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BY 4.0 license Open Access Published by De Gruyter October 7, 2020

Occupational exposure in lead and zinc mines induces oxidative stress in miners lymphocytes: Role of mitochondrial/lysosomal damage

  • Enayatollah Seydi , Mahshid Soltani , Maral Ramazani , Mohammad Hadi Zarei and Jalal Pourahmad EMAIL logo

Abstract

The purpose of this research was to determine mitochondrial and lysosomal damage and oxidative stress status in blood lymphocytes of lead-zinc miners. This research was performed in 10 mine workers who have been in contact with lead and zinc in comparison to a control group containing 10 healthy volunteers. Lymphocytes were isolated from peripheral blood using the Ficoll standard method and then mitochondrial and lysosomal damage and oxidative stress were evaluated. The level of reactive oxygen species (ROS), collapse in the mitochondrial membrane potential (MMP) collapse, and glutathione disulfide (GSSG) content, and lysosomal damage in miners were higher than the control group. Also, viability and glutathione (GSH) content were decreased. The lymphocytes of workers of a lead-zinc mine are more susceptible to oxidative stress, mitochondrial and lysosomal damage. The proper use of safety equipment can reduce the risk of toxic agents and their subsequent hazards for mine workers.

1 Introduction

In developing countries, heavy metals pollution is one of the serious problems and public awareness of their toxic effects is increasing (Qu et al., 2012). Occupational exposure is one of the most important sources of exposure to lead (Conterato et al., 2013; Ghanwat et al., 2016; Hsieh et al., 2017). The lead enter to the workers’ body through the inhalation route, and then can accumulate in the vital organs of the body (Ghanwat et al., 2016; Hsieh et al., 2017; Kalahasthi and Barman, 2018). Inhalation, skin and ingestion are among the most important routes of exposure to zinc. According to the National Institute for Occupational Safety and Health (NIOSH), the number of workers exposed with zinc fumes is around 50,000 (Ricco et al., 2018). According to the Occupational Safety and Health Administration (OSHA), the blood lead level (BLL) in workers is less than 40 μg/dL (Basit et al., 2015).

Research has shown that heavy metals can increase the generation of reactive oxygen species (ROS) and oxidative stress through Fenton like reaction (Qu et al., 2019). Oxidative stress is one of the most important mechanisms involved in lead toxicity (Kasperczyk et al., 2014b; Qu et al., 2019; Shraideh et al., 2018). In addition, lead can induce apoptosis signaling (Qu et al., 2019). It has been shown that lead has a high affinity to the sulfhydryl groups (SH) of proteins. Sulfhydryl groups play an important role in antioxidant enzymes against the generation of free radicals (Conterato et al., 2013; Kasperczyk et al., 2014a, 2016; Shraideh et al., 2018). An in vivo research has shown that overexposure to zinc affects the function of lymphocytes. Also, zinc excess has an effect on ROS generation, induction of oxidative stress, cytochrome c release, and induction of apoptosis (Plum et al., 2010). Exposure to lead leads to defects in lymphocyte function, and also changes in the ratio of lymphocytes subpopulation (Zarei et al., 2017).

Mitochondria is the main source of ROS generation in the cell, and damage to the mitochondria causes excessive release of ROS and induction of oxidative stress (Zarei et al., 2018a). Sulfhydryl groups are located in all parts of the mitochondrial respiratory chain (Fedotcheva et al., 2012). Lead with a high affinity to sulfhydryl groups induces ROS generation and oxidative stress (Conterato et al., 2013; Kasperczyk et al., 2014a, 2016; Shraideh et al., 2018). The damage to the mitochondria can disrupt the mitochondrial membrane potential (MMP) and release the cytochrome c and eventually induce cell death. Disruption of the lysosomal membrane is due to hydrogen peroxide (H2O2) transmission of mitochondria to cytosol and activation of the fenton reaction (Zarei et al., 2018a). In this research, we aimed to study the oxidative stress marker and mitochondrial and lysosomal damage in relation to exposure to lead and zinc in peripheral blood lymphocytes taken from workers of a lead-zinc mine.

