers was very poor, as shown by mean differences of 5.9 between scorer 1 and scorer 2 and 13.0 between scorer 1 and scorer 3. Calculation of the intra-class correlation coefficient (ICC) revealed that all scorer comparisons in this study were far from acceptable for the reliability of this assay. Possible implications for the use of the CBMNT in human biomonitoring studies are discussed.

Investigations of potential susceptibility toward formaldehyde-induced genotoxicity.

Blood samples were taken from three groups of volunteers (30 male smokers, 30 female non-smokers, and 30 school children) and tested for ex vivo susceptibility toward formaldehyde (FA)-induced genotoxicity. Blood samples were exposed to 150 µM FA for 2 h, and the induction of DNA-protein crosslinks (DPX) in leukocytes was measured by a modification of the alkaline comet assay (i.e., reduction of γ-irradiation induced DNA migration). Removal of DPX was determined by the abolition of FA-induced reduction in DNA migration within 4 h after the end of the exposure. Induction and persistence of FA-induced DNA lesions was also measured by the sister chromatid exchange (SCE) test with cultured lymphocytes after treatment of whole blood cultures with FA (150 µM). Furthermore, the expression (mRNA level) of the GSH-dependent formaldehyde dehydrogenase (FDH, identical to alcohol dehydrogenase 5; ADH5) was measured in leukocytes by quantitative real-time RT-PCR with TaqMan probes. The subjects were also analyzed for the GSTM1 and GSTT1 metabolic gene polymorphisms and a correlation analysis with the investigated genetic endpoints for FA-induced genotoxicity was performed. The results indicate that there are no biologically relevant differences between the three study groups with regard to the various indicators of cellular sensitivity toward FA-induced genotoxic effects and the expression of FDH. The induced genotoxic effects were not associated with polymorphisms in GSTM1 and GSTT1. None of the study groups showed particular mutagen sensitivity toward FA-induced genotoxicity. These results suggest that a low scaling factor to address possible human inter-individual differences in FA-induced genotoxicity could be reasonable.

Does formaldehyde induce aneuploidy?

Formaldehyde (FA) was tested for a potential aneugenic activity in mammalian cells. We employed tests to discriminate between aneugenic and clastogenic effects in accordance with international guidelines for genotoxicity testing. The cytokinesis-block micronucleus test (CBMNT) in combination with fluorescence in situ hybridisation (FISH) with a pan-centromeric probe was performed with cultured human lymphocytes and the human A549 lung cell line. FA induced micronuclei (MN) in binuclear cells of both cell types under standard in vitro test conditions following the OECD guideline 487. FISH analysis revealed that the vast majority of induced MN were centromere negative, thus indicating a clastogenic effect. A similar result was obtained for MN induced by γ-irradiation, whereas the typical aneugens colcemid (COL) and vincristine (VCR) predominantly induced centromere-positive MN. Furthermore, COL and VCR clearly enhanced the MN frequency in mononuclear lymphocytes in the CBMNT, whereas such an effect was not observed for γ-irradiation and FA. In experiments with the Chinese hamster V79 cell line, the aneugens COL and VCR clearly increased the frequency of tetraploid second division metaphases, whereas FA did not cause such an effect. Altogether, our results confirm the clastogenicity of FA in cultured mammalian cells but exclude a significant aneugenic activity.

The in vivo or ex vivo origin of micronuclei measured in human biomonitoring studies.

The micronucleus test (MNT) is a well-established assay in genotoxicity testing and human biomonitoring. The cytokinesis-block micronucleus test (CBMNT) is the preferred method for measuring MN in cultured human lymphocytes from human subjects exposed to genotoxins. However, it is unclear to what extent mutagen exposure either leads to the formation of MN already in vivo or to the formation of MN ex vivo during cell culture as a consequence of persisting DNA damage. MN that were already induced in vivo can be determined by scoring MN in mononuclear lymphocytes 24 h after the start of the lymphocyte culture (i.e. in lymphocytes that did not divide yet). Results obtained for cancer patients after chemotherapy suggest that mutagen exposure in vivo mainly leads to the formation of MN during ex vivo proliferation of lymphocytes as a consequence of mis-repair of persistent damage. If these results also apply to other kinds of mutagen exposure, increased MN frequencies in the CBMNT can only be expected for exposures leading to a sufficient amount of damage that persists during ex vivo lymphocyte culture. For a better understanding of the origin of increased MN frequencies and the correct interpretation of results obtained with the CBMNT, further research is recommended: MN in mononuclear lymphocytes should be additionally scored 24 h after the start of the cultures, comparative investigation with the CBMNT and the MNT with reticulocytes should be performed and the kinetics of MN formation in lymphocyte cultures and the repair capacity of lymphocytes for different kinds of DNA damage should be characterised.

