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. 2023 Dec 9;13(1):tfad119. doi: 10.1093/toxres/tfad119

Selenium and zinc supplementation mitigates metals-(loids) mixture- mediated cardiopulmonary toxicity via attenuation of antioxidant, anti-inflammatory and antiapoptotic mechanisms in female Sprague Dawley rats

Mfoniso Antia 1, Anthonet N Ezejiofor 2, Chinna N Orish 3, Ana Cirovic 4, Aleksandar Cirovic 5, Orish E Orisakwe 6,
PMCID: PMC10762678  PMID: 38179003

Abstract

This study evaluated the cardiopulmonary protective effects of essential elements (Zn and Se) against heavy metals mixture (HMM) exposure. Twenty five female Sprague Dawley albino rats, divided in to five groups: controls were orally treated only with distilled water; next, group 2 was exposed to HMM with the following concentrations: 20 mg/kg of Pb body weight, 0.40 mg/kg of Hg, 0.56 mg/kg of Mn, and 35 mg/kg of Al. Groups 3, 4 and 5 were exposed to HMM and co-treated with zinc chloride (ZnCl2; 0.80 mg/kg), sodium selenite (Na2SeO3;1.50 mg/kg) and both zinc chloride and sodium selenite, respectively. The experiment lasted for 60 days. Afterwards animals were sacrificed, and we conduced biochemical and histopathological examination of the heart and lungs. HMM only exposed animals had an increased levels of malondialdehyde (MDA) and nitric oxide (NO), increased IL-6 and TNF-α, attenuated SOD, GPx, CAT and GSH and caspase 3 in the heart and lungs. HMM affected NF-kB and Nrf2 in the heart muscle with histomorphological alterations. Zn and Se attenuated adverse effects of HMM exposure. Essential element supplementation ameliorated heavy metal cardiopulmonary intoxication in rats.

Keywords: heavy metals, metalloids, essential trace elements, oxido-inflammatory, heart, lungs

Graphical Abstract

Graphical Abstract.

Graphical Abstract

Schematic approach to experimental design (used heavy metals mixture and duration of exposure), examined organs and main outcomes of this study.

Introduction

Proper and synchronous heart and lungs actions are necessary for an adequate function of all other organs. The pulmonary and cardiovascular systems are closely knitted together with the primary role of adequate delivering oxygen to the tissues. This interwoven relationship implies imply that a defect of either system inimically affects the other, hampering cardiopulmonary function, systemic oxygen supply, and activity of other major organs1 i.e. decreased function of either of those (the heart and lungs) leads to suffering of other organs.

Lead Pb, Mercury Hg, Manganese Mn and Aluminum Al, ranked 2nd, 3rd, 140th and 183rd on the Agency for Toxic Substances and Disease Registry ATSDR Substance Priority List.2 These metals, especially Pb and Hg, are of profound public health concern because of their inadvertent bioaccumulation with high toxicity in different organs and tissues.3,4 The toxicity of these metals is premised on the disruption of cellular homeostatic condition via molecular mimicry, oxidative damage, and adduct formation with DNA or protein.5 Pb has toxicological effects on many organs including the lungs and heart.6 Pb creates reactive radicals which damage cell structures including DNA and cell membrane, interferes with the enzymes that maintain the integrity of the cell membrane, interferes with DNA transcription and increases endoplasmic reticulum stress.7 Exposure to Hg may damage lungs, change mucous membrane and may cause vomiting, nausea, skin rashes, increased blood pressure, renal dysfunction and severe neurological abnormalities.8 Hg induces genotoxic effects through oxidative stress, disturbs calcium homeostasis, and disrupts neurotransmitter systems and cytoskeletal interactions.9 Moreover, we have to keep in mind that for examples heart is incomparably more sensitive to heavy metals toxicity than some other organs such as the liver or kidneys10 and therefore less concentrations of heavy metals could induce more devastating effects.

According to WHO Pb is one of the ten chemicals of utmost public health concern given it ubiquity, toxicity even at diminutive levels and now touted as having no known safe blood lead concentration for human WHO 2017. The diverse anthropogenic activities (mining, smelting, manufacturing, and recycling activities, continued use of leaded paint, leaded gasoline, and leaded aviation fuel) add to the environmental burden of metals especially Pb, Al, Hg, Mn are rife in the Niger Delta, Nigeria.11,12 Drinking water supply, diets, soil and air are the major sources of metals The pathway of exposure includes ingestion,13 inhalation,14 and dermal absorption, and pathway varies depending on their sources.15 Metal exposure especially Pb can cause anemia, hypertension, immunotoxicity etc. (WHO, 2017). Pb-toxicity impedes normal cardiovascular processes.16,17 Manganese Mn is an essential transition element which plays an important role as cofactor of many metabolic and antioxidant enzymes like Mn superoxide dismutase (Mn-SOD), the principal mitochondrial antioxidant enzyme.18–20 Mn exposure is associated with toxicity in lung and heart.21 Mn can cause an inflammatory response in the lungs, with clinical symptoms including cough, acute bronchitis, and decreased lung functions.22 Aluminum can induce pulmonary injuries through increasing oxidative stress, reducing total antioxidant capacity, triggering inflammatory response, and impairing lung mechanics.23–25 Many studies have shown that occupational exposure to aluminum is associated with the increased risks of pneumoconiosis,26 asthma,27and non-malignant respiratory disease.28–30

The long period of crude oil exploration and other anthropogenic activities in Niger Delt, Nigeria have led to heavy metal especially Pb, Hg, Al and Mn contamination of foods, water and air.11,12 All in all, metals elicit toxicity via disruption of cellular metabolism, alterations in cell adhesion, intra- and inter-cellular signaling, protein folding, maturation, protein kinase C, apoptosis, ionic transportation, enzyme regulation, and release of neurotransmitters even at low concentration mainly due to its ability to replace other divalent cations like Ca2+, Mg2+, Fe2+ and monovalent cations like Na+. This leads to various disorders and can also result in excessive damage due to oxidative stress induced by free radical generation.31 There is ample evidence from both experimental and epidemiological studies that the combined effects of multi-heavy metals might be quite different from that induced by the individual metals.32–34

Anti-oxidant and anti-inflammatory agents are known to be beneficial in tissue injury.35,36 Zinc Zn a cofactor of several metabolic enzyme and selenium Se, which occupies the active centers of some proteins in the form of selenocysteine, are essential microelements considered vital in the maintenance of cellular homeostasis. The protective role of Zn and Se in cardiopulmonary injury, is largely unknown, therefore, this study has evaluated the anti-oxidant and anti-inflammatory effects of Zn, Se and Zn plus Se combination in heavy metal mixture mediated cardiopulmonary injury. This study hypothesized that Zn, Se and Zn plus Se combination supplementation might be beneficial in Pb, Al, Hg, Mn mixture-induced injury in the cardiopulmonary system of rat via attenuating oxidative stress, activating antioxidant enzymes, and reducing apoptosis and inflammatory response.

Materials and methods

Chemicals

All used chemicals, Pb(C2H3O2)2, AlCl3, HgCl2 and MnCl2 were bought from Sigma Chemical Co. (St. Louis, MO, USA). Inflammatory cytokines (tumor necrosis factor alpha; TNF—α, interleukin 6; IL—6), transcription factors and apoptotic marker [(nuclear factor kappa B; NF-kB), (nuclear factor erythroid 2-related factor 2; Nrf2) and (Caspase 3)] ELISA Kit (for rats) were obtained from Elabscience science Biotechnology Company, (Beijing, China). All other reagents used were of analytical grade and they were obtained from the British Drug Houses (Poole, Dorset, UK).

