Mutation Research/Genetic Toxicology and Environmental Mutagenesis
Genotoxic and cytotoxic effects of carbofuran and furadan® on Chinese hamster ovary (CHOK1) cells
Introduction
Carbofuran (CF) is one of the most widely granular employed N-methylcarbamate esters. CF is basically a systemic pesticide used in agriculture to control soil-dwelling and foliar-feeding insects, mites and nematodes in grain, forage, vegetable, seed and fiber crops (www.epa.gov). It is an anticholinesterase compound able to inhibit both acethylcholinesterase and butyrylcholinesterase in vivo and in vitro [1]. The main toxic effect of CF is regarded to result from carbamylation of the catalytic centre of the acethylcholinesterase in the nervous system. This results in accumulation of acetylcholine at nerve synapses and myoneural junctions leading to cholinergic signs and causing toxic effects [2]. The inhibition of the carbomoylated enzyme is labile, of short duration, and reversible compared to that induced by organophosphorus compounds, undergoing spontaneous and rapid reactivation [1], [3], [4].
In general, N-methylcarbamates have low acute toxicity to mammals, and are recognized as non-genotoxic to bacteria, yeast and fungi [5], [6], [7] as well as to mammalian cells [8], [9], [10], [11]. However, CF has been reported to be mutagenic in the Ames test after metabolic activation with S9-mix as well as in the base substitution mutation JK947 Salmonella lactam assay [12]. Furthermore, it has been claimed as a relatively weak mutagen in the Escherichia coli repair test [13]. Gentile and coworkers [6] reported the induction of unscheduled DNA synthesis in human lung fibroblasts. No single-strand breaks detected by alkaline sucrose gradient were induced in in vivo normal human skin fibroblasts [8] or mice peripheral lymphocytes [14]. However, Naravanemi and Jamil [15] reported its induction in in vitro human lymphocytes by the comet assay. The induction of cytotoxicity in human lymphocytes in vitro determined by the trypan blue dye exclusion method [15] and mitotic inhibition in mice bone marrow cells in vivo have been observed [16]. Furthermore, CF has been reported to induce sister chromatid exchanges (SCEs) in Chinese hamster ovary (CHO) cells [17], and in mice [6] and rats [18] exposed in vivo, chromosomal aberrations in human lymphocytes in vitro [15] and mice in vivo [16], as well as mice sperm abnormalities in vivo [16]. Although the induction of micronuclei (MNi) has been observed for mice exposed in vivo [16], Zhou and collaborators [14] were unable to register such effect not only after CF treatment but also with carbofuranphenol, one of its metabolites. While CF induced in vitro DNA fragmentation in rat cortical neurons [19], negative results were observed in Chinese hamster lung fibroblast in vitro [20]. Furthermore, CF has been reported to be teratogenic and embryotoxic [1].
CF is recognized either as a highly toxic pesticide for human health by inhalation and ingestion, or moderately toxic by dermal absorption and when affecting nervous system functions. However, this carbamate has been classified as moderately toxic (class II) by the EPA in spite of the great variety of occupational activities that involve the use of CF around the world (www.epa.org). Due to the lack of both human cancer epidemiology and positive rodent cancer bioassays data, the IARC has not listed this N-methylcarbamate pesticide as carcinogen so far (www.iarc.fr).
Due to its widespread employment in agriculture and household, contamination of food, water and air has become serious and adverse health problem for humans, animals and wildlife. Epidemiological studies suggested that long-term exposure to CF may be associated with increased risk of gastrointestinal, neurological, cardiac dysfunction and retinal degeneration [21], [22]. Therefore, the contamination of environment with CF can easily occur, especially in those countries where it is still in use and the probability of long-term low dose exposure becomes increased. The importance of further studies on this type of pesticide to achieve a complete knowledge on its genetic toxicology seems to be, then, more than evident.
In the present study we employed the SCE, cytokinesis-block MNi frequencies, cell-cycle progression analysis, mitotic index (MI), 3(4,5-dimethylthiazol-2-yl)-2,5-diphenyltetrazolium bromide (MTT) and neutral red (NR) bioassays as different end-points to characterize the genotoxicity and cytotoxicity exerted on Chinese hamster ovary (CHOK1) cells by CF and furadan® (47% CF), one of its commercial formulation currently employed in Argentina.
Section snippets
Chemicals
Carbofuran (CF, 2,3-dihydro-2,2-dimethyl-7-benzo-furanil methylcarbamate, CAS 1563-66-2), 5-bromo-2′-deoxyuridine (BrdUrd, CAS 59-14-3), cytochalasin B from Dreschslera dematioidea (Cyt-B, CAS 14930-96-2), dimethyl sulfoxide (DMSO, CAS 67-68-5), ethidium bromide (CAS 1239-45-8), acridine orange (CAS 10127-02-3), neutral red dye (NRD, CAS 553-24-2), 3(4,5-dimethylthiazol-2-yl)-2,5-diphenyltetrazolium bromide (MTT, CAS 57360-69-7), were obtained from Sigma Chemical Co. (St. Louis, Mo, USA).
