ABSTRACT
The fungicides strobilurins and succinate dehydrogenase inhibitors (SDHIs) are blockers of the electron transport chain (ETC) in fungi. Here, we show that the exposure for 24 h to kresoxym-methyl, a fungicide from the class of strobilurins, alters the mitochondrial respiration in human HepG2 hepatocytes. In addition, we demonstrate an increase in production of mitochondrial superoxide radical anion, a reduction in ATP level, a decrease in the ratio reduced/oxidized glutathione and a decrease in cell viability (assessed by the LDH assay, Presto Blue assay, and Crystal Violet assay). As kresoxym-methyl is associated to boscalid (SDHI) in commercial formulations, we analyzed a potential exacerbation of the induced mitochondrial dysfunction for this combination. For the highest dose at which kresoxym-methyl (5 µM) and boscalid (0.5 µM) did not induce changes in mitochondrial function when used separately, in contrast, when both fungicides were used in combination at the same concentration, we observed a significant alteration of the mitochondrial function of hepatocytes: there was a decrease in oxygen consumption rate, in the ATP level. In addition, the level of mitochondrial superoxide radical anion was increased leading to a decrease in the ratio reduced/oxidized glutathione, and an increase in viability.
KEYWORDS: Fungicides, mitochondrial function, Electron Paramagnetic Resonance (EPR), cocktail effect, strobilurin, SDHI
GRAPHICAL ABSTRACT
Introduction
Strobilurins form a class of fungicidal compounds that were initially isolated from Strobilurus tenacellus commonly known as the pinecone cap, a fungus that grows on the fallen cones of pine and spruce trees [1]. Synthetic analogs similar to strobilurin A (isolated from S. tenacellus) were developed to improve fungicidal activity and environmental stability [2]. From these efforts, emerged kresoxim-methyl (methyl(E)-methoxyimino-2-[2-(o-tolyloxymethyl)phenyl] acetate, initially referred as BAS 490 F), an active fungicide that specifically inhibits respiration by binding to the mitochondrial cytochrome bc1 complex (complex III) of the electron transport chain [2,3]. Kresoxim-methyl inhibits the growth of mildews, blast, and sheath blight and is largely used worldwide under different commercial brand names (Ayaan®, BAS 490®, Cygnus®, Ergon®, Kriman®, Sarthak®, …). Strobilurins were initially considered as relatively safe for ecosystems. However, in the past few years, a series of studies reported adverse effects on soils organisms, aquatic organisms and mammals (for recent reviews, see [4,5]). Of note, most reports on strobilurins analyzed the effects of azoxystrobin, fluoxastrobin, trifloxystrobin and pyraclostrobin. Kresoxym-methyl has been less studied, but this compound has been shown to change the activity of antioxidant enzymes in grass carp juveniles [6] and in algae [7], to induce mitochondrial dysfunction, metabolic disorders and alteration in the development of zebrafish [8–13], to alter redox balance in a monkey renal cell line [14], to cause neurotoxicity in primary cultured mouse cortical neurons [15], and to alter cellular homeostasis of murine neuroblastoma [16]. Intriguingly, studies reporting the impact of the exposure to strobilurins on human cells are scarce. It was found that trifloxystrobin induces TRAIL-mediated apoptosis and mitochondrial damage in keratinocytes from human skin [17,18], that azoxystrobin and trifloxystrobin inhibit mitochondrial oxidative respiration and alter the abundance of several lipids in neuronal cells [19], and that several strobilurins were toxic for the human hepatocytes HepG2 [20–22].