Animals and treatments

Female Sprague Dawley albino rats (n = 25; 6–8 weeks old) were provided by the Department of Pharmacology, Animal House, University of Port Harcourt, Rivers State, Nigeria. All the rats were kept in polypropylene cages at the room temperature of 25 ± 2 °C with 12-h light/dark cycles throughout the experiment. Before the beginning of the study, the animals had been acclimatized for fourteen days. The experimental animals (n = 25) were divided into five groups and each group consisted of five animals. Controls (group 1) were orally treated with distilled water for 60 days; group 2 was exposed to heavy metal mixture (HMM) with the following concentrations:20 mg/kg of Pb body weight,37 0.40 mg/kg of Hg,37 0.56 mg/kg of Mn, and 35 mg/kg of Al.38 Groups 3, 4 and 5 were exposed to HMM and co-treated with zinc chloride (ZnCl2; 0.80 mg/kg),39 sodium selenite (Na2SeO3;1.50 mg/kg)40 and both zinc chloride and sodium selenite, respectively. The heavy-metal compounds were separately dissolved as a stock solution before use to avoid precipitation and they were diluted to the working concentration using ultrapure water. Environmentally relevant doses of metal mixtures according to some recently conducted studies from various matrices of the Niger Delta, Nigeria, were used in this study.12 The exposure doses of metals mixture in this study were considered low37; moreover, they are in the lower range when compared to the doses of metals used in similar in vivo studies.41,42

The rats were weighed weekly, and their feed and fluid intake were recorded. After 60 days of exposure, the animals were euthanized by intraperitoneal administration of pentobarbital (50 mg/kg). The heart and lungs of each rat were dissected and rinsed in cold saline water, weighed, and used for both biochemical parameters and heavy metal analyses.

The ethical approval was obtained from the University of Port Harcourt institutional Centre for Research Management and Development Animal Care and Use Research Ethics Committee (UPH/PUTOR/REC/12). The experiment was conducted in accordance with the “Guide for the Care of Laboratory Animals” approved by the National Academy of Science (NAS). The animals received standard feed and deionized water ad libitum.

Sample collection and heart and lung tissues preparation

The rats were euthanized using pentobarbital (intraperitoneal administration; 50 mg/kg dose), and the heart and lungs samples were quickly dissected and stored at −80 °C for metal and biochemical analyses.

The heart and lungs were separately homogenized in 9 vol of cold phosphate buffer (0.1 M: pH 7.4) using homogenizer. The tissue homogenates were centrifuged at 3,000 rpm for 20 min at 4 °C to separate the nuclear debris. The heart and lungs lysates were used for assays of MDA, NO, GSH, GPx, GST, SOD and for ELISA assays [(Tumour necrosis factor alpha (TNF-α), Interleukin-6 (IL-6), Nuclear factor E2-related factor 2 (NRF2), Factor Kappa B (NF-kB), Casp-3).

ELISA analysis

The assay that determined the cytokine levels, transcription factors, and biomarkers of apoptosis in the heart and lungs were described in another study.43 Pro-inflammatory cytokines (IL-6 and TNF-α), transcription factors (NF-kB and Nrf2), (Hmox1), and a biomarker of apoptosis (Caspase 3) were analysed using the instructions provided by the manufacturer (Elabcience Biotechnology Company (Beijing, China)). An ELISA kit (Elabscience Biotechnology Company, (Beijing, China) was used to measure supernatant concentrations in pro-inflammatory cytokines (IL-6 and TNF-α), NFKB and Nrf2, (Hmox1), and the biomarker of apoptosis (Caspase 3) according to the manufacturer’s instructions.

Antioxidant and oxidative stress markers

Glutathione related antioxidants (GPx), reduced glutathione (GSH), glutathione S-transferase (GST), superoxide dismutase (SOD), catalase, lipid peroxidation, nitric oxide

In order to measure activity of various antioxidants we used following methodology Paglia and Valentine44 for the GPx measurement (412 nm), Jollow et al.’s method45 for the GSH measurements (412 nm), Habig et al.’s method45 for the GST activity (310 nm), using the following equation: GST activity (μmol min−1 mg−1 protein) = At/(1.9 × time × mg protein). SOD activity was assayed using 20 μL of the heart and lungs (separately) supernatant sample (test) or buffer (reference) and 10 μL pyrogallol (20 mM in 10 mM HCl) to which, 1 mL buffer solution was added.46 The absorbance of test (At) or reference (Ar) was measured at 420 nm against the air after 30 s and 90 s. The percentage inhibition of pyrogallol autoxidation was calculated according to the following equation: the percentage inhibition = [100 – (At min−1 mL−1 sample)/(Ar min−1 mL−1 reference)] × 100. Catalase activity was estimated by monitoring the rate of H2O2 breakdown at 240 nm according to Aebi’s method.47 Briefly, 990 μL of catalase buffer (0.036% H2O2 prepared in 50 mM phosphate buffer, pH 7.0) was added to 10 μL of the heart and lungs lysates separately in a cuvette. Catalase activity was assayed immediately at 240 nm for 3 min and expressed as μmol/min/mg protein.

Lipid peroxidation was analyzed as thiobarbituric acid reactive substances (TBARS) by the adaptation of Esterbauer and Cheeseman method.48 In a nutshell, 500 μL of heart and lungs supernatant, separately, was added to one ml TCA (20%) and mixed thoroughly. The mixture was centrifuged at 3,000 rpm for 10 min. One ml of the supernatant was added to 0.5 mL of 0.7% TBA and allowed to boil for 10 min. After cooling, the absorbance was read at 532 nm against blank.

Nitric oxide (NO): this assay adapted the Griess reaction technique.49,50 One microliter 100 μL of heart and lungs (separately) supernatant was added to 100 μL acidic Griess reagent (1% sulfanilamide and 0.1% naphthlethylenediamine dihydrochloride in 2.5% phosphoric acid). The absorbance was read at 540 nm against blank.

Determination of heavy metals

The harvested heart and lungs were dried for 48 h, then weighed and placed in 10 mL conical flasks with polypropylene lids containing 3 mL of HNO3 at room temperature until the solution became clear. Then, 1 mL of 30% H2O2 was added to the samples. At the end of effervescence, the samples were heated at 80 °C to remove the HNO3, cooled to room temperature and the final volume was made up to 10 mL with 2% HNO3. The samples were brought to a constant volume.

In order to ensure reproducible and reliable data the instrument was recalibrated after every10 runs. Chemical reagents and solvents were of picograde quality. The calibration curves for each element were obtained with high purity multi-cathode lamp (1,000 mg/kg) (Cambridge CB5 8BZ, UK) and multi element calibration curves were verified with a multi-element certified material (1,000 mg/kg) (Cambridge). Different concentrations (0.5, 1.0, 2.0, 5.0, and 10.0 mg/L) of trace elements were used for calibration of standard graphs.51The elements were measured at the stipulated wavelengths Pb: 216.9 nm, Al: 309.3 nm, Hg: 253.7 nm, and Mn: 530 nm. The limits of detection (LoD) were 0.001 for Al, Hg and Mn and 0.01 mg/kg for Pb, while the limits of quantification (LoQ) were 0.0033 for Al, Hg and Mn and 0.033 mg/kg for Pb. Pb, Al, Hg and Mn (Certified Reference Materials) standard solutions (1,000 mg/L) were obtained from the National Institute of Standards and Technology (NIST, USA) and diluted appropriately to obtain working standards.

Histopathological examination

On day 60, the animals were sacrificed and submitted to transcardiac perfusion with heparinized saline 0.9% solution followed by 4% paraformaldehyde in 0.2 M phosphate buffer. Surgical manipulation was performed only after the removal of the corneal and paw reflexes. The heart and lungs were excised and postfixed for 6 h in Bouin’s solution. The specimens were then washed with 50% alcohol, dehydrated in alcohol solutions in progressive concentrations clarified in xylol and embedded in paraffin.

The heart and lungs were harvested at the end of the experiment, and immediately fixed with 4% paraformaldehyde. These were embedded in paraffin and sectioned into 5 μm slices for hematoxylin and eosin staining. The histological examination was blindly evaluated by two experienced histopathologists.

Statistical analysis

The data were expressed as mean ± standard deviation (SD). The Kolmogorov-Smirnov test revealed normal distribution of all the measured parameters. Microsoft Xlstat 2014 was used for performing the one-way analysis of variance (ANOVA) with the Tukey’s post-hoc test to check if the concentration of the biomarkers was significantly different between the groups. Pandas was used in obtaining descriptive statistical parameters (biomarkers and metal mean concentrations) for the various organs of the rats. Seaborn and Matplotlib were used in plotting all the graphs. The data analysis involved performing descriptive statistics of the metal and biomarker concentration before One-Way ANOVA was used to determine if there was a significant difference in the concentrations of heavy metals and biomarkers among the groups. All significant differences were at P < 0.05.

