Oxidative stress and related gene expression effects of cyfluthrin in human neuroblastoma SH-SY5Y cells: Protective effect of melatonin
Introduction
Pyrethroids are a class of synthetic, neurotoxic, insecticides that are structurally based on purified extracts (pyrethrins) of Chrysanthemum sp. flowers. Characteristically, pyrethroids are described as phenoxybenzoic and cyclopropane moieties joined by an ester bond. Pyrethroids are frequently grouped according to the absence (Type I) or presence (Type II) of a cyano group at the α-carbon of the phenoxybenzoic constituent. The principal target site for pyrethroids is defined as the voltage-dependent sodium channel in the neuronal membrane leading to depolarization and hyperexcitation of the nervous system (Narahashi et al., 1998; Soderlund et al., 2002). This group of compounds has also been shown to act on isoforms of voltage sensitive calcium channels (Hildebrand et al., 2004), thereby contributing to the release of neurotransmitters and hence leading to pyrethroid induced toxicity (Symington and Clark, 2005). Pyrethroids are classified as Type I or Type II based on their chemical structure and also based on the toxic syndrome than they produce in rodents. Type I pyrethroids are associated to hyper-excitation and fine tremors (T-syndrome), and Type II pyrethroids are associated to a more complex syndrome, including clonic seizures (choreoathetosis) and salivation (CS syndrome) (Verschoyle and Aldridge, 1980; Aldridge, 1990). Some pyrethroids produce tremors and salivation, classified as the intermediate TS-syndrome (Soderlund et al., 2002; Soderlund, 2012). Types I and II pyrethroids are extensively applied to control pests in residential and agricultural settings, to treat head lice and scabies in humans and fleas in pets, for public health vector control, and for disinfection of commercial aircrafts (Anadón et al., 2009, Anadón et al., 2013a; USEPA, 2013, 2017). Data from in vivo and in vitro studies have shown that pyrethroids undergo extensive metabolism by carboxylesterases and CYP (Godin et al., 2007; Scollon et al., 2009). However, pyrethroids could interact with the normal metabolism of drugs and xenobiotics and some pyrethroids are found to induce CYP enzyme activities (Yang et al., 2009; Anadón et al., 2013b; Martínez et al., 2018). Moreover, there is evidence suggesting that the detoxifying enzymes of pyrethroids are present at lower levels during fetal and early postnatal development than they are later in life (Cantalamessa, 1993; Sheets, 2000). Previous experiments showed that the toxicity of pyrethroids increases as the age of the animal decreases, so that neonates appear highly sensitive to pyrethroid exposure (Cantalamessa, 1993). A comprehensive review summarizing the existing 22 studies of the developmental neurotoxicity of pyrethroids suggests that pyrethroids may exert developmental neurotoxicity (Shafer et al., 2005). Developmental neurotoxicity involves alterations in behavior, neurohistology, neurochemistry and/or dysmorphology of the central nervous system occurring in the adult age, as a result of neonatal exposure to pyrethroids. Learning and memory impairments in pyrethroid-treated rats and neurobehavioral changes could also be attributed to increased oxidative stress (Liu et al., 2003; Ansari et al., 2012a, b; Nasuti et al., 2007, 2013; Gargouri et al., 2018). Induction of oxidative stress is an important mechanism in pesticide induced toxicities, being the major endpoints damage to DNA, proteins and membrane lipids (Banerjee et al., 2001; Rehman et al., 2006; Tiwari et al., 2010; Romero et al., 2012, 2017). Because, the increased use of pyrethroids has made human exposure almost inevitable, further studies are necessary to assess the neurotoxicity of pyrethroids. It is accepted that animal testing should be reduced, refined or replaced as far as it is practicably possible. Alternative in vitro testing strategies are required, in particular for screening, as part of a tired testing scheme, and routine testing (Anadón et al., 2013c).