2 Results and discussion

2.1 Cell viability

The purpose of this study was to investigate the oxidative stress marker and mitochondrial and lysosomal damage in workers of a lead-zinc mine using blood lymphocytes. A few studies have been done on cytotoxic effects of heavy metals on human lymphocytes. Initially, the viability of lymphocytes of workers in the lead and zinc mine was evaluated. In this study, the survival of lymphocytes in exposed group is less than that of the un-exposed group (Figure 1a). These results are in agreement with previous studies shown the toxicity of lead and zinc in human lymphocytes using in vitro studies (Steffensen et al., 1994; Zarei et al., 2017, 2018a). In the exposed and un-exposed groups, there is a no significant difference in the cell viability based on the comparison of age, employment and duration of work (Figures 1b-d).

Figure 1 The cell viability assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). **** P < 0.0001.
Figure 1

The cell viability assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). **** P < 0.0001.

2.2 ROS generation

In the blood lymphocytes isolated from the exposed group, the level of ROS generation is significantly higher than that of the un-exposed group. The results show that exposure to lead and zinc increases ROS generation in isolated lymphocytes (Figure 2a). In the exposed group, there is a significant difference in the level of ROS based on the comparison of age, employment and duration of work (Figures 2b-d).

Figure 2 The mitochondrial ROS assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). * P < 0.05, ** P < 0.01, *** P < 0.001 and **** P < 0.0001. The unit of measurement of ROS formation is based on fluorescent intensity.
Figure 2

The mitochondrial ROS assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). * P < 0.05, ** P < 0.01, *** P < 0.001 and **** P < 0.0001. The unit of measurement of ROS formation is based on fluorescent intensity.

Studies showed that excessive exposure to heavy metals such as lead and zinc increases the level of ROS and oxidative stress (Akram et al., 2018; Kasperczyk et al., 2017; Plum et al., 2010; Zarei et al., 2017, 2018a). Another study showed that the level of free radicals in workers exposed to lead was higher than that of the control group (Fracasso et al., 2002). A significant increase in ROS generation was observed in the blood lymphocytes isolated from the lead and zinc mine workers. Mitochondria (complexes 1 and III) are considered as one of the important sources in the generation of ROS. ROS play various roles in the different concentrations (Dan Dunn et al., 2015; Li et al., 2013; Zorov et al., 2014). It has been shown that heavy metals with an effect on mitochondria increase the generation of ROS (Belyaeva et al., 2012; Ercal et al., 2001; Liu et al., 2017; Ranjbar et al., 2014). Therefore, damage to mitochondria with consequences such as an increase in the generation of ROS, induces oxidative stress and cell death.

2.3 MMP assay

As shown in Figure 3, there was a significant MMP collapse in the blood lymphocytes isolated from lead and zinc mine workers compared to control group (Figure 3a). An increase in fluorescence intensity (Rh 123) indicates a collapse in the MMP. In the exposed and un-exposed groups, there is a no significant difference in the MMP collapse based on the comparison of age, employment and duration of work (Figures 3b-d).

Figure 3 MMP assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). **** P < 0.0001. The unit of measurement of MMP collapse is based on fluorescent intensity.
Figure 3

MMP assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). **** P < 0.0001. The unit of measurement of MMP collapse is based on fluorescent intensity.

MMP collapse was evaluated as one of the important parameters of mitochondrial damage. A significant collapse in MMP was observed in the blood lymphocytes isolated from the lead and zinc mine workers compared to control healthy group in our research. Changes in MMP are one of the important indicators for the evaluation of mitochondrial function. Also, the collapse of the MMP is associated with cell death induction. Therefore, mitochondria in in vitro toxicity research are usually used as an important target (Kamogashira et al., 2017; Sakamuru et al., 2016). These results are in agreement with previous studies (Chen et al., 2003; Zarei et al., 2017, 2018a).

2.4 GSH and GSSG content assay

The results showed that GSH content in workers in lead and zinc mine was significantly lower than un-exposed group (Figure 4a). Also, GSSG content in workers in lead and zinc mine was significantly higher than control group (Figure 5a). In the exposed group, the results showed a significant difference between GSH (Figures 4c,d), and GSSG (Figures 5c,d) levels based on employment and duration of work.