Results

Effect of essential trace elements Zn, Se, Zn + Se combination of bioaccumulation of heavy metal in heart and lungs of Sprague Dawley rats following exposure to metal mixture

Zn, Se, Zn + Se combination caused significant (P < 0.05) decrease in the concentration (25.78, 12.70 and 27.05% respectively) of Pb when compared with HMM only treated group. The essential trace elements Zn, Se, Zn + Se combination significantly (P < 0.05) decreased the concentration (20.78, 8.92 and 22.12% respectively) of Hg in comparison to the HMM only treated group. The essential trace elements Zn, Se, Zn + Se combination significantly decreased the concentration (18.42, 7.18 and 19.79% respectively) of Mn in comparison to the HMM only treated groups (P < 0.05). The essential trace elements Zn, Se, Zn + Se combination caused significant (P < 0.05) reduction in the percent concentration (25.00, 14.25 and 26.37% respectively) of Al when compared with the HMM only treated groups.

The essential trace elements Zn, Se, Zn + Se combination significantly (P < 0.05) decreased the concentration (28.62, 14.14 and 29.85% respectively) of Pb when compared with HMM only treated. Zn, Se, Zn + Se combination co-treatment significantly (P < 0.05) decreased the concentration (22.44, 8.05 and 23.44% respectively) of Hg in comparison to the HMM only treated groups. The essential trace elements Zn, Se, Zn + Se combination significantly reduced the concentration (25.78, 12.70 and 27.05% respectively) of Mn in comparison to the HMM only treated group (P < 0.05). The essential trace elements Zn, Se, Zn + Se combination significantly (P < 0.05) decreased the concentration (26.25, 12.60 and 27.60% respectively) of Al in comparison to the HMM only treated.

Table 1 shows the effect of essential elements on the body weight, absolute and relative weight of lungs and heart of female albino rats exposed to HMM. There were no significant differences in the absolute and relative weights of the lungs and heart between the HMM exposed groups from the control groups (P > 0.05); moreover, absolute and relative weights of the lungs and heart did not vary between HMM only exposed animals and HMM animals co-treated with Zn, Se and Zn combined with Se (P > 0.05). There was gain in body weight in all groups both the percent gain was higher in the essential element treated groups with zinc showing the highest percent gain.

Table 1.

Effect of essential elements on the body weight, absolute and relative weight of lungs and heart of female albino rats exposed to HMM.

Treatment Absolute weight Lungs (g) Relative weight Lungs (%) Absolute weight Heart (g) Relative weight Heart (%) %Body weight gain Feed intake Fluid intake
Deionized H2O (only) 1.30 ± 0.00a 0.65 ± 0.00a 0.70 ± 0.14a 0.35 ± 0.09 58.9 154.10 ± 23.42a 242.98 ± 35.36a
Metal mixture (only) 1.30 ± 0.14a 0.72 ± 0.03a 0.60 ± 0.14a 0.33 ± 0.13 54.5 148.27 ± 16.42a 210.07 ± 33.46a
Metal mixture + Zinc 0.98 ± 0.01a 0.60 ± 0.08a 0.52 ± 0.06a 0.32 ± 0.05 172.6 147.94 ± 22.13a 195.62 ± 43.20a
Metal mixture + Selenium 0.99 ± 0.16a 0.64 ± 0.02a 0.52 ± 0.01a 0.33 ± 0.01 105.5 127.63 ± 35.47a 209.74 ± 51.27a
Metal mixture + Zn + Se 1.01 ± 0.02a 0.65 ± 0.03a 0.51 ± 0.01a 0.33 ± 0.14 126.5 127.82 ± 29.85a 203.85 ± 53.26a

Values expressed as Mean ± standard deviation, N = 5. Different superscripts (a, b, c) are significantly different from each other (P < 0.05). HMM: Heavy metal mixture.

The effects of essential elements (Zn and Se) on an antioxidant (SOD, GPx, CAT, GSH) and the oxidative stress markers MDA (μmol/mL) and NO (μM/L) levels in the heart and the lungs of the female albino rats following HMM exposure is shown in Table 2. HMM significantly decreased activity of the SOD, GPx, CAT and GSH in comparison to the control group in the heart and lungs (P < 0.05). Zn, Se and Zn plus Se combination significantly increased the SOD, GPx, CAT and GSH when compared with the HMM exposed rats (P < 0.05) Table 2. The MDA and NO levels of the HMM treated rats were significantly higher than the control group in the heart and lungs (P < 0.05). Zn, Se and Zn plus Se combination significantly decreased concentrations of the MDA and NO when compared with the HMM treated rats in both examined organs (P < 0.05).

Table 2.

Effects essential elements (Zn and Se) on antioxidants (SOD, GPx, CAT, GSH), MDA (μmol/mL) and NO (μM/L) levels in heart and lungs of female albino rats after exposure to heavy metal mixtures.

Treatment SOD GPx CAT GSH MDA NO
Heart Lungs Heart Lungs Heart Lungs Heart Lungs Heart Lungs Heart Lungs
Control 0.36 ± 0.06a 0.60 ± 0.04a 0.06 ± 0.01a 0.07 ± 0.01a 0.84 ± 0.08bc 2.69 ± 0.13a 1.08 ± 0.04b 1.45 ± 0.12a 0.46 ± 0.01b 0.25 ± 0.07bc 3.58 ± 0.42c 4.30 ± 0.03c
HMM only 0.20 ± 0.02b 0.36 ± 0.06b 0.03 ± 0.001c 0.04 ± 0.001a 0.41 ± 0.02d 0.82 ± 0.08a 0.72 ± 0.02c 0.82 ± 0.02c 0.56 ± 0.02a 0.495 ± 0.03a 8.05 ± 0.09a 8.63 ± 0.92a
HMM + Zn 0.45 ± 0.03a 0.52 ± 0.02bc 0.03 ± 0.001c 0.06 ± 0.004a 0.67 ± 0.08cd 1.63 ± 0.72a 0.78 ± 0.05c 1.16 ± 0.19a 0.43 ± 0.01b 0.28 ± 0.000b 6.21 ± 0.06ab 7.225 ± 0.11ab
HMM + Se 0.56 ± 0.06c 0.66 ± 0.05ab 0.05 ± 0.001ab 0.07 ± 0.01a 1.02 ± 0.14b 1.89 ± 0.79a 1.20 ± 0.01a 1.47 ± 0.21a 0.23 ± 0.03c 0.17 ± 0.02bc 5.53 ± 0.25bc 5.90 ± 0.28bc
HMM + Zn + Se 0.65 ± 0.02a 0.74 ± 0.01a 0.049 ± 0.001b 0.07 ± 0.01a 1.41 ± 0.098a 2.52 ± 0.38a 1.09 ± 0.01ab 1.52 ± 0.33a 0.16 ± 0.01c 0.11 ± 0.01c 4.78 ± 0.18bc 6.03 ± 0.18bc

Values are presented as Mean ± standard deviation values with different superscripts are significantly different from each other at P < 0.05, while values with the same superscripts are not significantly different.

Table 3 shows the effect of essential elements on the inflammatory cytokines (IL-6, (pg/mL)), (TNF-α, (pg/mL)), transcription factors (NRF2, (pg/mL)), (NFkB, (pg/mL)), and Caspase 3 (μmol/mL) in the heart and the lungs of Sprague Dawley female albino rats after heavy metal mixtures (Pb, Hg, Mn and Al) exposure.

Table 3.

Effect of essential elements on the pro-inflammatory cytokines (IL-6, (pg/mL)), (TNF-α, (pg/mL)), transcription factors (Nrf2, (pg/mL)), (NFkb, (pg/mL)), and caspase 3 (μmol/mL) in heart and lungs of female albino rats after heavy metal mixtures (Pb, hg, Mn and Al) exposure.