Assessment of genotoxic effects and changes in gene expression in humans exposed to formaldehyde by inhalation under controlled conditions.

Forty-one volunteers (male non-smokers) were exposed to formaldehyde (FA) vapours for 4 h/day over a period of five working days under strictly controlled conditions. For each exposure day, different exposure concentrations were used in a random order ranging from 0 up to 0.7 p.p.m. At concentrations of 0.3 and 0.4 p.p.m., four peaks of 0.6 or 0.8 p.p.m. for 15 min each were applied. During exposure, subjects had to perform bicycle exercises (∼80 W) four times for 15 min. Blood samples, exfoliated nasal mucosa cells and nasal biopsies were taken before the first and after the last exposure. Nasal epithelial cells were additionally sampled 1, 2 and 3 weeks after the end of the exposure period. The alkaline comet assay, the sister chromatid exchange test and the cytokinesis-block micronucleus test were performed with blood samples. The micronucleus test was also performed with exfoliated nasal mucosa cells. The expression (mRNA level) of the glutathione (GSH)-dependent formaldehyde dehydrogenase (FDH, identical to alcohol dehydrogenase 5; ADH5; EC 1.2.1.46) was measured in blood samples by quantitative real-time reverse transcription-polymerase chain reaction with TaqMan probes. DNA microarray analyses using a full-genome human microarray were performed on blood samples and nasal biopsies of selected subgroups with the highest FA exposure at different days. Under the experimental conditions of this study, inhalation of FA did not lead to genotoxic effects in peripheral blood cells and nasal mucosa and had no effect on the expression of the FDH gene. Inhalation of FA did also not cause alterations in the expression of genes in a microarray analysis with nasal biopsies and peripheral blood cells.

Analysis of micronuclei, histopathological changes and cell proliferation in nasal epithelium cells of rats after exposure to formaldehyde by inhalation.

The frequencies of micronuclei (MN), histopathological changes and cell proliferation were determined in the nasal epithelium of male Fischer-344 rats after exposure to formaldehyde (FA) by whole-body inhalation for four weeks (6h/day, 5 days/week). Groups of 12 rats each were exposed to the target concentrations of 0, 0.5, 1, 2, 6, 10 and 15ppm. The micronucleus test (MNT) was performed with nasal epithelial cells prepared from six animals per group. Two thousand cells per animal were analysed for the presence of MN. The other six rats per group were subcutaneously implanted with osmotic pumps containing 5-bromo-2'-deoxyuridine (BrdUrd), three days prior to necropsy. Paraffin sections were made from the nasal cavity (four levels) of these animals for histopathology and cell-proliferation measurements. The frequency of cells with MN was not increased in any of the groups. However, there was also no induction of MN in nasal cells of rats exposed to a single dose of cyclophosphamide (CP, 20mg/kg) by gavage and analysed 3, 7, 14 or 28 days after the treatment. In contrast, nasal epithelial cells from rats exposed to 10 or 15ppm FA vapour showed clear site-specific pathological changes (focal epithelial degeneration, inflammation and squamous metaplasia) in a decreasing gradient (anterior to posterior). Analysis of slides after anti-BrdUrd antibody staining clearly indicated increased cell proliferation (unit length labelling indices, ULLI) after exposure to 6ppm and higher. No treatment-related effects were measured after exposure to 0.5, 1 and 2ppm. When comparing the cell-proliferation rate of normal epithelium with that of directly adjacent metaplastic epithelium, no consistent pattern was found: depending on the location, cell proliferation of normal epithelia was either higher or lower. Our results support previous findings demonstrating local cytotoxic effects in the nose of rats after inhalation of FA. However, induction of MN in the nasal epithelium as an indicator of a mutagenic effect was not seen. Because only limited experience exists for the MNT with rat nasal epithelial cells, this result has to be interpreted with great care. The contribution of mutagenicity to FA's carcinogenicity in rat nasal epithelium remains unclear.