Figure 4 GSH content assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). * P < 0.05, ** P < 0.01 and **** P < 0.0001.
Figure 4

GSH content assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). * P < 0.05, ** P < 0.01 and **** P < 0.0001.

Figure 5 GSSG content assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). * P < 0.05, ** P < 0.01 and **** P < 0.0001.
Figure 5

GSSG content assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). * P < 0.05, ** P < 0.01 and **** P < 0.0001.

Heavy metals such as lead and zinc have the ability to reduce GSH level which plays an important role in the antioxidant system (Conterato et al., 2013; Kasperczyk et al., 2014a, 2017; Shraideh et al., 2018; Zarei et al., 2017, 2018a). Our results indicated a decline in GSH content and increased GSSG content in blood lymphocyte taken from worker groups compared to those of control group. It has been suggested that one of the mechanisms by which the level of GSH content is reduced is due to the high tendency of lead to complex sulfhydryl groups. This group plays an important role in antioxidant defense (Kasperczyk et al., 2016; Shraideh et al., 2018).

2.5 Lysosomal damage

As shown in Figure 5, there was a significant lysosomal damage in the blood lymphocytes isolated from the lead and zinc mine workers compared to un-exposed group (Figure 6a). The results show that lysosomes are similar to mitochondria targeted at lead and zinc. In the exposed and un-exposed groups, there is a no significant difference in the lysosomal damage based on the comparison of age, employment and duration of work (Figures 6b-d). Disruption of the lysosomal membrane is due to hydrogen peroxide (H2O2) transmission from mitochondria to cytosol and activation of the fenton reaction (Zarei et al., 2018a). Our results indicated a damage in the lysosomal membrane in miners group compared to the control group.

Figure 6 Lysosomal damage assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). **** P < 0.0001. The unit of measurement of lysosomal damage is based on fluorescent intensity.
Figure 6

Lysosomal damage assay. (a) Comparison between exposure and non-exposure groups. (b) Comparison between the exposed and unexposed groups based on age (year). (c) Comparison between the exposed and unexposed groups based on employment (year). (d) Comparison between the exposed and unexposed groups based on duration of work (hours). Data are presented as mean ± SD (n = 20). **** P < 0.0001. The unit of measurement of lysosomal damage is based on fluorescent intensity.

3 Conclusion

In conclusion, we showed that mitochondria and lysosomes are targeted at lymphocytes isolated from workers in lead and zinc mine. Also, the level of ROS, oxidative stress, collapse of MMP and GSSG content has increased in the lymphocytes isolated from lead and zinc miners.

Experimental

Chemical

2,7-dicloroflurescein diacetate (DCHF-DA), rhodamine 123 (Rh 123), MTT (3-[4,5-dimethylthiazol-2-yl]-2, 5 diphenyltetrazolium bromide) reagent and acridine orange were purchased from Sigma Chemical Co. (St. Louis, MO, USA). All other chemicals were of the highest commercial grade available.

Study population

The exposed group consisted of 32 lead-zinc mine workers (32 male and 0 female). 9 were smokers and 23 non-smokers; 0 were drinkers and 32 were non-drinkers; 3 donors had chronic disease or medicine consumption. The control or non-exposed group consisted of 28 volunteers, office workers, who had never been occupationally exposed to known toxic substances (28 male and 0 female), 6 among them were smokers; 0 were drinkers and 28 were non-drinkers; 2 donors had chronic disease or medicine consumption. In this study, exclusion criteria include smoking habits and acute and chronic disease (such as diabetes)/medicine consumption. Demography and other characteristic of donors from both groups are shown in Table 1. Finally, according to the exclusion criteria, 20 donors in each group were selected to study. The present study was approved by the ethics committee of Shahid Beheshti University of Medical Sciences as ID IR.SBMU.PHARMACY.REC.1397.202. After became aware of our study donors are asked to fill out the approval form.

Table 1

Demography and other characteristic of donors from both groups.