Cyfluthrin, a commonly used Type II pyrethroid, was selected for the current investigation. Cyfluthrin, a mixture of four diastereoisomeric pairs of enantiomers (I, II, III, IV) was first registered for use in the United States in 1987 (USEPA, 1987), frequently it is used in veterinary medicine, agriculture against grasshoppers and pests, industrial and residential settings, and public health and, in some countries for the protection of stored products (Ritter and Chappel, 1997; FAO, 1999; Surgan et al., 2002). Despite beneficial roles in agricultural and household products, recent studies in Wistar rats showed that oral exposure to cyfluthrin induced hepatic and renal CYP2E, CYP1A and CYP4A subfamilies, and also increased the β-oxidation of palmitoyl-coenzyme A and carnitine acetyltransferase activity, supporting cyfluthrin classification as a peroxisome proliferator with possible implications in oxidative stress (Anadón et al., 2013b). Also, alteration of GPx and AchE activities in liver and kidney of Wistar rats following intraperitoneal treatment of cyfluthrin has been described (Yilmaz et al., 2015). Cyfluthrin is readily absorbed by the oral route, enters the brain, accumulates in significant quantity and therefore it is appropriate that cyfluthrin affects the CNS function of the non-target organisms (Rodríguez et al., 2018). Because cyfluthrin is one of the more used pyrethroid insecticides worldwide (Surgan et al., 2002), and studies describing mechanisms underlying neurotoxicity of this insecticide (Mense et al., 2006; Eraslan et al., 2007; Rodríguez et al., 2016) are limited, in the present study the possible link between oxidative stress pathways and cyfluthrin neurotoxicity, was investigated. This in vitro study was undertaken (i) to characterize the concentration-dependent cytotoxicity of cyfluthrin using cell viability MTT assay and to determine the protective role of selected antioxidant substances (MEL, Trolox, NAC and Sylibin) on MTT reduction, lipid peroxidation, NO and ROS production and NQO1 activity and (ii) to evaluate gene expressions of apoptosis, proinflammation and oxidative stress (Bax, Bcl-2, Casp-3, BNIP3, AKT1, p53, APAF1, NFκB1, TNFα and Nrf2) mediators as well as to examine by Real-Time PCR array the expression of key genes related to oxidative stress after cyfluthrin and cyfluthrin plus MEL exposure. In the present study, human dopaminergic neuroblastoma cell line (SH-SY5Y) was used as an in vitro model to determine cytotoxic mechanisms of cyfluthrin. The human dopaminergic neuroblastoma cell line, SH-SY5Y, is a commonly used cell line in studies related to neurotoxicity, oxidative stress, and neurodegenerative diseases (Pahlman, 1990; Krishna et al., 2014).
Section snippets
Chemicals and reagents
The test substance, cyfluthrin [cyano (4-fluoro-3-phenoxyphenyl) methyl-3-(2,2-dichloroethenyl)-2,2- dimethylcyclopropanecarboxylate] was provided by Bayer AG (Wuppertal-Elberfeld, Germany) (CAS no: 68359-37-5), ≥97.5% purity, molecular weight 434.3 g/mol.
The compounds 2′,7′-dichlorofluorescin diacetate (DCFH), 3-[4,5 dimethylthiazol-2-yl]-2,5-diphenyl-tetrazolium bromide (MTT), melatonin (N-acetyl-5-methoxytryptamine) (MEL), N-acetyl-cysteine (NAC), Trolox
Cyfluthrin effect on SH-SY5Y cell viability (MTT assay)
In order to evaluate cell survival we used MTT assay. As shown in Fig. 1A, the difference between data of vehicle-treated cells (0.1% DMSO) and control cells was not statistically significant. A 24 h incubation period with cyfluthrin at increasing concentrations (0.01–25 μM) reduced cell viability in a concentration-dependent manner compared with vehicle-treated cells (negative control) (Fig. 1A). The IC30 and IC50 values for cyfluthrin was calculated to be 4.81 ± 0.92 μM and 19.39 ± 3.44 μM,
Discussion
In the environment, individuals are exposed to a multitude of environmental toxicants. Increased production and application of pyrethroid insecticides in recent years have raised serious concerns on potential risks of exposure. Cyfluthrin is a Type II synthetic pyrethroid with a broad spectrum of insecticidal and acaricidal activity used to control wide range of insect pests in a variety of applications (Anadón et al., 2013a). This compound, alike other synthetic pyrethroids Type II, is a
Conclusion
In conclusion, our work includes new data suggesting that oxidative stress mechanisms play a fundamental role in the toxicity induced by the insecticide pyrethroid cyfluthrin. Our work adds information on the possible involvement of several genes mainly AKT1, BNIP3, Nrf2, CYBB, DUOX1, DUOX2, AOX1, and NOS2 in the cyfluthrin toxicity in neuronal cells. This investigation provides a list of genes and pathways for further detailed studies and provides a framework for the observation of possible
Conflicts of interest
The authors declare that there are no conflicts of interest.
Acknowledgments
This work was supported by Project Ref. RTA2015-00010-C03-03 from Ministerio de Economía, Industria y Competitividad, Spain.
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2022, NeuroToxicologyCitation Excerpt :Similarly to OCs and OPs, oxidative stress represents the main mechanism of cytotoxicity for a variety of pyrethroids (Ding et al., 2017; Martínez et al., 2019; Martínez et al., 2020a; Romero et al., 2012; Romero et al., 2015; Romero et al., 2017) (Supplementary Table 2). This oxidative stress leads to increased expression of apoptotic-related genes, oxidative stress response genes and neuroinflammation-related genes such as BAX, Bcl-2, Bcl-2 interacting protein 3 (BNIP3), AKT serine/threonine kinase 1 (AKT1), apoptotic peptidase activating factor 1 (APAF1), nuclear factor kappa B subunit 1 (NFKB1), TNF-α, Nrf2, caspase-3 (CASP3) and tumor protein 53 (P53) in cells treated with cyfluthrin and cypermethrin (Martínez et al., 2019). The two main metabolites of deltamethrin, 2′-OH-deltamethrin and 4′-OH-deltamethrin show higher cytotoxicity and stronger effect on lipid peroxidation and NO production on SH-SY5Y than deltamethrin (Romero et al., 2012).