Treatment IL-6 TNF-α Nrf2 Nf-kβ Casp 3
Heart Lungs Heart Lungs Heart Lungs Heart Lungs Heart Lungs
Control 115.25 ± 2.80c 349.00 ± 2.68b 122.50 ± 2.33b 39.950 ± 2.24b 71.65 ± 8.98d 512.50 ± 8.27a 1.02 ± 0.02b 2.58 ± 0.02a 0.54 ± 0.01b 0.67 ± 0.04b
HMM only 364.00 ± 5.66a 613.00 ± 17.40a 321.50 ± 9.97a 109.00 ± 1.41a 719.50 ± 13.44a 1030.000 ± 7.07ab 2.38 ± 0.17a 2.60 ± 0.04a 2.60 ± 0.11a 5.06 ± 0.43a
HMM + Zn 132.50 ± 7.78c 251.50 ± 7.14c 184.50 ± 10.61ab 34.10 ± 1.83b 221.50 ± 2.12b 1046.500 ± 13.44b 1.56 ± 0.16b 2.10 ± 0.68a 0.65 ± 0.13b 1.98 ± 0.50b
HMM + Se 215.50 ± 1.91b 401.00 ± 1.97d 113.50 ± 2.12b 22.00 ± 7.78ab 70.50 ± 6.36d 802.50 ± 3.12c 1.28 ± 0.13b 2.54 ± 0.05a 0.80 ± 0.04b 1.92 ± 0.60b
HMM + Zn + Se 211.00 ± 5.66b 342.00 ± 4.80a 141.50 ± 1.20ab 31.60 ± 2.29b 127.50 ± 7.78c 513.55 ± 7.12a 1.190 ± 0.31b 2.56 ± 0.01a 0.82 ± 0.09b 1.17 ± 0.06b

Values are presented as Mean ± standard deviation values with different superscripts are significantly different from each other at P < 0.05, while values with the same superscripts are not significantly different.

The inflammatory cytokines (IL-6, (pg/mL)), (TNF-α, (pg/mL)) in the HMM exposed rats were significantly higher than the control groups (P < 0.05). Zn, Se and Zn plus Se combination caused significant decrease in the levels of IL-6 and TNF-α in comparison to the HMM exposed rats (P < 0.05). The levels of NRF2 and NFkB in the heart and lungs of HMM treated rats were significantly higher than the control group (P < 0.05). The essential elements Zn, Se and Zn + Se caused significant decrease in the NRF2 of the heart while Se and Zn + Se caused significant decrease in the NRF2 of the lungs in comparison to the HMM exposed rats. There were significant difference between NFkB (heart) levels between the HMM group 2.38 ± 0.17 pg/mL and control group 1.02 ± 0.02 pg/mL. The NFkB (heart) after Zn, Se and Zn + Se co-treatment with HMM were significantly (P < 0.05) lower than HMM only groups. There were no significant differences in the NFkb levels in the lungs among the control, HMM and the Zn, Se and Zn + Se co-treated groups. The caspase 3 activity was significantly (P < 0.05) increased from 0.54 ± 0.01 and 0.67 ± 0.04 μmol/mL to 2.60 ± 0.11 and 5.06 ± 0.43 μmol/mL in heart and lungs respectively. Co-treatment with Zn, Se and Zn + Se caused significant (P < 0.05) decrease in the caspase 3 μmol/mL) in heart and lungs of Sprague Dawley female albino rats.

Histopathological examination (heart)

In controls we found interstitial oedema (IO) and perivascular oedema (PVO) Fig. 1A–E. Histopathological examination of the HMM rats revealed multifocal interstitial oedema focal myofiber waviness, with associated (arrows). As for the HMM plus Zn animals, we found myocardial inflammation with multifocal areas of inflammatory cells infiltration (arrows). The photomicrograph of the HMM plus Se rats revealed normal myocardium showing the syncytium of myocardial fibers with central nuclei. Finally, HMM and Zn + Se photomicrographs revealed a myocardium with a focal area of interstitial oedema (IO), showing a large vein (LV).

Fig. 1.

Fig. 1

Histopathological evaluation of the heart and lungs in all five experimental rat groups: Group 1 (A): Deionized water—photomicrograph (X400, H&E) of the myocardium, demonstrating interstitial edema (IO) and perivascular edema (PVO). Group 2 (B): HMM only—photomicrograph (X400, H&E) of the myocardium, displaying multifocal interstitial edema, focal myofiber waviness, and associated features (arrows). Group 3 (C): HMM and Zn—photomicrograph (X400, H&E), showcasing myocardial inflammation with multifocal areas of inflammatory cell infiltration (arrows). Group 4 (D): HMM and se—photomicrograph (X100, H&E) of a longitudinal section of normal myocardium, illustrating the syncytium of myocardial fibers with central nuclei. Group 5 (E): HMM and Zn + Se—photomicrograph (X400, H&E) of myocardium, featuring a focal area of interstitial edema (IO) and a large vein (LV). Group 1 (A1): Deionized water—photomicrograph (X400, H&E) of the lungs, revealing diffuse alveolar septal necrosis with septal hypertrophy. Group 2 (B1): HMM only—photomicrograph (X400, H&E) of the lungs, indicating a reversible degenerative change with diffuse cytoplasmic vacuolation (arrows) of the alveolar septal wall and multiple necrotic foci (NF). Group 3 (C1): HMM and Zn—photomicrograph (X400, H&E) of the lungs, illustrating lung regeneration and the reformation of normal lung architecture with necrotic debris (arrows) in the epithelial wall of the respiratory bronchiole. Group 4 (D1): HMM and Se—photomicrograph (X400, H&E) of the lungs, showing lung degeneration, including distortion of lung architecture associated with multiple foci of necrosis (arrows) and sloughing of epithelial cells into the alveolar lumen (ES). Group 5 (E1): HMM and Zn + Se—photomicrograph (X400, H&E) of the lungs, presenting lung regeneration with a normal lung architecture and a few necrotic foci (arrows).

Histopathological examination (lungs)

In controls we found lungs showing diffuse alveolar septal necrosis with septal hypertrophy Fig. 1A1–E1. Histopathological examination of the HMM rats showing a reversible degenerative change with diffuse cytoplasmic vacuolation (arrows) of the alveolar septal wall and multi-necrotic foci (NF). Group 3: As for the HMM plus Zn animals, lungs showing lung regeneration, reformation of normal lung architecture with necrotic debris (arrows) in epithelial wall of the respiratory bronchiole. The photomicrograph of the HMM plus Se rats revealed lung degeneration. There is distortion of lung architecture associated with multi-foci necrosis (arrows) and sloughing of epithelial cells into alveolar lumen (ES). Finally, HMM and Zn + Se photomicrographs revealed lung regeneration. There is normal lung architecture associated with few necrosis foci (arrows).

Discussion

In the current study, toxicological evaluation of quaternary metal mixture (Pb, Hg, Al and Mn) and in combination essential metal (loid) Zn and Se on different parameters of the cardiopulmonary system in Sprague female rats have been evaluated. Usually, metals are not biodegradable and not digested in humans and animals. In an exposed organism, metals are poorly metabolized resulting in increased body burden with chronic exposure.52 Although the hepatic system is largely the target site for accumulation, these metals can also accumulate in the cardiac and pulmonary systems.53,54

Our results demonstrated that heart and lung tissues have tendencies to accumulate Pb, Hg, Al and Mn in high concentrations after exposure to these metals. This accumulation of non-essential metals in the heart may induce cardiovascular toxicity. The non-essential metals reach the vascular walls by metal-laden monocytes and accumulate in the walls of the aorta where it also accumulates in vascular smooth muscles and induce apoptosis of endothelial cells. The suggested cardiotoxicity mechanism may include direct myocardial structure damage, disruption of calcium channels, inhibition of vasodilators like NO, and/or direct vasoconstriction.53,55 Accumulation of metal in the artery can induce aortic weakness via enhancing vascular remodeling which leads to increased arterial stiffening, causing adversarial effects on the metabolism of smooth muscle cells.56 On exposure to various metal(loid), chances of hypertension and lung disease are exaggerated.57 Exposure of Hg and other metals predispose the heart to increased oxidative stress or decreased antioxidant enzymes e.g. GPx which culminate in increased lipoxidation.58,59

In this study the essential trace elements Zn, Se, Zn + Se combination significantly (P < 0.05) decreased the concentration of Pb, Hg, Al and Mn in heart and lungs when compared with untreated HMM only group. An antagonistic relationship between Se and Pb in the accumulation of both metal(loid) upon co-exposure has been reported.60 Se in co-exposure with Pb significantly reduced the Pb concentration in comparison to only Pb exposure.60 Therefore, the net Se-mediated detoxification potential has been reported against Pb toxicity. Furthermore, Se decreased the levels of other noxious metals. It has also been reported that with Se-insufficiency or deficiency exacerbates Pb-induced health risk even at miniscule amounts of Pb exposure.61