Exposed groupControl group
Number (n)3228
Smoking Habits96
Medicine consumption/ diseases (acute and chronic)32
Alcohol consumption00
Age< 35912
> 35118
GenderMale3228
Female00
Employment< 165
1-557
> 598
Duration of work8 h1315
10 h75
12 h00
16 h00

The blood lymphocytes isolation

Blood samples were taken from 10 lead-zinc mine workers and 10 control workers and samples were kept in heparin syringes. Briefly, ficoll plaque (3 mL) was used for the isolation of lymphocytes and then centrifugation was performed (2500 rpm for 20 min). The plasma layer is slowly detached and the white layer that is suspended in the lysis buffer (150 mM NH4Cl, 10 mM NaHCO3, 1 mM EDTA, pH = 7.4) of the erythrocyte is human lymphocytes, and then incubated for 5 min at 37°C. In the next step, 10 mL PBS was added to the tube. Then, cells were centrifuged at 1500 rpm and the supernatant was eliminated. Finally, cells with RPMI-1640 contain 10% fetal bovine serum (FBS) at 2000 g for 7 min were washed twice and 1×106 cell diluted in 1 mL of RPMI-1640 contain 10% FBS and 1% antibiotic (penestrep) for use in the different test (Assadian et al., 2019).

Cell viability assay

Cell viability was assayed using MTT assay. Blood lymphocytes (1×104 cells/well) were placed in 96-well plates with RPMI 1640, supplemented with 10% FBS and antibiotics (50 U/mL of penicillin and 50 μg/mL streptomycin). In the next step, MTT (5 mg/mL in RPMI 1640) was added to each well and incubated for 4 h after which the plate was centrifuged at 1800 x g for 5 min at 4°C. After careful removal of the medium, DMSO (100 μL) was added to each well, and plates were shaken. Then, absorbance was recorded at 570 nm using microplate reader (Tecan, Rainbow Thermo, Austria) (Zhang et al., 2008).

Reactive oxygen species (ROS) assay

After isolation, human lymphocytes were incubated with 500 μL of dichloro-dihydro-fluorescein Diacetate (DCFH-DA; at the concentration of 10 μM) solution for 20 min in 37°C. The human lymphocytes were washed with PBS. In the final step, fluorescence intensity was measured using a fluorescence spectrophotometer (Shimadzu RF5000U, Japan) at 495 and 530 nm excitation and emission wavelength. The results were expressed as fluorescent intensity (DCF) per 106 cells (Assadian et al., 2018).

The mitochondrial membrane potential (MMP) assay

At first and after removing the supernatant by centrifuging at 1000 × g for 5 min, 500 μL of 5 rhodamine 123 (Rh123; at the concentration of 5 μM) was added to the human lymphocytes suspension and incubated for 10 min. In the final step, fluorescence intensity was measured using a fluorescence spectrophotometer (Shimadzu RF5000U, Japan) at 470 and 540 nm excitation and emission wavelength. The results were expressed as fluorescent intensity (Rh 123) per 106 cells (Zhao et al., 2010).

Glutathione (GSH) and oxidized glutathione (GSSG) assay

After isolation, TCA 10% (0.5 mL) was added to the human lymphocytes and then centrifuged at 11 000 RPM for 2 min. In the next step, supernatant (0.5 mL) was diluted by the addition of EDTA buffer (4.5 mL). In addition, 1000 microliter of diluted supernatant was added to phosphate‐EDTA buffer (2.8 mL) and the ortho-phthalaldehyde (OPA; 100 μL) solution. Finally, after incubation at room temperature for 15 min, fluorescence intensity was assayed at the λ Ex = 350 nm and λ Em = 420 using a fluorescence spectrophotometer (Shimadzu RF5000U, Japan) (Assadian et al., 2019; Hilf and Hissin, 1976).

Lysosomal damage assay

To perform this test, 1000 μL of acridine orange at the concentration of 5 μM was added to the human lymphocytes (100 μL) and incubated for 10 min in 37°C. After washing the lymphocytes, the fluorescence intensity (acridine orange) was assayed at the λ Ex = 470 nm and λ Em = 540 using a fluorescence spectrophotometer (Shimadzu RF5000U, Japan).