Because the target of strobilurins is the complex III of the ETC and because mitochondrial perturbations can lead to major effects on metabolism, energy store and production of reactive oxygen species (ROS), it is worth to investigate the consequences of the exposure of human cells to strobilurins. Here, because kresoxym-methyl has been less studied than other strobilurins, we focused on the exposure of human hepatic HepG2 cells exposed to this compound. Kresoxym-methyl is rather lipophilic (logP = 3.4), rapidly absorbed (0.5–1 h after oral administration) with a bioavailability of 63% [23] and a half-life of 19–22 h, with the highest concentrations of compound found in the gut, liver and kidneys after oral administration [24]. AOEL (Acceptable Operator Exposure Level) and ADI (Acceptable Daily Intake) for this compound are 0.9 mg/kg bw/day and 0.3 mg/kg bw/day, respectively. Considering an oral absorption of 63%, for a person of 70 kg body weight with a volume of blood of 5 L, the peak of concentration in the blood would achieve a value around 8 µM or 24 µM after a single exposure dose close to the ADI or the AOEL, respectively. Therefore, our first investigations were carried out in this relevant range of concentration. The study design was similar to our recent study performed on pyraclostrobin, another strobilurin [21]. We first screened a dose-dependent effect on the oxygen consumption rate (OCR) to define the lowest concentration that induced a significant effect on HepG2 cells. Because an alteration of the mitochondrial function may increase the leakage of free electrons and an excessive production of the mitochondrial superoxide radical anion, we evaluated its production by Electron Paramagnetic Resonance (EPR) spectroscopy. We also explored the consequences of the induced mitochondrial dysfunction in terms of ATP level (marker of energy store), the ratio between reduced and oxidized glutathione (redox state marker of oxidative stress), and cytotoxicity. In our previous study, we highlighted a potential cocktail toxic effect for the association strobilurin/SDHI (succinate dehydrogenase inhibitor) using pyraclostrobin/boscalid [21]. Therefore, here, we also investigated a potential similar exacerbation of toxicity for the mixture kresoxym-methyl/boscalid as both compounds are associated in several commercial preparations (Camro®, Castra®, Collis®, …).
Methods and materials
Reagents and cell culture
Kresoxym-methyl PESTANAL (CAS number: 143390-89-0) and Boscalid PESTANAL (CAS number:188425-85-6) were purchased from Supelco (Sigma Aldrich, Hoeilaert, Belgium) and dissolved in DMSO (Sigma Aldrich, Hoeilaert, Belgium). HepG2 cells were acquired from the American Type Culture Collection (ATCC) (Manassas, VA, U.S.A.) and cultured in MEM no nucleosides medium (Thermo Fischer, Merelbeke, Belgium) with 10% of heat-inactivated fetal bovine serum (FBS) (Sigma Aldrich). Cells were maintained at 37°C in humidified atmosphere with 5% CO2.
Oxygen consumption rate
EPR spectroscopy was used to measure variations in oxygen levels in cell media over time [25, 26]. The principle is based on the analysis of the EPR linewidth of an oxygen-sensing probe, 15N-PDT (4-oxo-2,2,6,6-tetramethylpiperidine-d16-15N-1-oxyl) (CDN Isotopes, Pointe-Claire, QC, Canada). As the linewidth of 15N-PDT has been calibrated as a function of the % oxygen present in the sample, it allows the monitoring of OCR in a given preparation of cells. The full detail procedure for measuring OCR by EPR has been described elsewhere [27]. 24 h before the experiment, the cells were treated with fungicides (kresoxym-methyl and/or boscalid) or the appropriate control (DMSO, final concentration 0.1% v/v). The cells were collected to form a stock solution of 5 × 106 cells/mL of culture medium. A mixture containing 60 µL of cell suspension, 40 µL of Dextran solution (20% m/v, from leuconostoc mesenteroides, MW 60-76,000, Sigma Aldrich, Hoeilaert, Belgium), and 4 µL of 15N-PDT (2 mM) was placed into a hematocrit capillary sealed with gum. The sealed capillary was inserted into a quartz tube and put into the EPR cavity heated at 37°C with continuous nitrogen flow. The OCR of cells was measured using a Bruker EMX-Plus spectrometer operating in X-band (9.85 GHz). The experimental parameters were: microwave power, 2.518 mW; modulation amplitude, 5 µT; modulation frequency, 100 kHz; center field, 335 mT; sweep time, 15 s; and sweep width, 1.5 mT. The measurement started 2 min after having mixed 15N-PDT with the cells. EPR spectra were recorded each minute to monitor evolution of oxygen concentration as a function of time.