Results
Since no difference of SCEs, cell-cycle progression, PRI, MI, micronuclei frequencies, cell viability, and mitotic proliferative factor values were observed between untreated and negative controls (untreated and DMSO-treated cells), pooled data are presented for control values.
The results of SCE analysis in CHOK1 cells treated with different concentrations of CF and F® and the positive control (BLM) are presented in Table 1. As expected, results showed statistically significant differences
Discussion
In the present report, the genotoxicity and cytotoxicity of the systemic pesticide CF and the CF-containing technical formulation F® were evaluated in vitro on CHOK1 cells. The study was conducted using several bioassays for both genotoxicity (e.g., SCE and MNi frequencies), and cytotoxicity (e.g., cell-cycle progression, MI, MTT, and NR). Overall, both chemicals induced higher SCE and MNi frequencies compared to control values. When not toxic, either CF or F® altered the cell-cycle
Conflict of interest statement
None.
Acknowledgements
This study was supported by grants from National University of La Plata (11/N493), National Agency of Scientific and Technological Promotion (PICT 2004 no. 26116), and National Council of Scientific and Technological Research (CONICET, PIP 6386) from Argentina.
References (42)
Anticholinesterases: dramatic aspects of their use and misuse
Neurochem. Int.
(1998)- et al.
An evaluation of the genotoxic properties of insecticides following plant and animal activation
Mutat. Res.
(1982) - et al.
Sister-chromatid exchanges and thioguanine resistance in V79 Chinese hamster cells after treatment with the aneuploidy-inducing agent carbaryl +/− S9 mix
Mutat. Res.
(1984) - et al.
Induction of chromosome aberrations, micronucleus formation and sperm abnormalities in mouse following carbofuran exposure
Mutat. Res.
(2000) - et al.
The delayed genotoxic effect of N-nitroso N-propoxur insecticide in mammalian cells
Food Chem. Toxicol.
(2007) - et al.
Carbofuran induces apoptosis of rat cortical neurons and down-regulates surface alpha7 subunit of acetylcholine receptors
Mol. Cells
(2004) - et al.
N-Nitrosocarbofuran, but not carbofuran, induces apoptosis and cell cycle arrest in CHL cells
Toxicology
(2001) - et al.
Cell kinetics and sister chromatid exchange frequency in human lymphocytes
Mutat. Res.
(1983) - et al.
The end of the (cell) line: methods for the study of apoptosis in vitro
Methods Cell Biol.
(1995) - et al.
Toxicity determined in vitro by morphological alterations and neutral red absorption
Toxicol. Lett.
(1985)
Induction of apoptosis and necrosis in A549 cells by the cis-Pt(II) complex of 3-aminoflavone in comparison with cis-DDP
Mutat. Res.
The in vitro micronucleus technique
Mutat. Res.
Cytogenetic effects of carbofuran in mammals
Mutat. Res.
Comparative evaluation of acetylcholinesterase status and genome damage in blood cells of industrial workers exposed to carbofuran
Food Chem. Toxicol.
Effect of the dithiocarbamate pesticide zineb and its commercial formulation, the azzurro. V. Abnormalities induced in the spindle apparatus of transformed and non-transformed mammalian cell lines
Mutat. Res.
Evaluation of thresholds for benomyl- and carbendazim-induced aneuploidy in cultured human lymphocytes using fluorescence in situ hybridization
Mutat. Res.
Evaluation of DNA damage induced by atrazine and atrazine-based herbicide in human lymphocytes in vitro using a comet and DNA diffusion assay
Toxicol. In Vitro
Effect of dithiocarbamate pesticide zineb and its commercial formulation azzurro. III. Genotoxic evaluation on Chinese hamster ovary (CHO) cells
Mutat. Res.
The chlorophenoxy herbicide dicamba and its commercial formulation banvel induce genotoxicity in Chinese hamster ovary cells
Mutat. Res.
Carbofuran toxicity
J. Toxicol. Environ. Health Part A
Neurotoxic disorders of organophosphorus compounds and their managements
Arch. Iran. Med.
Cited by (49)
An ultrasensitive carbamate pesticide detection sensor based on metal molybdate encapsulated with boron doped reduced graphene oxide nanocomposite
2023, Colloids and Surfaces A: Physicochemical and Engineering AspectsCarbofuran pesticide toxicity to the eye
2023, Experimental Eye Research