Elsevier

Toxicology in Vitro

Volume 61, December 2019, 104654
Toxicology in Vitro

In vitro exposure to thiacloprid-based insecticide formulation promotes oxidative stress, apoptosis and genetic instability in bovine lymphocytes

https://doi.org/10.1016/j.tiv.2019.104654Get rights and content

Highlights

  • Calypso® cytotoxicity and genotoxicity was examined in cultured bovine lymphocytes.

  • The insecticide caused decrease in cell proliferation and viability.

  • P53 mediated cell cycle arrest at the G0/G1 phase was found.

  • Apoptosis was detected as a consequence of oxidative damage.

  • Genetic instability was mediated by increased levels of oxidative damage.

Abstract

A proprietary thiacloprid-based neonicotinoid insecticide formulation is widely used in agriculture to protect vegetables and fruit against various pests. However, its effect on animal cells has not been fully elucidated. In this study, bovine peripheral lymphocytes were incubated with different concentrations of this formulation (10; 30; 60; 120 and 240 μg.mL−1) for 4 h to address the potential cytotoxic and genotoxic effects of the insecticide. Insecticide formulation treatment resulted in decreased cell viability and proliferation, p53-mediated cell cycle arrest at the G0/G1 phase, and apoptosis induction accompanied by elevated levels of mitochondrial superoxide and protein carbonylation. Oxidant-based DNA damage and DNA damage response (DDR) were also observed, namely the formation of micronuclei, DNA double-strand breaks and slightly elevated recruitment of p53 binding protein (53BP1) foci. Our results contribute to the elucidation of insecticide effects on animal lymphocyte cultures after short-term exposure. Due to increased application of neonicotinoids worldwide, resulting in both higher yields and adverse effects on non-target animals and humans, further in vivo and in vitro experiments should be performed to confirm their cytotoxic and genotoxic activities during short-term exposure.

Introduction

Pesticides are widely used in agriculture and for veterinary and public health purposes against various kinds of pests. Apart from their beneficial effects such as crop protection, increasing yields and treatment of diseases, they are often detected in foods (Skretteberg et al., 2015), water (Kwon et al., 2017) and in agricultural land (Sankoh et al., 2016) as pollution, and they affect non-target organisms (Saladin et al., 2003) including animals and humans. Occupational and environmental exposures together with poisonings are the most common ways in which humans may be affected. Pesticides are able to form a covalent bond with the nucleophilic centres of cellular molecules. Long-term pesticide exposure can disturb the function of various organs and systems in the body, and has been linked with human chronic diseases such as cancer, neurodegenerative diseases, multiple sclerosis and diabetes (Gangemi et al., 2016; Mostafalou and Abdollahi, 2013; Saravi and Dehpour, 2016).

Neonicotinoids, a class of insecticides acting selectively on the nicotinic acetylcholine receptors (nAChRs) in the central nervous system (CNS) of insects (Han et al., 2018), have replaced classical insecticides due to their lower resistance, higher effectiveness and less danger to mammals (Jeschke et al., 2013). Thiacloprid, a chloronicotinyl neonicotinoid, known under the commercial name Calypso® 480SC (480 g.L−1), is used to protect fruit, vines, vegetables and ornamental plants against sucking and voracious insects. Thiacloprid is extensively metabolized and excreted through urine within 24 h after oral administration. The organ primarily affected in rats, mice and dogs is the liver; prostate toxicity has also been detected in dogs (EFSA, 2019; EPA, 2013). Thiacloprid has been shown to cause fetal resorptions, skeletal retardations and changes in motor and locomotor activity in offspring and adult rats respectively (EPA, 2013). Because its mutagenic and clastogenic effects long remained unnoticed, the active substance was classified as “unlikely to be genotoxic to humans”. On the other hand, carcinogenic changes in rats (thyroid adenomas and uterine adenocarcinomas) and mice (ovarian luteoma) have been observed, and thiacloprid is marked as “likely to be carcinogenic to humans” (EPA, 2013; FAO, 2010). Moreover, it was found that thiacloprid exhibits a high level of acute toxicity to fish (Tomizawa and Casida, 2005).

But its adverse effects on non-target organisms have caught people's attention. Previous studies have found changes in honey bees´ immune response (Brandt et al., 2016) and behaviour (Tison et al., 2016) after pure thiacloprid treatment. Then experiments on greenhouse whitefly Trialeurodes vaporariorum (Safavi and Bakhshaei, 2017), predacious coccinellids (Katsarou et al., 2009) and Daphnia magna (Takács et al., 2017) have shown increased toxicity, lower survival and high mortality (up to 100%) respectively after Calypso insecticide formulation treatment. In fish, namely the early stages of Cyprinus carpio (Velisek and Stara, 2018) growth decrease, development delay and changes in antioxidant enzyme levels were found after exposure to pure thiacloprid. Other researchers have observed micronucleus induction in rats (Hendawi et al., 2016; Sekeroglu et al., 2013) and a decrease in cell proliferation associated with higher levels of chromosomal aberrations in bovine lymphocytes (Galdikova et al., 2015) after treatment with this commercial product. Kocaman et al. (2014) tested pure thiacloprid on human lymphocytes; both genotoxic and cytotoxic effects were detected.

