Genotoxicity Experiments Research Articles

Characterization and safety evaluation of a Deinococcus member as feed additive for hens

As previous studies mainly focus on understanding the mechanisms of radioresistance in Deinococcus bacteria, the present study aimed at characterizing and verifying the safety use of the GKB-Aid 1995 strain, a member of the radiation-resistant bacterial genus Deinococcus, as an ingredient in feed supplements. Using Vitek 2 system and 16S rRNA gene sequencing, GKB-Aid 1995 most resembles Deinococcus grandis. The Ames test, in vitro chromosomal test, in vivo micronucleus test and acute toxicity test were performed subsequently for its safety evaluation. As there is a possibility that the pigment of GKB-Aid 1995 can pass from feed to eggs intended for human consumption, an acute toxicity test was also carried out in pigmented egg yolk. The results confirmed that GKB-Aid 1995 was non-genotoxic in three genotoxicity experiments, and the LD50 of GKB-Aid 1995 and the pigmented egg yolk in ICR mice was greater than 10 and 12 g kg−1 body weight, respectively. Overall, these data indicate that GKB-Aid 1995 is a non-toxic substance with no genotoxicity and is therefore safe to be used as a feed supplement or feed additive. This study suggests there is potential in developing GKB-Aid 1995 as an animal feed additive intended to enhance yolk coloration to meet the demand of consumers.

Broccoli seed extract: Genotoxicity and subchronic toxicity studies

Potential health benefits have been attributed to broccoli consumption. Hence, there is potential for use of broccoli seed extract (BSE) in food or for use as a dietary supplement. To assess the potential safety of a BSE product, three genotoxicity experiments, including an Ames, in vivo mouse micronucleus, and in vivo mouse sperm abnormality assay, were carried out. BSE was subject to an acute oral toxicity test and was evaluated in a 30-day feeding study in rats. BSE showed no mutagenic activity in the Ames assay and no evidence of genotoxic potential in the in vivo assays at doses up to 10 g/kg body weight (bw). The LD50 of BSE in rats was >10 g/kg bw/d. In the 30-day feeding study, in which BSE was administered in the diet to provide doses of 0, 0.3, 1.0, or 3.0 g/kg bw/d, no toxicological significant effects were noted on body weight, body weight gain, organ weights, or on the results of hematological, clinical chemistry and histopathological evaluations. The no-observed-adverse-effect level was considered to be 3.0 g/kg bw/d, the highest dose tested. Collectively, these results support the safe use of BSE as a food ingredient or product.

Red mud a byproduct of aluminum production contains soluble vanadium that causes genotoxic and cytotoxic effects in higher plants

Red mud (RM) is a byproduct of aluminum production; worldwide between 70 and 120million tons is produced annually. We analyzed RM which was released in the course of the Kolontar disaster in Hungary into the environment in acute and genotoxicity experiments with plants which are widely used for environmental monitoring. We detected induction of micronuclei which reflect chromosomal damage in tetrads of Tradescantia and in root cells of Allium as well as retardation of root growth with contaminated soils and leachates. Chemical analyses showed that RM contains metals, in particular high concentrations of vanadium. Follow-up experiments indicated that vanadate causes the effects in the plants. This compound causes also in humans DNA damage and positive results were obtained in carcinogenicity studies. Since it was found also in RM from other production sites our findings indicate that its release in the environment is a global problem which should be studied in more detail. Capsule abstractOur findings indicate that the red mud causes genotoxic effect in plants probably due to the presence of vanadate which is contained at high concentrations in the residue.