Is individual nasal sensitivity related to cellular metabolism of formaldehyde and susceptibility towards formaldehyde-induced genotoxicity?

Forty-one volunteers (male non-smokers, aged 32 ± 9.6yrs) were tested for susceptibility towards unspecific nasal irritation (sensitivity towards CO(2)) in order to define subgroups of hypersensitive and hyposensitive subjects. Blood samples were taken and the expression (mRNA level) of the GSH-dependent formaldehyde dehydrogenase gene (FDH, identical to alcohol dehydrogenase 5, ADH5; EC 1.2.1.46) was measured in leukocytes by quantitative real-time RT-PCR with TaqMan probes. FDH is the most important enzyme for the metabolic inactivation of FA. Blood samples were exposed to 150µM formaldehyde (FA) for 2h and the induction of DNA-protein crosslinks (DPX) in leukocytes was measured by means of a modification of the alkaline comet assay (i.e., by assessing the reduction of DNA migration induced by γ-radiation). Removal of DPX was determined by the abolition of FA-induced reduction in DNA migration within 4h after the end of the exposure. Furthermore, the induction of sister chromatid exchange (SCE) in cultured lymphocytes was studied after treatment of whole blood cultures with FA (150µM). A correlation analysis was performed for all parameters tested for the whole study group and for hypersensitive and hyposensitive subgroups. The results indicate that despite large differences in CO(2)-sensitivity, the susceptibility towards nasal irritation was not related to the induction of genotoxic effects (DPX, SCE) in peripheral blood or to the protection of blood cells against FA-induced effects (expression of FDH, repair capacity for FA-induced DPX). There was no correlation between CO(2)-sensitivity and the expression of FDH. There was also no close correlation between the various indicators of cellular sensitivity towards FA-induced genotoxic effects and no subgroups were identified with particular mutagen sensitivity towards FA.

Workshop summary: Top concentration for in vitro mammalian cell genotoxicity assays; and report from working group on toxicity measures and top concentration for in vitro cytogenetics assays (chromosome aberrations and micronucleus).

The selection of maximum concentrations for in vitro mammalian cell genotoxicity assays was reviewed at the 5th International Workshop on Genotoxicity Testing (IWGT), 2009. Currently, the top concentration recommended when toxicity is not limiting is 10mM or 5mg/ml, whichever is lower. The discussion was whether to reduce the limit, and if so whether the 1mM limit proposed for human pharmaceuticals was appropriate for testing other chemicals. The consensus was that there was reason to consider reducing the 10mM limit, and many, but not all, attendees favored a reduction to 1mM. Several proposals are described here for the concentration limit. The in vitro cytogenetics expert working group also discussed appropriate measures and level of cytotoxicity. Data were reviewed from a multi-laboratory trial of the in vitro micronucleus (MN) assay with multiple cell types and several types of toxicity measurements. The group agreed on a preference for toxicity measures that take cell proliferation after the beginning of treatment into account (relative increase in cell counts, relative population doubling, cytokinesis block proliferation index or replicative index), and that this applies both to in vitro MN assays and to in vitro chromosome aberration assays. Since relative cell counts (RCC) underestimate toxicity, many group members favored making a recommendation against the use of RCC as a toxicity measure for concentration selection. All 14 chemicals assayed for MN induction in the multi-laboratory trial were detected without exceeding 50% toxicity by any measure, but some were positive only at concentrations with toxicity quite close to 50%. The expert working group agreed to accept the cytotoxicity range recommended by OECD guideline 487 (55±5% toxicity at the top concentration scored). This also reinforces the original intent of the guidance for the in vitro chromosome aberration assay, where ">50%" was intended to target the range close to 50% toxicity.