Since there is a lack of data regarding thiacloprid formulation effects on animal/bovine lymphocytes, we decided to analyze the potential cytotoxic and genotoxic effects of thiacloprid-based insecticide formulation (Calypso®) on bovine peripheral lymphocytes in vitro in more detail, especially upon short-term exposure. Cattle represent a suitable model for monitoring of pesticide exposure because of their high ingestion of contaminated feed or polluted soil during grazing (Rhind, 2005). Moreover, milk and other tissues, which could contain accumulated pesticides during their life, may have harmful effects on their offspring, and on humans (Pardio et al., 2012; Pardio et al., 2003). In addition, lymphocytes are widely used to evaluate potential cytotoxic and genotoxic pesticide effects (Ferri et al., 2018; Jacobsen-Pereira et al., 2018; Schwarzbacherova et al., 2017).

Section snippets

Sample collection and cell cultivation

A one-year-old bull (Holstein crossbreed) was the source of whole blood samples, from which peripheral lymphocytes were isolated using HISTOPAQUE®-1077 (Sigma Aldrich, Poznan, Poland) according to the manufacturer's instructions. Then they were cultured at a concentration of 2 × 105 per mL of culture (total volume of culture medium per concentration was 2 mL) in cell culture plates at 37 °C for 24 h. The only exception was the micronucleus test, where the 72 h cultivation is required. Separated

Results

Results of cell viability assessment after 4-h treatment with insecticide concentrations are shown on Fig. 1A. Acridine orange-ethidium bromide staining was used. Gradual decrease in cell viability was seen; the maximum level of cells in late apoptosis (up to 27%; p <0.01) was found at the highest concentration tested (240 μg.mL−1).

For detection of apoptotic events in insecticide-treated cells, Annexin V staining (Fig. 1B, C) and TUNEL assays (Fig. 1D, E) were performed. Apoptotic cell death

Discussion

Neonicotinoids, a new class of insecticides, act preferably on insect nicotinic acetylcholine receptors (nAChRs) as their agonists. These receptors belong in the group of ligand gated ion channels, whose role is to enable rapid excitatory cholinergic transmission (Tomizawa and Casida, 2005; Tomizawa and Yamamoto, 1993). However, various side effects on non-target animals have been observed after exposure to neonicotinoids, such as hepatotoxicity (Toor et al., 2013), neurotoxicity (Lonare et

Conclusions

To conclude, we detected lower cell viability accompanied by DNA damage in bovine lymphocytes after their exposure to thiacloprid-based formulation. Genetic instability was probably mediated by increased levels of oxidative damage. Moreover, apoptosis as a consequence of oxidative damage was detected. Despite the fact that neonicotinoids are already under supervision because of their harmful effects both in insects and mammals, further research should be conducted using different in vitro and

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgement

This study was supported by the Slovak Scientific Agency VEGA [project 1/0242/19] and IGA 01/2019: Assessment of genotoxic and cytotoxic effect of acetamipride insecticide in cell cultures.

References (76)

  • A. Gregorc et al.

    Cell death localization in situ in laboratory reared honey bee (Apis mellifera L.) larvae treated with pesticides

    Pestic. Biochem. Physiol.

    (2011)
  • W.C. Han et al.

    Human exposure to neonicotinoid insecticides and the evaluation of their potential toxicity: An overview

    Chemosphere

    (2018)
  • H. Hintzsche et al.

    Fate of micronuclei and micronucleated cells

    Mutat. Res.-Rev. Mutat. Res.

    (2017)
  • J.H. Jiang et al.

    Effect of acetochlor on transcription of genes associated with oxidative stress, apoptosis, immunotoxicity and endocrine disruption in the early life stage of zebrafish

    Environ. Toxicol. Pharmacol.

    (2015)
  • K. Konca et al.

    A cross-platform public domain PC image-analysis program for the comet assay

    Mutat. Res.

    (2003)
  • H. Kwon et al.

    DNA as an environmental sensor: detection and identification of pesticide contaminants in water with fluorescent nucleobases

    Org. Biomol. Chem.

    (2017)
  • A. Lewinska et al.

    Capsaicin-induced genotoxic stress does not promote apoptosis in A549 human lung and DU145 prostate cancer cells

    Mutat. Res.-Gen. Tox. En.

    (2015)
  • Y.S. Li et al.

    Antioxidant and behavior responses of earthworms after introduction to a simulated vermifilter environment

    Ecol. Eng.

    (2015)
  • T. Liu et al.

    Oxidative stress and gene expression of earthworm (Eisenia fetida) to clothianidin

    Ecotoxicol. Environ. Saf.

    (2017)
  • M. Lonare et al.

    Evaluation of imidacloprid-induced neurotoxicity in male rats: a protective effect of curcumin

    Neurochem. Int.