Genotoxicity test and subchronic toxicity study with Superba™ krill oil in rats

The safety of krill oil was assessed in a subchronic toxicity study and in a genotoxicity test. In a 13-week study, rats were fed krill oil or control diets. There were no differences noted in body weight, food consumption or in the functional observation battery parameters in either gender. Differences in both haematology and clinical chemistry values were noted in the krill oil-treated groups. However these findings were of no toxicological significance. Significant decreases in absolute and covariant heart weight in some krill oil-treated animals were noted although no corresponding histological changes were observed. In addition, periportal microvesicular hepatocyte vacuolation was noted histologically in males fed 5% krill oil. This finding was not associated with other indications of hepatic dysfunction. Given that the effects of the 13-week toxicity study were non-toxic in nature, the no observed adverse effect level (NOAEL) for the conditions of this study was considered to be 5% krill oil. The genotoxicity experiments documented no mutagenicity of krill oil in bacteria.

Systematic safety evaluation on photoluminescent carbon dots

Photoluminescent carbon dots (C-dots) were prepared using the improved nitric acid oxidation method. The C-dots were characterized by tapping-mode atomic force microscopy, and UV–vis absorption spectroscopy. The C-dots were subjected to systematic safety evaluation via acute toxicity, subacute toxicity, and genotoxicity experiments (including mouse bone marrow micronuclear test and Salmonella typhimurium mutagenicity test). The results showed that the C-dots were successfully prepared with good stability, high dispersibility, and water solubility. At all studied C-dot dosages, no significant toxic effect, i.e., no abnormality or lesion, was observed in the organs of the animals. Therefore, the C-dots are non-toxic to mice under any dose and have potential use in fluorescence imaging in vivo, tumor cell tracking, and others.

Genotoxic evaluation of the antimalarial drugs artemisinin and artesunate in human HepG2 cells and effects on CASP3 and SOD1 gene expressions

The malaria treatment recommended by the World Health Organization involves medicines derived from artemisinin, an active compound extracted from the plant Artemisia annua, and some of its derivatives, such as artesunate. Considering the lack of data regarding the genotoxic effects of these compounds in human cells, the objective of this study was to evaluate the cytotoxicity and genotoxicity, and expressions of the CASP3 and SOD1 genes in a cultured human hepatocellular liver carcinoma cell line (HepG2 cells) treated with artemisinin and artesunate. We tested concentrations of 2.5, 5, 7.5, 10, and 20 μg/mL of both substances with a resazurin cytotoxicity assay, and the concentrations used in the genotoxicity experiments (2.5, 5, and 10 μg/mL) and gene expression analysis (5 μg/mL) were determined. The results of the comet assay in cells treated with artemisinin and artesunate showed a significant dose-dependent increase (P < 0.001) in the number of cells with DNA damage at all concentrations tested. However, the gene expression analysis revealed no significant change in expression of CASP3 or SOD1. Our data showed that although artemisinin and artesunate exhibited genotoxic effects in cultured HepG2 cells, they did not significantly alter expression of the CASP3 and SOD1 genes at the doses tested.

Metabolic profiling of TRPV1 antagonists of the benzothiazole amide series: implications for in vitro genotoxicity assessment

1. In vitro metabolic profiling and in vitro genotoxicity assessment are important aspects of the drug discovery program as they eliminate harmful compounds from further development. In standard in vitro genotoxicity testing, induced rat liver S9 is used as an exogenous bio-activation system for detecting promutagens. In this study we show that rat liver S9 is an insufficient system regarding the conversion of TRPV1 antagonists of the benzothiazole amide series into relevant in vivo metabolites.2. Human and rat hepatocyte experiments demonstrated generation of an aryl amine metabolite that was subsequently N-acetylated. The hydrolyzed metabolites as well as the parent compound were also metabolized into glutathione (GSH) conjugates. Rat liver S9 exhibited a very low amide hydrolysis capacity and no formation of GSH conjugates when supplemented with NADPH and GSH.3. The discrepancy in metabolic capability between hepatocytes and rat liver S9 led to confounding results in in vitro genotoxicity assessment for this chemical class as judged by the results of Ames test, mouse lymphoma assay, SOS/umu test and Comet assay in rat hepatocytes.4. This study highlights the pivotal role that understanding the mechanism of metabolite formation has in interpreting as well as designing reliable and relevant in vitro genotoxicity experiments.