Mitochondrial superoxide radical anion measurement with EPR
The method is based on the transformation of a cyclic hydroxylamine Mito-TEMPO-H (2-(2,2,6,6-Tetramethylpiperidin-1-oxyl-4-ylamino)−2-oxoethyl triphenylphosphonium chloride) (Enzo Lifescience, Antwerpen, Belgium) into a paramagnetic nitroxide in the presence of reactive species [28,29]. This compound accumulates in mitochondria due to its tryphenylphosphonium (TPP+) group. The full detailed procedure has been described elsewhere [27]. 24 h before the experiment, the cells were treated with fungicides (kresoxym-methyl and/or boscalid) or the appropriate control (DMSO, final concentration 0.1% v/v). The cells were collected to form a stock solution of 15 × 106 cells/mL of culture medium. A mixture containing 37 µL of cell suspension, 0.50 µL of DTPA (100 mM), 5 µL of PBS ((1x) – pH 7.4), and 7.5 µL of Mito-TEMPO-H (1 mM) was placed into a gas-permeable polytetrafluoroethylene tube (inside diameter 0.025 in., wall thickness 0.002 in.) inserted into an open quartz tube. The quartz tube was inserted in the EPR cavity and heated at 37°C with continuous air flow. The formation of nitroxides can be actually due to the presence of superoxide radical anion, but also reaction with other ROS species such as peroxynitrite, and derived nitrogen species. Therefore, to evaluate the specific contribution of the superoxide radical anion to the oxidation of the probe, control experiments were carried out with PEG-SOD2 as a scavenger of the superoxide radical anion [30]. Experiments were done using the same conditions by adding 2.5 µL of PEG-SOD2 (4000 U/mL) incubated for 15 min before adding the Mito-TEMPO-H probe, allowing the cellular uptake of the enzyme and the intracellular scavenging of superoxide. The superoxide radical anion production was monitored using the same spectrometer described for the OCR measurements. The experimental parameters were: microwave power, 20 mW; 100 kHz; modulation amplitude, modulation frequency, 0.1 mT; center field, 336.5 mT; sweep time, 30.5 s; and sweep width,1.5 mT. The measurement started 2 min after mixing the probe with the cells and repeated with a time delay of 40 s between each point. Double integration of the central peak was used to assess the amount of nitroxide produced.
Cell viability
Three assays were used to assess the cytotoxicity: the Presto Blue assay that reflects cytotoxicity through altered metabolic mitochondrial activity, the Crystal Violet assay that stains the nuclear DNA and the proteins of adherent cells, and lactate dehydrogenase (LDH) release assay that quantifies the release of this cytosolic enzyme reflecting cell plasma membrane damage due to cytotoxicity. The protocol we used for the Presto Blue and Crystal Violet assays were described previously [21]. For all three assays, the cells were seeded in a 96-well plate at the density of 10,000 cells/well two days before the experiment. The cells were treated with fungicides (kresoxym-methyl and/or boscalid) or the appropriate control (DMSO, final concentration 0.1% v/v) for 24 h. For the Presto Blue assay, mix of cell medium with 10% (v/v) PrestoBlue cell viability reagent (ThermoFisher) was added to each well and incubated for 2 h at 37°C, protected from the light. Fluorescence was measured at 560 and 590 nm on a SpectraMaxE2 plate reader (Molecular Devices). For the Crystal Violet assay, the cells were washed twice with PBS and 50 µL of Crystal Violet solution (1%) (CAS number: 548-62-9) (Sigma-Aldrich, Hoeilaert, Belgium) and incubated for 20 min at room temperature on an orbital plate (20 oscillations/min). Then, the cells were washed with PBS to eliminate the excess of the Crystal Violet solution and the remaining dead cells. The stain dried for 2 h and was resuspended in methanol. The absorbance was measured at 570 nm. For the LDH assay, the CyQUANTTM LDH Cytotoxicity Assay Kit (Invitrogen, Thermo Fisher Scientific, Dilbeek, Belgium) was used to perform the LDH assay. LDH was quantified via a coupled enzymatic reaction: LDH catalyzes the conversion of lactate to pyruvate via the reduction of NAD+ to NADH. In the presence of diaphorase, the NADH formed in the previous reaction enables the reduction of tetrazolium to a red formazan product, which can be measured spectrophotometrically. Three parameters were measured: maximum LDH release, spontaneous LDH release and LDH release in cells exposed to fungicides. These parameters were quantified following the manufacturer’s instructions. Absorbance was measured with a SpectraMaxE2 plate reader (Molecular Devices) at the wavelength of 490 and 680 nm. To determine LDH activity, the absorbance measured at 680 nm, equivalent to the background, was subtracted from the absorbance measured at 490 nm. All results are presented as a percentage of the control condition (DMSO).