    (2014)
  • S. Mostafalou et al.

    Pesticides and human chronic diseases: evidences, mechanisms, and perspectives

    Toxicol. Appl. Pharmacol.

    (2013)
  • Z.W. Nie et al.

    Thiamethoxam inhibits blastocyst expansion and hatching via reactive-oxygen species-induced G2 checkpoint activation in pigs

    Cell. Signal.

    (2019)
  • V. Pardio et al.

    Human health risk of dietary intake of organochlorine pesticide residues in bovine meat and tissues from Veracruz, Mexico

    Food Chem.

    (2012)
  • G. Saladin et al.

    Stress reactions in Vitis vinifera L. following soil application of the herbicide flumioxazin

    Chemosphere

    (2003)
  • A.I. Sankoh et al.

    An assessment of the impacts of pesticide use on the environment and health of rice farmers in Sierra Leone

    Environ. Int.

    (2016)
  • V. Schwarzbacherova et al.

    Evaluation of cytotoxic and genotoxic activity of fungicide formulation Tango (R) Super in bovine lymphocytes

    Environ. Pollut.

    (2017)
  • L.G. Skretteberg et al.

    Pesticide residues in food of plant origin from Southeast Asia - a Nordic project

    Food Control

    (2015)
  • S. Soloneski et al.

    Carbamates: a study on genotoxic, cytotoxic, and apoptotic effects induced in Chinese hamster ovary (CHO-K1) cells

    Toxicol. in Vitro

    (2015)
  • J. Surralles et al.

    Induction of micronuclei by five pyrethroid insecticides in whole-blood and isolated human lymphocyte cultures

    Mutat. Res.

    (1995)
  • H.K. Toor et al.

    Imidacloprid induced histological and biochemical alterations in liver of female albino rats

    Pestic. Biochem. Physiol.

    (2013)
  • J. Velisek et al.

    Effect of thiacloprid on early life stages of common carp (Cyprinus carpio)

    Chemosphere

    (2018)
  • C.E.D. Vieira et al.

    DNA damage and oxidative stress induced by imidacloprid exposure in different tissues of the Neotropical fish Prochilodus lineatus

    Chemosphere

    (2018)
  • J. Vignard et al.

    Ionizing-radiation induced DNA double-strand breaks: a direct and indirect lighting up

    Radiother. Oncol.

    (2013)
  • S.G. Wu et al.

    Joint toxic effects of triazophos and imidacloprid on zebrafish (Danio rerio)

    Environ. Pollut.

    (2018)
  • D. Zeljezic et al.

    Cytotoxic, genotoxic and biochemical markers of insecticide toxicity evaluated in human peripheral blood lymphocytes and an HepG2 cell line

    Food Chem.Toxicol.

    (2016)
  • A. Azqueta et al.

    Comet assay to measure DNA repair: approach and applications

    Front. Genet.

    (2014)
  • R. Bal et al.

    Insecticide imidacloprid induces morphological and DNA damage through oxidative toxicity on the reproductive organs of developing male rats

    Cell Biochem. Funct.

    (2012)
  • C.B. Bennett et al.

    Lethality induced by a single site-specific double-strand break in a dispensable yeast plasmid

    P. Natl. Acad. Sci. USA

    (1993)
  • Cited by (20)

    • Genotoxic effects and bacteria-related bioremediation of pesticides

      2022, Pesticides Remediation Technologies from Water and Wastewater
    • Effects of deltamethrin and thiacloprid on cell viability, colony formation and DNA double-strand breaks in human bronchial epithelial cells

      2021, Chemosphere
      Citation Excerpt :

      It can also indicate cytotoxic/cytostatic effects by affecting and/or inhibiting cell proliferation and to influence the cell cycle because of decreasing of mitotic index and proliferation indices in bovine cultures (Galdikova et al., 2019). Decreased cell viability and proliferation values were found in bovine peripheral lymphocytes treated with THI for 4 h. THI induced p53-mediated cell cycle arrest at the G0/G1 phase, apoptosis, formation of micronucleus, DNA double-strand breaks and 53BP1 foci (Schwarzbacherova et al., 2019). Some pesticides can disrupt metabolic processes by causing DNA damage that may reflect the genotoxicity of pesticides (Şenyıldız et al., 2018).

    • Evaluation of the genotoxic potential of cypermethrin, chlorpyrifos and their subsequent mixture, on cultured bovine lymphocytes

      2020, Chemosphere
      Citation Excerpt :

      In addition, binucleated cells with nucleoplasmic bridges and with micronuclei + nuclear buds were only induced with MMC, and were absent in the negative control (Table 1). Other chemical compounds evaluated in CBMN-cyt bovine lymphocytes were doramectin (Anchordoquy et al., 2019), thiacloprid (Galdíková et al., 2015; Schwarzbacherová et al., 2018) bisphenol A (Šutiaková et al., 2014). These reports have also been able to evaluate clastogenic and aneugenic effect, through cultures of bovine lymphocytes.

    View all citing articles on Scopus
    View full text