Use of nasal cells in micronucleus assays and other genotoxicity studies

Genotoxicity experiments with exfoliated nasal mucosa cells are a promising minimally invasive approach for the detection of DNA-damaging compounds in ambient air. Results of single cell gel electrophoresis (SCGE) assays with individual cells and organ cultures from bioptic material show that DNA damage caused by compounds such as nitrosamines, polycyclic aromatic hydrocarbons and pesticides can be detected. Biochemical studies indicate that enzymes involved in the metabolism of environmental mutagens are represented in nasal cells. Several protocols for experiments with nasal cells have been developed and it was shown that formaldehyde, metals, styrene and crystalline silica induce DNA damage in SCGE and/or in micronucleus studies; furthermore, it was also found that polluted urban air causes DNA instability in nasal epithelial cells. Comparisons of these data with results obtained in lymphocytes and buccal cells indicate that nasal cells are in general equally sensitive. Broad variations in the baseline levels, differences of results obtained in various studies as well as the lack of information concerning the impact of confounding factors on the outcome of experiments with these cells indicate the need for further standardisation of the experimental protocols.

Inhalation Toxicity of Particulate Matters Doped with Arsenic Induced Genotoxicity and Altered Akt Signaling Pathway in Lungs of Mice

In the workplace, the arsenic is used in the semiconductor production and the manufacturing of pigments, glass, pesticides and fungicides. Therefore, workers may be exposed to airborne arsenic during its use in manufacturing. The purpose of this study was to evaluate the potential toxicity of particulate matters (PMs) doped with arsenic (PMs-Arsenic) using a rodent model and to compare the genotoxicity in various concentrations and to examine the role of PMs-Arsenic in the induction of signaling pathway in the lung. Mice were exposed to PMs 124.4 ± 24.5 μg/m3 (low concentration) , 220.2 ± 34.5 μg/m3 (middle concentration) , 426.4 ± 40.3 μg/m3 (high concentration) doped with arsenic 1.4 μg/m3 (Low concentration) ,2.5 μg/m3 (middle concentration) , 5.7 μg/m3 (high concentration) for 4 wks (6 h/d, 5 d/wk) , respectively in the whole-body inhalation exposure chambers. To determine the level of genotoxicity, Chromosomal aberration (CA) assay in splenic lymphocytes and Supravital micronucleus (SMN) assay were performed. Then, signal pathway in the lung was analyzed. In the genotoxicity experiments, the increases of aberrant cells were concentration-dependent. Also, PMs-arsenic caused peripheral blood micronucleus frequency at high concentration. The inhalation of PMs-Arsenic increased an expression of phosphorylated Akt (p-Akt: protein kinase B) and phpsphorylated mammalian target of rapamycin (p-mTOR) at high concentration group. Taken together, inhaled PMs-Arsenic caused genotoxicity and altered Akt signaling pathway in the lung. Therefore, the inhalation of PMs-Arsenic needs for a careful risk assessment in the workplace.

A statistical evaluation of the potential genotoxic activity in the surface waters of the Golden Horn Estuary

The potential genotoxic activity in the surface waters of the Golden Horn Estuary was statistically evaluated utilizing a combination of appropriate parametric and non-parametric tests. The genotoxic activities that were associated with the water samples were determined by the SOS chromotest microplate assay. This assay utilizes β-galactosidase activity, alkaline phosphatase activity, and four different solvent controls, to generate reliable results when corrected induction factors (CIF) are used as quantitative measurements of genotoxic activity. The CIF values were obtained from a total of 384 different genotoxic experiments that were grouped into subsets according to the respective seasons and the selected sampling locations. A total of 160 subsets were statistically compared to assess any possible differences between the pairs of groups, with 95% confidence limits. The findings of this study clearly indicate that some seasonal variations exist in the CIF values at several sampling sites. However, no potentially hazardous impact to the aquatic environment was found in the estuarine system.