Ratio oxidized / reduced glutathione
Intracellular glutathione levels were assessed using a protocol previously described [21]. The Glutathione colorimetric detection kit (Invitrogen, Waltham, MA, U.S.A., Thermo Fischer) was used. Cells were treated for 24 h with fungicides (kresoxym-methyl and/or boscalid) or the DMSO (control, final concentration 0.1% v/v). The total glutathione (GSHtot) and the oxidized form (GSSG) were quantified according the manufacturer’s instructions. The absorbance was measured with a SpectraMaxE2 plate reader (Molecular Devices) at the wavelength of 405 nm. The reduced form (GSH) was deduced via the subtraction of GSHtot from the GSSG concentration. The proteins were quantified for each condition using a BCA Protein Assay kit (PierceTM, Thermo Fisher). The concentration of intracellular glutathione was normalized by mg of protein. L-Buthionine sulfoximine (L-BSO, 25 µM, Sigma-Aldrich, Hoeilaert, Belgium), a glutathione synthase inhibitor, was used as a positive control.
Intracellular ATP
Celltiter-Glo® Luminescent cell viability assay (Promega, Madison, WI, U.S.A.) was used to quantify the intracellular ATP. The cells were seeded in a 96-well plate at the density of 7,500 cells/well 48 h prior to quantification. Cells were treated for 24 h with fungicides (kresoxym-methyl and/or boscalid) or DMSO (control). Cells were washed twice with PBS (pH 7.4, Thermo Scientific, Waltham, MA, U.S.A.), and the Celltiter-Glo® Reagent mixed in PBS was added following the manufacturer’s instructions. The luminescence was measured after 5 min of incubation using a SpectraMaxE2 plate reader (Molecular Devices, San Jose, CA, U.S.A.). The quantity of ATP was assessed from a calibration curve of ATP disodium (Sigma-Aldrich, Hoeilaert, Belgium) from 10 nM to 1 µM. For each condition, the protein quantification was performed using a BCA Protein Assay Kit (PierceTM, ThermoFisher). The concentration of intracellular ATP was normalized by mg of protein and presented as a percentage of the control condition (DMSO). Oligomycin (0.1 µg/mL m/v, Sigma-Aldrich, Hoeilaert, Belgium), an ATP synthase inhibitor, was used as a positive control.
Statistical analysis
The statistical analysis was performed on GraphPad Prism 9.5 Software. For each experiment, the normality of the data was verified with the Shapiro–Wilk test. The test and number of replicates are provided in each figure. The data shown are mean ± SEM.
Results
Kresoxim-methyl induces a mitochondrial dysfunction in human hepatocytes
To study mitochondrial function following exposure to the fungicide kresoxym-methyl, we first measured the OCR by EPR oximetry in HepG2 cells. The dose-effect relationship study revealed a significant decrease in OCR for concentrations equal to or greater than 7 µM of kresoxim-methyl, compared with untreated cells (Figure 1A). The concentration of 7 µM was therefore selected to assess the impact of kresoxim-methyl on various parameters linked to a potential mitochondrial dysfunction. After 24 h exposure to kresoxim-methyl, we observed a significant increase in the level of mitochondrial superoxide radical anion in HepG2 cells (Figure 1B).
Contrarily to BSO, an irreversible inhibitor of γ-glutamylcysteine synthetase used as a positive control, the exposure to kresoxim-methyl did not significantly alter the level of total glutathione (Figure 2A). In contrast, the ratio GSH/GSSG was significantly reduced after 24 h exposure to 7 µM of kresoxim-methyl, suggesting a consumption of the reduced GSH by the overproduction of ROS (Figure 2B). The level of ATP was also significantly decreased showing an alteration in the energetic metabolism (Figure 2C).