Zn has two-edged effect of on Pb toxicity according to Piao et al.62. According to this study Pb level in whole blood was not affected by Zn alone or Zn + Pb, but showed that Zn was significantly higher in the Zn alone treated group.62 In another study, Zn was observed to boost the efficacy of Pb chelation through lowering the blood, hepatic and renal Pb contents, and reversed the inhibited activity on blood ALAD.63 Prasanthi et al., have also reported the antioxidant property of Zn against Pb-toxicity in small mammals study.64 All in all, Se and Zn supplementation reduce Pb-toxicity, attenuates the oxidative stress and restores the essential metal homeostasis by decreasing the Pb accumulation in different organs.31 Many non-essential metals are known to form selenium-metal complexes via bonding to selenium and thiol (-SH)-containing molecules. These complexes hamper the efficiency of different antioxidant enzymes. For instance the diminution in the activity of catalase is due to the deficiency of selenium-binding protein.65 Cardiotoxicity mediated by metals is multifaceted involving diminishing of antioxidant enzyme activity, amplification of reactive oxygen species ROS which have been implicated in myocardial infarction,66 destruction of phospholipases, increased oxidation of low-density lipoproteins,67 and the inactivation of paraoxonase implicated in atherosclerosis and acute myocardial infarction. Furthermore, metal activation of phospholipase A2 and the concomitant hydrolysis of glycerol phospholipids, formation of lysophosphatidic and arachidonic acid catabolic products such as thromboxanes and prostaglandins have also been associated with coronary artery disease.68

Following oral exposure, aluminum is distributed throughout an organism, and its accumulation in many tissues. The exact mechanism of aluminum toxicity is poorly understood. Al amplifies oxidative stress and inflammatory responses which culminate into cellular injury.69–71 The release of various cytokines into the circulation after metal exposure may increase both cardiac and vascular inflammation to mediate cardiovascular toxicity.

As a divalent metal, zinc (Zn) is one of the essential metals in which the mimicry function of all the divalent metal and metalloids has demonstrated. Zn mediates several physiological functions72 in addition to its protective biological role against free radical damage via ramping of enough metallothioneins (MT) levels, sustenance of being an essential component of Cu,Zn- superoxide dismutase (Cu,Zn-SOD), or as protective agent of thiols and other chemical groups.73 Zn is also a crucial cofactor of several vital enzymes.74 Another essential trace element selenium (Se) ameliorates toxicity exerted by many metals. It is now known that Se acts by the formation of selenoproteins in accentuating cellular antioxidant defense, and immune responses in various biological processes.75,76 Se is an essential oligo element in humans with significant antioxidant, free radical scavenging, and protective roles from oxidative damage in the tissues and organs. It is also an enhancer of the body’s immune system. Whereas HMM only significantly (P < 0.05) decreased the SOD, GPx, CAT and GSH in comparison to the control group in the heart and lungs, Zn, Se and Zn plus Se combination significantly (P < 0.05) increased the SOD, GPx, CAT and GSH when compared with the HMM exposed rats.

In one study, Li et al.77 reported an upregulation of TNF-α, iNOS and NF-κB following Pb exposure which was significantly reduced by Se and Pb co-administration. Another study found that, Se in combination with Pb exposure alleviated the Pb-induced downregulation of selenoproteins level Gpx1, Gpx2, Gpx4.78 In another study, it was also reported that Se inhibited Pb mediated apoptosis79–81 The mechanisms of aluminum mediated pulmonary toxicity is not fully understood, although Al is known to directly trigger lung mechanics impairment,82 and also cause oxidative stress. Epidemiological data suggest a positive association between Al and decreased total antioxidant capacity in Al exposed workers,23 and a positive relationship of Al exposure with increased urinary MDA among schoolchildren.83 Furthermore, inflammation might be implicated in Al pulmonary toxicity since in vitro, Al salt crystals have been observed to activate NLRP3 inflammasome and up-regulate the maturation and release of interleukin-1b in human peripheral blood mononuclear cells84; and in vivo, inhalation of aluminum hydroxide has been reported to promote the recruitment of inflammatory cells to the lung and increases the levels of cytokine interferon-g and chemokine CCL2 in lung tissues.25

Jin and coworkers reported increased oxidative stress (MDA), and pro-apoptotic genes (caspase 3) following Pb exposure which were significantly reversed by co-treatment with Se and Pb.79 Similarly, Pb-mediated oxidative stress by decreasing total antioxidant activity, SOD, CAT, GSH, GPx and increase of MDA,78 were significantly reversed by the co-treatment of Se with Pb in.85 The MDA and NO of the HMM treated rats were significantly (P < 0.05) higher than the control group. Zn, Se and Zn plus Se combination significantly (P < 0.05) decreased MDA and NO when compared with the HMM treated rats in the present study.

As a component of glutathione peroxidase (GSH-Px), Se regulates pro-inflammatory cytokines and antioxidant defense.86,87 Whereas systemic inflammatory response or oxidative stress conditions predispose individuals to the risk of Se deficiency,88 Se supplementation has been observed to be beneficial.89,90 Also, experimental studies have demonstrated increased oxidative stress in blood and impairment in vascular function in Se deficient rats.91 Conversely, Se administration could ameliorate chemical induced tissue injury via activation antioxidant enzyme GSH-Px, reducing inflammatory cytokines TNF-α, interleukin-1 beta (IL-1β),43,78,92 or decreasing oxidative product MDA in tissues.93–96 As hypothesized, the pro-inflammatory cytokines IL-6, TNF-α, in the HMM exposed rats were significantly (P < 0.05) higher than the control groups but supplementation with Zn, Se and Zn plus Se combination caused significant decrease (P < 0.05) when compared with the HMM exposed rats. In the same vein, the levels of Nrf2 and NFkβ in the heart and lungs of HMM treated rats were significantly (P < 0.05) higher than the control group and co-treatment with the essential elements Zn, Se and Zn + Se significantly decreased in the Nrf2 of the heart while Se and Zn + Se caused significant decrease in the Nrf2 of the lungs in comparison to the HMM exposed rats. Also, in this study the significant increases in the caspase 3 activities in the heart and lungs following HMM exposure was attenuated by co-administration with Zn, Se and Zn + Se combination.

Taken together, it could be deduced from the present study that micronutrient Zn, Se and Zn plus Se combination supplementations might be beneficial in cocktail quaternary metal (Pb, Al, Hg, Mn) mixture-induced cardiopulmonary toxicity by augmentation of antioxidant status, abrogation of inflammatory processes and antiapoptotic mechanisms.

Author contributions

Orish Ebere Orisakwe and Chinna N Orish have designed the study, interpreted the data and drafted the manuscript. Mfoniso Antia and Anthonet N. Ezejiofor collected the data of the work. Ana Cirovic and Aleksander Cirovic proofread the manuscript. All the authors finally approved the version to be published.

Funding

This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.

 

Conflict of interest statement: All authors involved in the production of this research declared that they have no conflict of interest.

Data availability

Authors declare that all the data are original and they are available upon request.

Contributor Information

Mfoniso Antia, African Centre of Excellence for Public Health and Toxicological Research (ACE-PUTOR), University of Port Harcourt, PMB, East West Road, Choba, Port Harcourt, Rivers State, Choba 5323, Nigeria.

Anthonet N Ezejiofor, African Centre of Excellence for Public Health and Toxicological Research (ACE-PUTOR), University of Port Harcourt, PMB, East West Road, Choba, Port Harcourt, Rivers State, Choba 5323, Nigeria.

Chinna N Orish, Department of Anatomy, Faculty of Basic Medical Sciences, College of Health Sciences, University of Port Harcourt, PMB, East West Road, Choba, Port Harcourt, Rivers State, Choba 5323, Nigeria.

Ana Cirovic, Faculty of Medicine, The Institute of Anatomy, University of Belgrade, East West Road, Choba, Port Harcourt, Rivers State Belgrade, Serbia.