Genotoxicity testing of Cecropia obtusifolia extracts in two in vivo assays: The wing somatic mutation and recombination test of Drosophila and the human cytokinesis-block micronucleus test

Cecropia obtusifolia Bertol. (Cecropiaceae) is a tree that grows in secondary vegetation in the tropical rain forest along both coasts of Mexico. Its leaves are used in folk medicine for the treatment of diabetes mellitus type 2. The aim of the present studies was the evaluation of possible genotoxic effects of the aqueous extract from the leaves of Cecropia obtusifolia by means of two different experimental assay models: the wing somatic mutation and recombination test in flies and the micronucleus test from lymphocytes obtained from patients treated with the extract. No toxicity was found to be induced by the leaves of Cecropia obtusifolia. The Drosophila wing somatic mutation and recombination test (SMART) was applied in the standard version with basal biotransformation activity as well as in a variant version with increased cytochrome P450-dependent bioactivation capacity. The ranges of exposure concentrations for these genotoxicity experiments were between 0.82 and 13.32 mg/ml. The extract did not produce any genotoxic effect; however it showed a non significant antigenotoxic effect. The human micronucleus assay in vivo was performed with cultured lymphocytes obtained from six diagnosed type 2 diabetic patients treated daily with 13.5 g of the aqueous extract between 32 and 85 days. No statistically significant increases in cytotoxicity and/or genotoxicity between control and diabetic blood samples were observed.

Genetic and epigenetic mechanisms in metal carcinogenesis and cocarcinogenesis: nickel, arsenic, and chromium.

Chronic exposure to nickel(II), chromium(VI), or inorganic arsenic (iAs) has long been known to increase cancer incidence among affected individuals. Recent epidemiological studies have found that carcinogenic risks associated with chromate and iAs exposures were substantially higher than previously thought, which led to major revisions of the federal standards regulating ambient and drinking water levels. Genotoxic effects of Cr(VI) and iAs are strongly influenced by their intracellular metabolism, which creates several reactive intermediates and byproducts. Toxic metals are capable of potent and surprisingly selective activation of stress-signaling pathways, which are known to contribute to the development of human cancers. Depending on the metal, ascorbate (vitamin C) has been found to act either as a strong enhancer or suppressor of toxic responses in human cells. In addition to genetic damage via both oxidative and nonoxidative (DNA adducts) mechanisms, metals can also cause significant changes in DNA methylation and histone modifications, leading to epigenetic silencing or reactivation of gene expression. In vitro genotoxicity experiments and recent animal carcinogenicity studies provided strong support for the idea that metals can act as cocarcinogens in combination with nonmetal carcinogens. Cocarcinogenic and comutagenic effects of metals are likely to stem from their ability to interfere with DNA repair processes. Overall, metal carcinogenesis appears to require the formation of specific metal complexes, chromosomal damage, and activation of signal transduction pathways promoting survival and expansion of genetically/epigenetically altered cells.

Genotoxicity and subchronic toxicity studies of DHA-rich oil in rats

Polyunsaturated fatty acids, including docosahexaenoic acid (DHA), are natural constituents of the human diet. DHA-algal oil is produced through the use of the non-toxigenic and non-pathogenic marine protist, Ulkenia sp. The safety of DHA-algal oil was assessed in a subchronic toxicity study and in genotoxicity studies. In a 90-day study, rats were orally administered water or DHA-algal oil at concentrations of 0, 500, 1000, and 2000 mg/kg in combination with 2000, 1500, 1000 or 0 mg/kg DHA-containing fish oil, respectively. Additional animals were administered water, 2000 mg/kg DHA-algal oil, or 2000 mg/kg fish oil for 90 days, followed by a 4-week recovery phase. No treatment-related effects were observed in clinical observations, food and water consumption, mortality, gross pathology, and histopathology. Increased body weights and liver weights in oil-treated groups were attributed to the large lipid load and were not regarded as toxicologically significant. Furthermore, no treatment-related differences in the measured parameters between the DHA-algal oil and fish oil groups were detected. In genotoxicity experiments, DHA-algal oil exerted no mutagenic activity in various bacterial strains, nor did it induce chromosomal aberrations in Chinese hamster fibroblast cells. These results support the safety of DHA-algal oil as a dietary source of DHA.