Finally, we studied the cytotoxicity by three different assays that provided consistent results suggesting an alteration of cell viability after 24 h exposure to 7 µM of kresoxim-methyl: we observed a significant increase in LDH release (Figure 3A), decrease in mitochondrial activity (Presto Blue assay) (Figure 3B) and decrease in Crystal Violet staining (Figure 3C). Of note, exposure during 2 h or 8 h did not lead to a significant cytotoxicity (Supplementary Figure 1).
The mixture of kresoxim-methyl and boscalid potentiates a mitochondrial dysfunction in human hepatocytes
To fight against resistance, kresoxim-methyl is often mixed with boscalid (SDHI) in various commercial preparations. To evaluate a potential exacerbation of mitochondrial dysfunction for this mixture of two fungicides, we selected, for each compound, the higher concentrations that did not induce a mitochondrial dysfunction when used individually. While no significant effect was observed at the concentration of 5 µM for kresoxim-methyl and 0.5 µM for boscalid on OCR (Figure 4A) and on mitochondrial superoxide radical anion production (Figure 4B), we observed that combined exposure to both fungicides at the same concentration induced a significant decrease in OCR (Figure 4A) and a significant increase in the mitochondrial superoxide radical anion production (Figure 4B). In Figure 5, we present representative EPR spectra showing the evolution of OCR and mitochondrial ROS over time in control cells and cells exposed to a mixture kresoxym-methyl/boscalid.
While the exposure to the mixture did not alter the level of total glutathione (Figure 6A), we observed a significant decrease in the ratio GSH/GSSG for the mixture (Figure 6B). We also observed that the level of ATP was significantly decreased in HepG2 cell after the exposure to the mixture (Figure 6C).
The cytotoxicity was significantly increased after 24 h exposure to the mixture (Figure 7A). Finally, the three viability assays revealed a significant cytotoxicity after the combined exposure to both fungicides for 24 h (Figures 7 A-B-C). Results for shorter exposure are presented in Supplementary Figure 1.
Discussion
The two main results of the present study are: (1) human hepatic cells exposed to kresoxym-methyl (7 µM) present an alteration in their mitochondrial function; (2) the combined exposure to kresoxym-methyl and boscalid alters the mitochondrial function of human hepatocytes at concentrations that were non-toxic when used individually. A previous screening on a panel of mitochondrial targeting agrochemicals suggested an induced alteration in oxygen consumption by human hepatocytes exposed to kresoxym-methyl (10 µM), as measured by the Seahorse XF technology [20]. Here, using EPR spectroscopy, we confirmed this alteration in OCR after kresoxym-methyl exposure (for concentrations equal or higher than 7 µM). In addition, we demonstrated that the alteration of OCR in hepatocytes led to a boost in mitochondrial superoxide radical anion production. As a consequence, defenses against oxidative stress were depleted, energy stores were altered and viability was decreased (Figure 1). These results are in the same line than our previous observations on pyraclostrobin, another strobilurin [21]. In addition, it was interesting to analyze the effect of a combined exposure to kresoxym-methyl together with boscalid. Boscalid belongs to the class of SDHIs for which toxicity concerns for human cells have been raised in the recent literature [31–33]. We observed a potentiating toxic effect (often called toxic cocktail effect) for the association kresoxym-methyl/boscalid (Figure 2), with an alteration of mitochondrial function at doses that did not present toxicity when used as single agent. Due to the scarcity of biomonitoring studies [34], there is a large uncertainty regarding the real blood levels concentrations that can be achieved after incidental exposure. Despite this lack of data, the concentrations at which we observed a mitochondrial dysfunction (when used alone or in combination) are relevant as they are in the range of concentrations that could be achieved after a single exposure at levels closed to the maximal tolerated exposure (ADI or AOEL) defined by authorities. Putting the results from our previous studies on boscalid [32], on pyraclostrobin [21], on their combination [21] and from the present study on kresoxym-methyl and its combination with boscalid, it becomes clear that agrochemicals targeting the ETC of fungi can also induce detrimental effects on the mitochondrial function of human cells. These observations could lead to a reconsideration of the balance benefice/risk and adaptation of regulation regarding the maximal tolerated levels of exposures. This seems particularly true for cocktails of fungicides. As discussed in our previous paper on the effects of pyraclostrobin, when used alone or in combination with boscalid [21], there is an urgent need for further research to assess the effect of prolonged or repeated exposure to fungicides, not only on hepatocytes, but also on cells more likely to be exposed (i.e. from the lungs, skin, and kidneys) or cells particularly sensitive to mitochondrial dysfunction (i.e. neurons).