Statistical analysis results

Data were analyzed using SPSS software version 20 and GraphPad Prism 5 (Graphpad Software, La Jolla, CA). The Kolmogorov-Smirnov test was used to examine the distribution of data. Due to the normal distribution of data, one-way ANOVA test, followed by the post hoc Tukey test and independent sample T-Test were used to analyze the data. Values less than 0.05 were considered significant levels.

Acknowledgments

The data provided in this article was extracted from the Pharm D. thesis of Dr. Mahshid Soltani. The thesis was conducted under supervision of Prof. Jalal Pourahmad at Department of Toxicology and Pharmacology, Faculty of Pharmacy, Shahid Beheshti University of Medical Sciences, Tehran, Iran.

  1. Conflict of interest: The authors declare that there is no conflict of interest.

References

Akram Z., Riaz S., Kayani M.A., Jahan S., Ahmad M.W., Ullah M.A., et al., Lead induces DNA damage and alteration of ALAD and antioxidant genes mRNA expression in construction site workers. Arch. Environ. Occup. H., 2018, 1-8.10.1080/19338244.2018.1428523Search in Google Scholar PubMed

Assadian E., Dezhampanah H., Seydi E., Pourahmad J., Toxicity of Fe2O3 nanoparticles on human blood lymphocytes. J. Biochem. Mol. Toxicol., 2019, 33(6), e22303.10.1002/jbt.22303Search in Google Scholar PubMed

Assadian E., Zarei M.H., Gilani A.G., Farshin M., Degampanah H., Pourahmad J., Toxicity of copper oxide (CuO) nanoparticles on human blood lymphocytes. Biol. Trace Elem. Res., 2018, 184, 350-357.10.1007/s12011-017-1170-4Search in Google Scholar PubMed

Basit S., Karim N., Munshi A.B., Occupational lead toxicity in battery workers. Pak. J. Med. Sci., 2015, 31(4), 775-780.10.12669/pjms.314.7066Search in Google Scholar PubMed PubMed Central

Belyaeva E.A., Sokolova T.V., Emelyanova L.V., Zakharova I.O., Mitochondrial electron transport chain in heavy metal-induced neurotoxicity: effects of cadmium, mercury, and copper. Sci. World J., 2012, 2012,136063.10.1100/2012/136063Search in Google Scholar PubMed PubMed Central

Chen L., Yang X., Jiao H., Zhao B., Tea catechins protect against lead-induced ROS formation, mitochondrial dysfunction, and calcium dysregulation in PC12 cells. Chem. Res. Toxicol., 2003, 16(9), 1155-1161.10.1021/tx0340605Search in Google Scholar PubMed

Conterato G.M., Bulcao R.P., Sobieski R., Moro A.M., Charao M.F., de Freitas F.A., et al., Blood thioredoxin reductase activity, oxidative stress and hematological parameters in painters and battery workers: relationship with lead and cadmium levels in blood. J. Appl. Toxicol., 2013, 33(2), 142-50.10.1002/jat.1731Search in Google Scholar PubMed

Dan Dunn J., Alvarez L.A., Zhang X., Soldati T., Reactive oxygen species and mitochondria: A nexus of cellular homeostasis. Redox Biol., 2015, 6, 472-845.10.1016/j.redox.2015.09.005Search in Google Scholar PubMed PubMed Central

Ercal N., Gurer-Orhan H., Aykin-Burns N., Toxic metals and oxidative stress part I: mechanisms involved in metal-induced oxidative damage. Curr. Top. Med. Chem., 2001, 1(6), 529-539.10.2174/1568026013394831Search in Google Scholar PubMed

Fedotcheva T., Shimanovskii N., Kruglov A., Teplova V., Fedotcheva N., Role of mitochondrial thiols of different localization in the generation of reactive oxygen species. Biochem (Mosc). Suppl. Ser. A Membr. Cell Biol., 2012, 6(1), 92-99.10.1134/S1990747811060043Search in Google Scholar