A phytotherapeutic extract of Equisetum myriochaetum is not genotoxic either in the in vivo wing somatic test of Drosophila or in the in vitro human micronucleus test

Equisetum myriochaetum is a Mexican plant used in folk medicine to treat kidney diseases and type 2 diabetes mellitus. The main constituents of the phytoextract are flavonol glycosides (kaempferol), phytoesterols and carbohydrates. In this study, phytotherapeutic extracts from Equisetum myriochaetum were investigated for genotoxicity in the in vivo wing spot test in Drosophila melanogaster and in the in vitro human micronucleus test. No acute toxicity of the phytoextract could be determined in Drosophila or in human lymphocytes in culture, ranging from 0.78 μg/ml to 3700 μg/ml for the wing assay and between 12.5 μg/ml and 500 μg/ml for the micronucleus test. The Drosophila wing somatic mutation and recombination test (SMART) was applied in the standard version with basal biotransformation activity as well as in a variant version with increased cytochrome P450-dependent bioactivation capacity. The ranges of exposure concentrations for these genotoxicity experiments were between 0.78 μg/ml and 500 μg/ml. The human micronucleus test in vitro was performed with cultured lymphocytes obtained from four healthy donors. The concentrations assayed for these experiments ranged from 12.5 μg/ml to 500 μg/ml. No statistically significant increase was observed between treated series when compared with a concurrent negative (water solvent) control series in either assay. The results demonstrate clearly that the phytotherapeutic extract from Equisetum myriochaetum, under the experimental conditions tested, is not genotoxic in the in vivo experiments or in the in vitro studies.

A Rapid Method for Comparing the Oncogenic Potential of Retroviral Vectors.

Retroviral gene transfer has successfully cured patients with X-linked severe combined immunodeficiency (X-SCID). Unfortunately, three of the treated patients developed leukemia at least in part due to insertional activation of a neighboring gene. Further advances of this exciting therapeutic modality will require safer viral vectors. Genotoxicity experiments in animals, although an important preclinical study, are not practical for screening large numbers of vectors. We have developed a rapid plasmid-based assay to compare downstream gene activation by retroviral vectors. We constructed a plasmid, pACT, that contains a minimal CMV promoter, an internal ribosome entry site (IRES) and a luciferase reported gene followed by a polyadenylation site. Four different proviral constructs containing identical internal PGK-EGFP expression cassettes were inserted upstream of the minimal promoter and nucleofected (Amaxa Biosystems) into K562 cells. The relative luciferase activation of each provirus was determined and compared to cells nucleofected with the basic pACT plasmid. The relative luciferase activation by a plasmid containing a Moloney murine leukemia virus (MLV) vector provirus with full length long terminal repeats (LTRs) was 144, 1230, and 4525 at 1, 2 and 4 days post nucleofection, respectively. Changing the orientation of the proviral DNA did not significantly change the results, consistent with an enhancer effect from the proviral LTRs. In comparison, the relative luciferase activation by a plasmid containing a self inactivating (SIN) MLV vector provirus with LTR deletions was only 59, 90 and 170, respectively, and was reduced by greater than 90% with the reverse orientation consistent with residual activation by read-through transcription. For plasmids containing the HIV SIN vector provirus, the relative luciferase activation was 48, 45 and 52, respectively at 1, 2 and 4 days post nucleofection, and decreased by >90% with the inverse orientation. The relative luciferase activation for plasmids containing the Foamy Virus (FV) vector provirus, also a “SIN” vector, was the least, only 3, 2 and 6, respectively, at 1, 2 and 4 days post nucleofection. Therefore, all three SIN vectors (MLV, HIV and FV) produced significantly less downstream gene activation than a conventional MLV vector, with the FV vectors being the lowest. Additional studies comparing various internal promoters and vectors will also be presented. These results demonstrate the usefulness of the pACT assay system to identify safer retroviral vectors.