In conclusion, this study showed that the exposure to kresoxym-methyl, a fungicide from the class of strobilurins, alters the mitochondrial function in human HepG2 cells (Figure 8): the OCR was decreased, the level of mitochondrial superoxide radical anion was increased, the ATP level was reduced, the ratio reduced/oxidized glutathione was decreased, with a consequent decrease in cell viability. In addition, we observed an exacerbation of the toxicity when kresoxym-methyl was associated with boscalid, a SDHI.
Supplementary Material
Funding Statement
The research was funded by the Fonds National de la Recherche Scientifique (FNRS) – CDR J.0084.22. M.C. and B.M. are Research Fellows (‘Aspirants’) of the Belgian National Fund for Scientific Research (FNRS). This study used the EPR equipment of the Nuclear and Electron Spin Technologies (NEST) platform of the health sector of UCLouvain.
Disclosure statement
No potential conflict of interest was reported by the author(s).
Data availability statement
Rough data are available on request
References
- 1.Anke T, Oberwinkler F, Steglich W, et al. . The strobilurins – new antifungal antibiotics from the basidiomycete Strobilurus tenacellus. J Antibiot. 1977;30:806–810. doi: 10.7164/antibiotics.30.806 [DOI] [PubMed] [Google Scholar]
- 2.Ypema HL, Gold RE.. Kresoxim - methyl: modification of a naturally occurring compound to produce a new fungicide. Plant Dis. 1999;83:4–19. doi: 10.1094/PDIS.1999.83.1.4 [DOI] [PubMed] [Google Scholar]
- 3.Bartlett DW, Clough JM, Godwin JR, et al. . The strobilurin fungicides. Pest Manag Sci. 2002;58:649–662. doi: 10.1002/ps.520 [DOI] [PubMed] [Google Scholar]
- 4.Pandey G, Rathore H.. Toxicity of strobilurins fungicides: a comprehensive review. J Chem Health Risks. 2023;13:207–218. doi: 10.22034/jchr.2023.1960279.1563 [DOI] [Google Scholar]
- 5.Leite FG, Sampaio CF, Cardoso Pires JA, et al. . Toxicological impact of strobilurin fungicides on human and environmental health: a literature review. J Environ Sci Health B. 2024;59:142–151. ahead of print 1-10. doi: 10.1080/03601234.2024.2312786 [DOI] [PubMed] [Google Scholar]
- 6.Liu L, Jiang C, Wu ZQ, et al. . Toxic effects of three strobilurins (trifloxystrobin, azoxystrobin and kresoxim-methyl) on mRNA expression and antioxidant enzymes in grass carp (Ctenopharyngodon idella) juveniles. Ecotoxicol Environ Saf. 2013;98:297–302. doi: 10.1016/j.ecoenv.2013.10.011 [DOI] [PubMed] [Google Scholar]
- 7.Liu X, Wang Y, Chen H, et al. . Acute toxicity and associated mechanisms of four strobilurins in algae. Environ Toxicol Pharmacol. 2018;60:12–16. doi: 10.1016/j.etap.2018.03.021 [DOI] [PubMed] [Google Scholar]
- 8.Jiang J, Wu S, Lv L, et al. . Mitochondrial dysfunction, apoptosis and transcriptomic alterations induced by four strobilurins in zebrafish (Danio rerio) early life stages. Environ Pollut. 2019;253:722–730. doi: 10.1016/j.envpol.2019.07.081 [DOI] [PubMed] [Google Scholar]
- 9.Jiang J, Lv L, Wu S, et al. . Developmental toxicity of kresoxim-methyl during zebrafish (Danio rerio) larval development. Chemosphere. 2019;219:517–525. doi: 10.1016/j.chemosphere.2018.12.061 [DOI] [PubMed] [Google Scholar]
- 10.Mao L, Jia W, Zhang L, et al. . Embryonic development and oxidative stress effects in the larvae and adult fish livers of zebrafish (Danio rerio) exposed to the strobilurin fungicides, kresoxim-methyl and pyraclostrobin. Sci Total Environ. 2020;729:139031. doi: 10.1016/j.scitotenv.2020.139031 [DOI] [PubMed] [Google Scholar]