Aleksandar Cirovic, Faculty of Medicine, The Institute of Anatomy, University of Belgrade, East West Road, Choba, Port Harcourt, Rivers State Belgrade, Serbia.

Orish E Orisakwe, African Centre of Excellence for Public Health and Toxicological Research (ACE-PUTOR), University of Port Harcourt, PMB, East West Road, Choba, Port Harcourt, Rivers State, Choba 5323, Nigeria.

References

  • 1. Bronicki RA, Anas NG. Cardiopulmonary interaction. Pediatr Crit Care Med. 2009:10(3):313–322. [DOI] [PubMed] [Google Scholar]
  • 2. Atsdr . Priority list of hazardous substances; Atlanta USA: Agency for toxic substances and disease registry - 2015 - ATSDR CDC. 2015. pp. 1–9
  • 3. Clemens S, Ma JF. Toxic heavy metal and metalloid accumulation in crop plants and foods. Annu Rev Plant Biol. 2016:67(1):489–512. [DOI] [PubMed] [Google Scholar]
  • 4. Bjørklund G, Mutter J, Aaseth J. Metal chelators and neurotoxicity: lead, mercury, and arsenic. Arch Toxicol. 2017:91(12):3787–3797. [DOI] [PubMed] [Google Scholar]
  • 5. Keil DE, Berger-Ritchie J, McMillin GA. Testing for toxic elements: a focus on arsenic, cadmium, lead, and mercury. Lab Med. 2011:42(12):735–742. [Google Scholar]
  • 6. Adikwu E, Deo O, Geoffrey O-BP, Enimeya DA. Lead organ and tissue toxicity: roles of mitigating agents (part 2). Br J Pharmacol Toxicol. 2014:5(1):1–15. [Google Scholar]
  • 7. Wani A-LAA, Ara A, Usmani JA. Lead toxicity: a review. Interdiscip Toxicol. 2015:8(2):55–64. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 8. Jan AT, Azam M, Siddiqui K, Ali A, Choi I, Haq Q. Heavy metals and human health: mechanistic insight into toxicity and counter defense system of antioxidants. Int J Mol Sci. 2015:16(12):29592–29630. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9. Pieper I, Wehe CA, Bornhorst J, Ebert F, Leffers L, Holtkamp M, Höseler P, Weber T, Mangerich A, Bürkle A, et al. Mechanisms of Hg species induced toxicity in cultured human astrocytes: genotoxicity and DNA-damage response. Metallomics. 2014:6(3):662–671. [DOI] [PubMed] [Google Scholar]
  • 10. Limaye DA, Shaikh ZA. Cytotoxicity of cadmium and characteristics of its transport in cardiomyocytes. Toxicol Appl Pharmacol. 1999:154(1):59–66. [DOI] [PubMed] [Google Scholar]
  • 11. Orisakwe OE, Blum JL, Sujak S, Zelikoff JT. Metal pollution in Nigeria: a biomonitoring update. J Health Pollut. 2014:4(6):40–52. [Google Scholar]
  • 12. Okoye EA, Bocca B, Ruggieri F, Ezejiofor AN, Nwaogazie IL, Frazzoli C, Orisakwe OE. Arsenic and toxic metals in meat and fish consumed in Niger delta, Nigeria: employing the margin of exposure approach in human health risk assessment. Food Chem Toxicol. 2022:159:112767. [DOI] [PubMed] [Google Scholar]
  • 13. Naidoo V, Wolter K, Botha CJ. Lead ingestion as a potential contributing factor to the decline in vulture populations in southern Africa. Environ Res. 2017:152:150–156. [DOI] [PubMed] [Google Scholar]
  • 14. Eqani SAMAS, Khalid R, Bostan N, Saqib Z, Mohmand J, Rehan M, Ali N, Katsoyiannis IA, Shen H. Human lead (Pb) exposure via dust from different land use settings of Pakistan: a case study from two urban mountainous cities. Chemosphere. 2016:155:259–265. [DOI] [PubMed] [Google Scholar]
  • 15. Filon FL, Boeniger M, Maina G, Adami G, Spinelli P, Damian A. Skin absorption of inorganic lead (PbO) and the effect of skin cleansers. J Occup Environ Med. 2006:48(7):692–699. [DOI] [PubMed] [Google Scholar]
  • 16. Liu G, Yang G, Guan G, Zhang Y, Ren W, Yin J, Aguilar YM, Luo W, Fang J, Yu X, et al. Effect of dietary selenium yeast supplementation on porcine circovirus type 2 (PCV2) infections in mice. PLoS One. 2015:10(2):e0115833. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17. Müller YM, Rivero LB, Carvalho MC, Kobus K, Farina M, Nazari EM. Behavioral impairments related to lead-induced developmental neurotoxicity in chicks. Arch Toxicol. 2008:82(7):445–451. [DOI] [PubMed] [Google Scholar]
  • 18. Stephenson AP, Schneider JA, Nelson BC, Atha DH, Jain A, Soliman KFA, Aschner M, Mazzio E, Renee Reams R. Manganese-induced oxidative DNA damage in neuronal SH-SY5Y cells: attenuation of thymine base lesions by glutathione and N-acetylcysteine. Toxicol Lett. 2013:218(3):299–307. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19. Takeda A. Manganese action in brain function. Brain Res Rev. 2003:41(1):79–87. [DOI] [PubMed] [Google Scholar]
  • 20. Horning KJ, Caito SW, Tipps KG, Bowman AB, Aschner M. Manganese is essential for neuronal health. Annu Rev Nutr. 2015:35(1):71–108. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21. Brurok H, Berg K, Sneen L, Grant D, Karlsson JOG, Jynge P. Cardiac metal contents after infusions of manganese: an experimental evaluation in the isolated rat heart. Investig Radiol. 1999:34(7):470–476. [DOI] [PubMed] [Google Scholar]
  • 22. Han J, Lee J-S, Choi D, Lee Y, Hong S, Choi J, Han S, Ko Y, Kim JA, Kim YM, et al. Manganese (II) induces chemical hypoxia by inhibiting HIF-prolyl hydroxylase: implication in manganese-induced pulmonary inflammation. Toxicol Appl Pharmacol. 2009:235(3):261–267. [DOI] [PubMed] [Google Scholar]
  • 23. Samir A, Rashed L. Effects of occupational exposure to aluminium on some oxidative stress and DNA damage parameters. Hum Exp Toxicol. 2018:37(9):901–908. [DOI] [PubMed] [Google Scholar]
  • 24. Zhou M, Yang S, Wang X, Zhang X, Cen X, Mu G, Wang D, Ma J, Wang B, Chen W. The association between urinary aluminum and lung function among an urban adult population: a repeated-measure longitudinal study. Chemosphere. 2021:270:129443. [DOI] [PubMed] [Google Scholar]
  • 25. Kozima ET, Souza ABF, Castro TF, Matos NA, Philips NE, Costa GP, Talvani A, Cangussú SD, Bezerra FS. Aluminum hydroxide nebulization-induced redox imbalance and acute lung inflammation in mice. Exp Lung Res. 2020:46(3–4):64–74. [DOI] [PubMed] [Google Scholar]
  • 26. Peters S, Reid A, Fritschi L, de Klerk N, Musk AB. Long-term effects of aluminium dust inhalation. Occup Environ Med. 2013:70(12):864–868. [DOI] [PubMed] [Google Scholar]
  • 27. Vandenplas O, Delwiche J, Vanbilsen M, Joly J, Roosels D. Occupational asthma caused by aluminium welding. Eur Respir J. 1998:11(5):1182–1184. [DOI] [PubMed] [Google Scholar]
  • 28. Friesen MC, Fritschi L, del Monaco A, Benke G, Dennekamp M, de Klerk N, Hoving JL, MacFarlane E, Sim MR. Relationships between alumina and bauxite dust exposure and cancer, respiratory and circulatory disease. Occup Environ Med. 2009:66(9):615–618. [DOI] [PubMed] [Google Scholar]
  • 29. Pun VC, Yu IT-S, Qiu H, Ho KF, Sun Z, Louie PKK, Wong TW, Tian L. Short-term associations of cause-specific emergency hospitalizations and particulate matter chemical components in Hong Kong. Am J Epidemiol. 2014:179(9):1086–1095. [DOI] [PubMed] [Google Scholar]