Use of human-derived liver cell lines for the detection of environmental and dietary genotoxicants; current state of knowledge.

This article gives an overview of the results of genotoxicity tests, which have been conducted within the last 5 years with the human liver cell line HepG2. It is an update of an earlier review from 1998 (by Knasmüller et al.). In addition, a number of publications are discussed which are relevant for the use of human derived liver cell lines in genetic toxicology. They concern the establishment of new endpoints, the development of new cell lines and possible pitfalls and problems. HepG2 cells have been used to test a wide variety of compounds over the last years. The most interesting observations are that the cells are highly sensitive toward polycyclic aromatic hydrocarbons and that genotoxic effects are seen with a number of carcinogenic mycotoxins, that give negative results in other in vitro assays. Carcinogenic metals such as As and Cd caused positive results as well, whereas only marginal or negative results were seen with nitrosamines. The low sensitivity toward these latter carcinogens is probably due to a lack of cytochrome P4502E1 which catalyses their activation. Also, a number of structurally different synthetic pesticides as well as bioactive plant constituents ("natural pesticides") have been tested and with some of them genotoxic effects were found. In most experiments, the formation of micronuclei was used as an endpoint; however also the single cell gel electrophoresis assay is increasingly used. Several transfectant lines of HepG2 have been constructed which express increased levels of phase I enzymes (such as CYP1A1, CYP1A2, CYP2E1 etc.); furthermore, cell lines became available which express human glutathione-S-transferases. These new clones might be particularly useful for the investigation of specific classes of genotoxicants and also for mechanistic studies. Apart from HepG2 cells, a number of other human derived liver cell lines have been isolated, but so far no data from genotoxicity experiments are available, except for Hep3B cells, which were compared with HepG2 and found to be less sensitive in general. Studies with HepG2 clones of a different origin indicate that the cells differ in regard to their sensitivity toward genotoxicants; also medium effects and the cultivation time might affect the outcome of genotoxicity studies. Overall, the results support the assumption that HepG2 cells are a suitable tool for genotoxicity testing.

Genotoxicity evaluation of polluted ground water in human peripheral blood lymphocytes using the comet assay

This paper presents the genotoxicity experiments with the ground water collected from an area under the influence of textile dyeing and bleaching industries in Tirupur, Tamilnadu, India. The alkaline single cell gel electrophoresis (SCGE) assay was performed in vitro with human peripheral blood lymphocytes. The cells were exposed to two doses of non-volatile organic agents extracted from ground water samples. Ground water samples were collected from 12 locations distributed in and around Tirupur and extracts were taken at different pHs (without pH adjustment and acidic pH 2.0). The persistence of the DNA damage after exposure to the organic extracts was also studied. All the samples were found to contain substances capable of inducing DNA damage in human lymphocytes. Extracts from acidified waters (pH=2.0) were found to induce more DNA damage than extracts from without pH adjustment (natural pH). The DNA damage was not fully repaired after incubation for 2 h at 37 °C. The chemical characterization of the sub-fractions revealed the existence of aromatic amines in the extracts, which may be responsible for the DNA damaging activity of the water samples. The results of this investigation demonstrate the application of the comet assay in environmental monitoring studies.