- 11.Li XY, Qin YJ, Wang Y, et al. . Relative comparison of strobilurin fungicides at environmental levels: Focus on mitochondrial function and larval activity in early staged zebrafish (Danio rerio). Toxicology. 2021;452:152706. doi: 10.1016/j.tox.2021.152706 [DOI] [PubMed] [Google Scholar]
- 12.Wang X, Li X, Wang Y, et al. . A comprehensive review of strobilurin fungicide toxicity in aquatic species: Emphasis on mode of action from the zebrafish model. Environ Pollut. 2021;275:116671. doi: 10.1016/j.envpol.2021.116671 [DOI] [PubMed] [Google Scholar]
- 13.Fang N, Zhang C, Hu H, et al. . Histology and metabonomics reveal the toxic effects of kresoxim-methyl on adult zebrafish. Chemosphere. 2022;309:136739. doi: 10.1016/j.chemosphere.2022.136739 [DOI] [PubMed] [Google Scholar]
- 14.Flampouri E, Mavrikou S, Mouzaki-Paxinou AC, et al. . Alterations of cellular redox homeostasis in cultured fibroblast-like renal cells upon exposure to low doses of cytochrome bc1 complex inhibitor kresoxim-methyl. Biochem Pharmacol. 2016;113:97–109. doi: 10.1016/j.bcp.2016.06.002 [DOI] [PubMed] [Google Scholar]
- 15.Regueiro J, Olguín N, Simal-Gándara J, et al. . Toxicity evaluation of new agricultural fungicides in primary cultured cortical neurons. Environ Res. 2015;140:37–44. doi: 10.1016/j.envres.2015.03.013 [DOI] [PubMed] [Google Scholar]
- 16.Flampouri E, Theodosi-Palimeri D, Kintzios S.. Strobilurin fungicide kresoxim-methyl effects on a cancerous neural cell line: oxidant/antioxidant responses and in vitro migration. Toxicol Mech Methods. 2018;28:709–716. doi: 10.1080/15376516.2018.1506848 [DOI] [PubMed] [Google Scholar]
- 17.Jang Y, Kim JE, Jeong SH, et al. . Trifloxystrobin-induced mitophagy through mitochondrial damage in human skin keratinocytes. J Toxicol Sci. 2016;41:731–737. doi: 10.2131/jts.41.731 [DOI] [PubMed] [Google Scholar]
- 18.Jang Y, Lee AY, Chang SH, et al. . Trifloxystrobin induces tumor necrosis factor-related apoptosis-inducing ligand (TRAIL)-mediated apoptosis in HaCaT, human keratinocyte cells. Drug Chem Toxicol. 2017;40:67–73. doi: 10.1080/01480545.2016.1174871 [DOI] [PubMed] [Google Scholar]
- 19.Nguyen K, Sanchez CL, Brammer-Robbins E, et al. . Neurotoxicity assessment of QoI strobilurin fungicides azoxystrobin and trifloxystrobin in human SH-SY5Y neuroblastoma cells: Insights from lipidomics and mitochondrial bioenergetics. Neurotoxicology. 2022;91:290–304. doi: 10.1016/j.neuro.2022.06.002 [DOI] [PubMed] [Google Scholar]
- 20.van der Stel W, Carta G, Eakins J, et al. . Multiparametric assessment of mitochondrial respiratory inhibition in HepG2 and RPTEC/TERT1 cells using a panel of mitochondrial targeting agrochemicals. Arch Toxicol. 2020;94:2707–2729. doi: 10.1007/s00204-020-02792-5 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 21.Carbone M, Mathieu B, Vandensande Y, et al. . Impact of exposure to Pyraclostrobin and to a Pyraclostrobin/Boscalid Mixture on the mitochondrial function of human hepatocytes. Molecules. 2023;28:7013. doi: 10.3390/molecules28207013 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 22.Wu M, Bian J, Han S, et al. . Characterization of hepatotoxic effects induced by pyraclostrobin in human HepG2 cells and zebrafish larvae. Chemosphere. 2023;340:139732. doi: 10.1016/j.chemosphere.2023.139732 [DOI] [PubMed] [Google Scholar]
- 23.EFSA . Conclusion on the peer review of the pesticide risk assessment of the active substance kresoxim-methyl. 2010;8(11):1891. doi: 10.2903/j.efsa.2010.1891 [DOI] [Google Scholar]
- 24.Kanungo D, Dewhurst I. (2018). Kresoxym-methyl. In: Pesticide residues in food - 2018: toxicological evaluations. pp 225-277. https://inchem.org/documents/jmpr/jmpmono/v2018pr01.pdf.