Fracasso M.E., Perbellini L., Solda S., Talamini G., Franceschetti P., Lead induced DNA strand breaks in lymphocytes of exposed workers: role of reactive oxygen species and protein kinase C. Mutat. Res., 2002, 515(1-2), 159-169.10.1016/S1383-5718(02)00012-8Search in Google Scholar

Ghanwat G., Patil A.J., Patil J., Kshirsagar M., Sontakke A., Ayachit R.K., Effect of Vitamin C Supplementation on Blood Lead Level, Oxidative Stress and Antioxidant Status of Battery Manufacturing Workers of Western Maharashtra, India. J. Clin. Diagn. Res., 2016, 10(4), Bc08-11.10.7860/JCDR/2016/15968.7528Search in Google Scholar

Hilf R., Hissin P., A fluorometric method for determination of oxidized and reduced glutathione in tissues. Anal. Biochem., 1976, 74(1), 214-226.10.1016/0003-2697(76)90326-2Search in Google Scholar

Hsieh N.H., Chung S.H., Chen S.C., Chen W.Y., Cheng Y.H., Lin Y.J., et al., BMC Public Health. BMC Public Health, 2017, 17(1), 89.10.1186/s12889-017-4315-7Search in Google Scholar PubMed PubMed Central

Kalahasthi R., Barman T., Assessment of Lead Exposure and Urinary-delta-aminolevulinic Acid Levels in Male Lead Acid Battery Workers in Tamil Nadu, India. J. Health Pollut., 2018, 8(17), 6-13.10.5696/2156-9614-8.17.6Search in Google Scholar PubMed PubMed Central

Kamogashira T., Hayashi K., Fujimoto C., Iwasaki S., Yamasoba T., Functionally and morphologically damaged mitochondria observed in auditory cells under senescence-inducing stress. NPJ Aging Mech. Dis., 2017, 3, 2.10.1038/s41514-017-0002-2Search in Google Scholar PubMed PubMed Central

Kasperczyk S., Dobrakowski M., Kasperczyk A., Machnik G., Birkner E., Effect of N-acetylcysteine administration on the expression and activities of antioxidant enzymes and the malondialdehyde level in the blood of lead-exposed workers. Environ. Toxicol. Pharmacol., 2014a, 37(2), 638-647.10.1016/j.etap.2014.01.024Search in Google Scholar PubMed

Kasperczyk S., Dobrakowski M., Kasperczyk A., Nogaj E., Boron M., Szlacheta Z., et al., alpha-Tocopherol supplementation and the oxidative stress, homocysteine, and antioxidants in lead exposure. Arch. Environ. Occup. Health., 2017, 72(3), 153-158.10.1080/19338244.2016.1182112Search in Google Scholar PubMed

Kasperczyk S., Dobrakowski M., Kasperczyk A., Romuk E., Rykaczewska-Czerwińska M., Pawlas N., et al., Effect of N-acetylcysteine administration on homocysteine level, oxidative damage to proteins, and levels of iron (Fe) and Fe-related proteins in lead-exposed workers. Toxicol. Ind. Health, 2016, 32(9), 1607-1618.10.1177/0748233715571152Search in Google Scholar PubMed

Kasperczyk S., Dobrakowski M., Kasperczyk J., Ostalowska A., Zalejska-Fiolka J., Birkner E., Beta-carotene reduces oxidative stress, improves glutathione metabolism and modifies antioxidant defense systems in lead-exposed workers. Toxicol. Appl. Pharmacol., 2014b, 280(1), 36-41.10.1016/j.taap.2014.07.006Search in Google Scholar PubMed

Li X., Fang P., Mai J., Choi E.T., Wang H., Yang X.F., Targeting mitochondrial reactive oxygen species as novel therapy for inflammatory diseases and cancers. J. Hematol. Oncol., 2013, 6,19.10.1186/1756-8722-6-19Search in Google Scholar

Liu B., Qin H., Zhang B., Shi T., Cui Y., Enhanced oxidative stress by lead toxicity retards cell survival in primary thyroid cells. Int. J. Clin. Exp. Med., 2017, 10(3), 4590-4597.Search in Google Scholar