Genotoxic and Ecotoxic Effects of Groundwaters and Their Relation to Routinely Measured Chemical Parameters

The primary aim of the present investigation was to study possible adverse effects of groundwater from an aquifer south of Austria's capital, Vienna, and to relate these toxicological effects to routinely measured physical/chemical parameters. Fourty-three water samples were tested for genotoxic and ecotoxic effects. For genotoxicity testing the Salmonella/microsome assay, the micronucleus test with primary rat hepatocytes and micronucleus tests with plants (Tradescantia, Vicia faba) were used. In ecotoxicity tests, algae (Selenastrum capricornutum), water cress (Lepidium sativum), and water flea (Dapnia magna) were studied as target organisms. In genotoxicity assays, 10 samples (23%) gave a weak positive response with a single end point, but only one sample (2%) was genotoxic in three different test systems. Thirty-six samples (86%) caused adverse effects in ecotoxicity assays. Plants (algae and water cress) were more sensitive than daphnie. No correlations between toxic effects and physical/chemical parameters were detected. The genotoxicity experiments indicate presently a low risk from genotoxic compounds. The ecotoxic (especially phytotoxic) properties of many water samples raise concern about their suitability for irrigation purposes. The lacking correlation between results from toxicity tests and physical/chemical data indicates that it is presently impossible to predict toxic properties from routine physical/chemical measurements with a sufficient level of safety. It is therefore important to include biological toxicity assays in groundwater monitoring programs.

Formation of DNA Adducts in Skin, Lung and Lymphocytes After Skin Painting of Rats with Undiluted Bitumen or Coal-Tar Fume Condensates

Abstract During the hot application of bitumen-containing materials, e.g. in road paving or roofing, fumes are emitted that contain traces of polycyclic compounds. Although worker exposures to these fumes are low, they might lead to health problems. Bitumens have been classified by IARC in group 3 (compounds not classifiable as to their carcinogenicity to humans) and extracts of steam-refined and air-refined bitumens in group 2B (possible human carcinogens). Carcinogenicity and genotoxicity experiments by skin painting have to date always involved dilution of bitumens or their fume condensates in solvents. In order to determine whether undiluted bitumen fume condensates (BFCs) are potentially genotoxic to humans, these were produced by trapping the particulates on a glass fibre filter and the semi-volatiles (vapours) on XAD-2 resin. the benzene soluble matter (BSM) from the particulates phase was combined with the diethyl ether extract of the XAD resin that contained the semi-volatiles. the ether was evap...

Optimal experimental design and sample size for the statistical evaluation of data from somatic mutation and recombination tests (SMART) in Drosophila

In genetic toxicology it is important to know whether chemicals should be regarded as clearly hazardous or whether they can be considered sufficiently safe, which latter would be the case from the genotoxicologist's view if their genotoxic effects are nil or at least significantly below a predefined minimal effect level. A previously presented statistical decision procedure which allows one to make precisely this distinction is now extended to the question of how optimal experimental sample size can be determined in advance for genotoxicity experiments using the somatic mutation and recombination tests (SMART) of Drosophila. Optimally, the statistical tests should have high power to minimise the chance for statistically inconclusive results. Based on the normal test, the statistical principles are explained, and in an application to the wing spot assay, it is shown how the practitioner can proceed to optimise sample size to achieve numerically satisfactory conditions for statistical testing. The somatic genotoxicity assays of Drosophila are in principle based on somatic spots (mutant clones) that are recovered in variable numbers on individual flies. The underlying frequency distributions are expected to be of the Poisson type. However, some care seems indicated with respect to this latter assumption, because pooling of data over individuals, sexes, and experiments, for example, can (but need not) lead to data which are overdispersed, i.e, the data may show more variability than theoretically expected. It is an undesired effect of overdispersion that in comparisons of pooled totals it can lead to statistical testing which is too liberal, because overall it yields too many seemingly significant results. If individual variability considered alone is not contradiction with Poisson expectation, however, experimental planning can help to minimise the undesired effects of overdispersion on statistical testing of pooled totals. The rule for the practice is to avoid disproportionate sampling. It is recalled that for optimal power in statistical testing, it is preferable to use equal total numbers of flies in the control and treated series. Statistical tests which are based on Poisson expectations are too liberal if there is overdispersion in the data due to excess individual variability. In this case we propose to use the U test as a non-parametric two-sample test and to adjust the estimated optimal sample size according to (i) the overdispersion observed in a large historical control and (ii) the relative efficiency of the U test in comparison to the t test and related parametric tests.