  • 30. Baccarelli AA, Zheng Y, Zhang X, Chang D, Liu L, Wolf KR, Zhang Z, McCracken JP, Díaz A, Bertazzi PA, et al. Air pollution exposure and lung function in highly exposed subjects in Beijing, China: a repeated-measure study. Part Fibre Toxicol. 2014:11(1):51. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 31. Rahman MM, Hossain KFB, Banik S, Sikder MT, Akter M, Bondad SEC, Rahaman MS, Hosokawa T, Saito T, Kurasaki M. Selenium and zinc protections against metal-(loids)-induced toxicity and disease manifestations: a review. Ecotoxicol Environ Saf. 2019:168:146–163. [DOI] [PubMed] [Google Scholar]
  • 32. Kortenkamp A. Ten years of mixing cocktails: a review of combination effects of endocrine-disrupting chemicals. Environ Health Perspect. 2007:115 Suppl(Suppl 1):98–105. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 33. Pandya CD, Pillai PP, Gupta SS. Lead and cadmium co-exposure mediated toxic insults on hepatic steroid metabolism and antioxidant system of adult male rats. Biol Trace Elem Res. 2010:134(3):307–317. [DOI] [PubMed] [Google Scholar]
  • 34. Mauderly JL, Samet JM. Is there evidence for synergy among air pollutants in causing health effects? Environ Health Perspect. 2009:117(1):1–6. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 35. du X, Jiang S, Bo L, Liu J, Zeng X, Xie Y, He Q, Ye X, Song W, Zhao J. Combined effects of vitamin E and omega-3 fatty acids on protecting ambient PM(2.5)-induced cardiovascular injury in rats. Chemosphere. 2017:173:14–21. [DOI] [PubMed] [Google Scholar]
  • 36. Villarreal-Calderon R, Reed W, Palacios-Moreno J, Keefe S, Herritt L, Brooks D, Torres-Jardón R, Calderón-Garcidueñas L. Urban air pollution produces up-regulation of myocardial inflammatory genes and dark chocolate provides cardioprotection. Exp Toxicol Pathol. 2012:64(4):297–306. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 37. Institóris L, Kovács D, Kecskeméti-Kovács I, Lukács A, Szabó A, Lengyel Z, Papp A, Nagymajtényi L, Dési I. Immunotoxicological investigation of subacute combined exposure with low doses of Pb, Hg and Cd in rats. Acta Biol Hung. 2006:57(4):433–439. [DOI] [PubMed] [Google Scholar]
  • 38. Su H, Li Z, Fiati Kenston SS, Shi H, Wang Y, Song X, Gu Y, Barber T, Aldinger J, Zou B, et al. Joint toxicity of different heavy metal mixtures after a short-term oral repeated-administration in rats. Int J Environ Res Public Health. 2017:14(10):1164. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 39. Anyanwu BO, Orish CN, Ezejiofor AN, Nwaogazie IL, Orisakwe OE. Neuroprotective effect of Costus afer on low dose heavy metal mixture (lead, cadmium and mercury) induced neurotoxicity via antioxidant, anti-inflammatory activities. Toxicol Rep. 2020:7:1032–1038. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 40. Messarah M, Klibet F, Boumendjel A, Abdennour C, Bouzerna N, Boulakoud MS, el Feki A. Hepatoprotective role and antioxidant capacity of selenium on arsenic-induced liver injury in rats. Exp Toxicol Pathol. 2012:64(3):167–174. [DOI] [PubMed] [Google Scholar]
  • 41. Andjelkovic M, Buha Djordjevic A, Antonijevic E, Antonijevic B, Stanic M, Kotur-Stevuljevic J, Spasojevic-Kalimanovska V, Jovanovic M, Boricic N, Wallace D, et al. Toxic effect of acute cadmium and lead exposure in rat blood, liver, and kidney. Int J Environ Res Public Health. 2019:16(2):274. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 42. Zhou F, Yin G, Gao Y, Ouyang L, Liu S, Jia Q, Yu H, Zha Z, Wang K, Xie J, et al. Insights into cognitive deficits caused by low-dose toxic heavy metal mixtures and their remediation through a postnatal enriched environment in rats. J Hazard Mater. 2020:388:122081. [DOI] [PubMed] [Google Scholar]
  • 43. Eddie-Amadi BF, Ezejiofor AN, Orish CN, Orisakwe OE. Zinc and selenium mitigated heavy metals mixture (Pb, Al, Hg and Mn) mediated hepatic-nephropathy via modulation of oxido-inflammatory status and NF-kB signaling in female albino rats. Toxicology. 2022:481:153350. [DOI] [PubMed] [Google Scholar]
  • 44. Paglia DE, Valentine WN. Studies on the quantitative and qualitative characterization of erythrocyte glutathione peroxidase. J Lab Clin Med. 1967:70(1):158–169. [PubMed] [Google Scholar]
  • 45. Jollow D, Mitchell J, Zampaglione N, Gillette J. Bromobenzene-induced liver necrosis. Protective role of glutathione and evidence for 3, 4-bromobenzene oxide as the hepatotoxic metabolite. Pharmacology. 1974:11(3):151–169. [DOI] [PubMed] [Google Scholar]
  • 46. Marklund S, Marklund G. Involvement of the superoxide anion radical in the autoxidation of pyrogallol and a convenient assay for superoxide dismutase. Eur J Biochem. 1974:47(3):469–474. [DOI] [PubMed] [Google Scholar]
  • 47. Bergmeyer H, Gawehn K, Grassl M. Enzymes as biochemical agents: catalase. Methods of Enzym Anal. 1974:1:438–439. [Google Scholar]
  • 48. Esterbauer H, Cheeseman KH. [42] Determination of aldehydic lipid peroxidation products: malonaldehyde and 4-hydroxynonenal. Methods Enzymol. 1990:186:407–421. [DOI] [PubMed] [Google Scholar]
  • 49. Oktem G, Uysal A, Oral O, Sezer ED, Olukman M, Erol A, Akgur SA, Bilir A. Resveratrol attenuates doxorubicin-induced cellular damage by modulating nitric oxide and apoptosis. Exp Toxicol Pathol. 2012:64(5):471–479. [DOI] [PubMed] [Google Scholar]
  • 50. Sosroseno W, Sugiatno E, Samsudin AR, Ibrahim MF. The role of nitric oxide on the proliferation of a human osteoblast cell line stimulated with hydroxyapatite. J Oral Implantol. 2008:34(4):196–202. [DOI] [PubMed] [Google Scholar]
  • 51. Okoye EA, Ezejiofor AN, Nwaogazie IL, Frazzoli C, Orisakwe OE. Heavy metals and arsenic in soil and vegetation of Niger Delta, Nigeria: ecological risk assessment. Case Stud Chem Environ Eng. 2022:6:100222. [Google Scholar]
  • 52. Adams WJ, Blust R, Borgmann U, Brix KV, DeForest DK, Green AS, Meyer JS, McGeer JC, Paquin PR, Rainbow PS, et al. Utility of tissue residues for predicting effects of metals on aquatic organisms. Integr Environ Assess Manag. 2011:7(1):75–98. [DOI] [PubMed] [Google Scholar]
  • 53. Ali S, Hussain S, Khan R, Mumtaz S, Ashraf N, Andleeb S, Shakir HA, Tahir HM, Khan MKA, Ulhaq M. Renal toxicity of heavy metals (cadmium and mercury) and their amelioration with ascorbic acid in rabbits. Environ Sci Pollut Res. 2019:26(4):3909–3920. [DOI] [PubMed] [Google Scholar]
  • 54. Josthna P, Geetharathan T, Sujatha P, Deepika G. Accumulation of lead and cadmium in the organs and tissues of albino rat. Int J Pharm Life Sci. 2012:3:2186–2189. 10.1007/s11356-018-3819-8. [DOI] [Google Scholar]
  • 55. Horiguchi H, Oguma E, Kayama F. Cadmium induces anemia through interdependent progress of hemolysis, body iron accumulation, and insufficient erythropoietin production in rats. Toxicol Sci. 2011:122(1):198–210. [DOI] [PubMed] [Google Scholar]