Plum L.M., Rink L., Haase H., The essential toxin: impact of zinc on human health. Int. J. Environ. Res. Public. Health, 2010, 7(4), 1342-1365.10.3390/ijerph7041342Search in Google Scholar

Qu C.S., Ma Z.W., Yang J., Liu Y., Bi J., Huang L., Human exposure pathways of heavy metals in a lead-zinc mining area, Jiangsu Province, China. PLoS One, 2012, 7(11), e46793.10.1201/b16566-8Search in Google Scholar

Qu W., Du G.L., Feng B., Shao H., Effects of oxidative stress on blood pressure and electrocardiogram findings in workers with occupational exposure to lead. J. Int. Med. Res., 2019, 47(6), 2461-2470.10.1177/0300060519842446Search in Google Scholar

Ranjbar A., Ghasemi H., Rostampour F., The role of oxidative stress in metals toxicity; mitochondrial dysfunction as a key player. Galen Med. J., 2014, 3(1), 2-13.10.31661/gmj.v3i1.100Search in Google Scholar

Ricco M., Cattani S., Signorelli C., Zinc exposure for female workers in a galvanizing plant in Northern Italy. Int. J. Occup. Med. Env., 2018, 31(1), 113-124.10.13075/ijomeh.1896.00878Search in Google Scholar

Sakamuru S., Attene-Ramos M.S., Xia M., Mitochondrial Membrane Potential Assay. Methods Mol. Biol., 2016, 1473,17-22.10.1007/978-1-4939-6346-1_2Search in Google Scholar

Shraideh Z., Badran D., Hunaiti A., Battah A., Association between occupational lead exposure and plasma levels of selected oxidative stress related parameters in Jordanian automobile workers. Int. J. Occup. Med. Env., 2018, 31(4), 517-525.10.13075/ijomeh.1896.01243Search in Google Scholar

Steffensen I.L., Mesna O.J., Andruchow E., Namork E., Hylland K., Andersen R.A., Cytotoxicity and accumulation of Hg, Ag, Cd, Cu, Pb and Zn in human peripheral T and B lymphocytes and monocytes in vitro. Gen. Pharmacol., 1994, 25(8), 1621-1633.10.1016/0306-3623(94)90364-6Search in Google Scholar

Zarei M.H., Hosseini Shirazi S.F., Aghvami M., Salimi A., Pourahmad J., Analysis of cytotoxic effects of nickel on human blood lymphocytes. Toxicol. Mech. Method., 2018a, 28(2), 79-86.10.1080/15376516.2017.1364314Search in Google Scholar PubMed

Zarei M.H., Pourahmad J., Aghvami M., Soodi M., Nassireslami E., Lead acetate toxicity on human lymphocytes at non-cytotoxic concentrations detected in human blood. Main Group Met. Chem., 2017, 40(5-6), 105-112.10.1515/mgmc-2017-0023Search in Google Scholar

Zhang Q., Zhao X.-H., Wang Z.-J., Flavones and flavonols exert cytotoxic effects on a human oesophageal adenocarcinoma cell line (OE33) by causing G2/M arrest and inducing apoptosis. Food Chem. Toxicol., 2008, 46(6), 2042-2053.10.1016/j.fct.2008.01.049Search in Google Scholar PubMed

Zhao Y., Ye L., Liu H., Xia Q., Zhang Y., Yang X., et al., Vanadium compounds induced mitochondria permeability transition pore (PTP) opening related to oxidative stress. J. Inorg. Biochem., 2010, 104(4), 371-378.10.1016/j.jinorgbio.2009.11.007Search in Google Scholar PubMed

Zorov D.B., Juhaszova M., Sollott S.J., Mitochondrial reactive oxygen species (ROS) and ROS-induced ROS release. Physiol. Rev., 2014, 94(3), 909-950.10.1152/physrev.00026.2013Search in Google Scholar PubMed PubMed Central

Received: 2020-07-01
Accepted: 2020-07-24
Published Online: 2020-10-07

© 2020 Seydi et al., published by De Gruyter

This work is licensed under the Creative Commons Attribution 4.0 International License.

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