- 25.Diepart C, Verrax J, Calderon PB, et al. . Comparison of methods for measuring oxygen consumption in tumor cells in vitro. Anal Biochem. 2010;396:250–256. doi: 10.1016/j.ab.2009.09.029 [DOI] [PubMed] [Google Scholar]
- 26.d’Hose D, Danhier P, Northshield H, et al. . A versatile EPR toolbox for the simultaneous measurement of oxygen consumption and superoxide production. Redox Biol. 2021;40:101852. doi: 10.1016/j.redox.2020.101852 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 27.d'Hose D, Gallez B.. Measurement of mitochondrial (dys)function in cellular systems using electron paramagnetic resonance (epr): oxygen consumption rate and superoxide production. Methods Mol Biol. 2022;2497:83–95. doi: 10.1007/978-1-0716-2309-1_5 [DOI] [PubMed] [Google Scholar]
- 28.Dikalov SI, Harrison DG.. Methods for detection of mitochondrial and cellular reactive oxygen species. Antioxid Redox Signal. 2014;20:372–382. doi: 10.1089/ars.2012.4886 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29.Scheinok S, Leveque P, Sonveaux P, et al. . Comparison of different methods for measuring the superoxide radical by EPR spectroscopy in buffer, cell lysates and cells. Free Radic Res. 2018;52:1182–1196. doi: 10.1080/10715762.2018.1541321 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.Scheinok S, Capeloa T, Porporato PE, et al. . An EPR study using cyclic hydroxylamines to assess the level of mitochondrial ROS in superinvasive cancer cells. Cell Biochem Biophys. 2020;78:249–254. doi: 10.1007/s12013-020-00921-6 [DOI] [PubMed] [Google Scholar]
- 31.Bénit P, Kahn A, Chretien D, et al. . Evolutionarily conserved susceptibility of the mitochondrial respiratory chain to SDHI pesticides and its consequence on the impact of SDHIs on human cultured cells. PLoS One. 2019;14:e0224132. doi: 10.1371/journal.pone.0224132 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 32.Bénit P, Goncalves J, El Khoury R, et al. . Succinate dehydrogenase, succinate, and superoxides: a genetic, epigenetic, metabolic, environmental explosive crossroad. Biomedicines. 2022;10:1788. doi: 10.3390/biomedicines10081788 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 33.d'Hose D, Isenborghs P, Brusa D, et al. . The short-term exposure to SDHI fungicides boscalid and bixafen induces a mitochondrial dysfunction in selective human cell lines. Molecules. 2021;26:5842. doi: 10.3390/molecules26195842 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34.Kumar D, Sinha SN, Rajendra S, et al. . Assessing farmer's exposure to pesticides and the risk for non-communicable diseases: a biomonitoring study. Sci Total Environ. 2023;891:164429. doi: 10.1016/j.scitotenv.2023.164429 [DOI] [PubMed] [Google Scholar]
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Data Availability Statement
Rough data are available on request