  • 56. Sangartit W, Kukongviriyapan U, Donpunha W, Pakdeechote P, Kukongviriyapan V, Surawattanawan P, Greenwald SE. Tetrahydrocurcumin protects against cadmium-induced hypertension, raised arterial stiffness and vascular remodeling in mice. PLoS One. 2014:9(12):e114908. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 57. Massanyi PL, Lukac N, Slivkova J, Kovacik J, Makarevich AV, Chrenek P, Toman R, Forgacs Z, Somosy Z, Stawarz R, et al. Mercury-induced alterations in rat kidneys and testes in vivo. J Environ Sci Health A Tox Hazard Subst Environ Eng. 2007:42(7):865–870. [DOI] [PubMed] [Google Scholar]
  • 58. Ali S, Awan Z, Mumtaz S, Shakir HA, Ahmad F, Ulhaq M, Tahir HM, Awan MS, Sharif S, Irfan M, et al. Cardiac toxicity of heavy metals (cadmium and mercury) and pharmacological intervention by vitamin C in rabbits. Environ Sci Pollut Res. 2020:27(23):29266–29279. [DOI] [PubMed] [Google Scholar]
  • 59. Mackness M, Mackness B. Paraoxonase 1 and atherosclerosis: is the gene or the protein more important? Free Radic Biol Med. 2004:37(9):1317–1323. [DOI] [PubMed] [Google Scholar]
  • 60. Jin X, Liu CP, Teng XH, Fu J. Effects of dietary selenium against lead toxicity are related to the ion profile in chicken muscle. Biol Trace Elem Res. 2016:172(2):496–503. [DOI] [PubMed] [Google Scholar]
  • 61. Maza D, Ojo J. Development of human PBBK models for mixtures: binary mixtures of mercury/selenium, and lead/selenium. IFE J Sci. 2016:18:1019–1040. [Google Scholar]
  • 62. Piao F, Cheng F, Chen H, Li G, Sun X, Liu S, Yamauchi T, Yokoyama K. Effects of zinc coadministration on lead toxicities in rats. Ind Health. 2007:45(4):546–551. [DOI] [PubMed] [Google Scholar]
  • 63. Flora S, Tandon S. Beneficial effects of zinc supplementation during chelation treatment of lead intoxication in rats. Toxicology. 1990:64(2):129–139. [DOI] [PubMed] [Google Scholar]
  • 64. Prasanthi RJ, Devi CB, Basha DC, Reddy NS, Reddy GR. Calcium and zinc supplementation protects lead (Pb)-induced perturbations in antioxidant enzymes and lipid peroxidation in developing mouse brain. Int J Dev Neurosci. 2010:28(2):161–167. [DOI] [PubMed] [Google Scholar]
  • 65. Farina M, Aschner M, Rocha JB. Oxidative stress in MeHg-induced neurotoxicity. Toxicol Appl Pharmacol. 2011:256(3):405–417. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 66. Clarkson TW, Magos L. The toxicology of mercury and its chemical compounds. Crit Rev Toxicol. 2006:36(8):609–662. [DOI] [PubMed] [Google Scholar]
  • 67. Mazerik JN, Hagele T, Sherwani S, Ciapala V, Butler S, Kuppusamy ML, Hunter M, Kuppusamy P, Marsh CB, Parinandi NL. Phospholipase A2 activation regulates cytotoxicity of methylmercury in vascular endothelial cells. Int J Toxicol. 2007:26(6):553–569. [DOI] [PubMed] [Google Scholar]
  • 68. Houston MC. The role of mercury in cardiovascular disease. J Cardiovasc Dis Diagn. 2014:2:1–8. [Google Scholar]
  • 69. Igbokwe IO, Igwenagu E, Igbokwe NA. Aluminium toxicosis: a review of toxic actions and effects. Interdiscip Toxicol. 2019:12(2):45–70. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 70. Wei X, Wei H, Yang D, Li D, Yang X, He M, Lin E, Wu B. Effect of aluminum exposure on glucose metabolism and its mechanism in rats. Biol Trace Elem Res. 2018:186(2):450–456. [DOI] [PubMed] [Google Scholar]
  • 71. Willhite CC, Karyakina NA, Yokel RA, Yenugadhati N, Wisniewski TM, Arnold IMF, Momoli F, Krewski D. Systematic review of potential health risks posed by pharmaceutical, occupational and consumer exposures to metallic and nanoscale aluminum, aluminum oxides, aluminum hydroxide and its soluble salts. Crit Rev Toxicol. 2014:44(sup4):1–80. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 72. Gilmour PS, Schladweiler MC, Nyska A, McGee JK, Thomas R, Jaskot RH, Schmid J, Kodavanti UP. Systemic imbalance of essential metals and cardiac gene expression in rats following acute pulmonary zinc exposure. J Toxicol Environ Health A. 2006:69(22):2011–2032. [DOI] [PubMed] [Google Scholar]
  • 73. Formigari A, Irato P, Santon A. Zinc, antioxidant systems and metallothionein in metal mediated-apoptosis: biochemical and cytochemical aspects. Comp Biochem Physiol C Toxicol Pharmacol. 2007:146(4):443–459. [DOI] [PubMed] [Google Scholar]
  • 74. Prasad AS. Discovery of human zinc deficiency: 50 years later. J Trace Elem Med Biol. 2012:26(2–3):66–69. [DOI] [PubMed] [Google Scholar]
  • 75. Ognjanović BI, Marković SD, Pavlović SZ, Žikić RV, Štajn A, Saičić ZS. Effect of chronic cadmium exposure on antioxidant defense system in some tissues of rats: protective effect of selenium. Physiol Res. 2008:57:403–411. [DOI] [PubMed] [Google Scholar]
  • 76. Tinggi U. Selenium: its role as antioxidant in human health. Environ Health Prev Med. 2008:13(2):102–108. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 77. Li X, Xing M, Chen M, Zhao J, Fan R, Zhao X, Cao C, Yang J, Zhang Z, Xu S. Effects of selenium-lead interaction on the gene expression of inflammatory factors and selenoproteins in chicken neutrophils. Ecotoxicol Environ Saf. 2017:139:447–453. [DOI] [PubMed] [Google Scholar]
  • 78. Moniruzzaman M, Lee S, Park Y, Min T, Bai SC. Evaluation of dietary selenium, vitamin C and E as the multi-antioxidants on the methylmercury intoxicated mice based on mercury bioaccumulation, antioxidant enzyme activity, lipid peroxidation and mitochondrial oxidative stress. Chemosphere. 2021:273:129673. [DOI] [PubMed] [Google Scholar]
  • 79. Jin X, Xu Z, Zhao X, Chen M, Xu S. The antagonistic effect of selenium on lead-induced apoptosis via mitochondrial dynamics pathway in the chicken kidney. Chemosphere. 2017:180:259–266. [DOI] [PubMed] [Google Scholar]
  • 80. Hong W, Liu Y, Liang J, Jiang C, Yu M, Sun W, Huang B, Dong N, Kang L, Tang Y. Molecular mechanisms of selenium mitigating lead toxicity in chickens via mitochondrial pathway: Selenoproteins, oxidative stress, HSPs, and apoptosis. Toxics. 2023:11(9):734. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 81. Miao Z, Miao Z, Shi X, Wu H, Yao Y, Xu S. The antagonistic effect of selenium on lead-induced apoptosis and necroptosis via P38/JNK/ERK pathway in chicken kidney. Ecotoxicol Environ Saf. 2022:231:113176. [DOI] [PubMed] [Google Scholar]
  • 82. Mazzoli-Rocha F, dos Santos AN, Fernandes S, Ferreira Normando VM, Malm O, Nascimento Saldiva PH, Wanderley Picanço-Diniz DL, Faffe DS, Zin WA. Pulmonary function and histological impairment in mice after acute exposure to aluminum dust. Inhal Toxicol. 2010:22(10):861–867. [DOI] [PubMed] [Google Scholar]
  • 83. Bae S, Pan X-C, Kim S-Y, Park K, Kim YH, Kim H, Hong YC. Exposures to particulate matter and polycyclic aromatic hydrocarbons and oxidative stress in schoolchildren. Environ Health Perspect. 2010:118(4):579–583. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 84. Hornung V, Bauernfeind F, Halle A, Samstad EO, Kono H, Rock KL, Fitzgerald KA, Latz E. Silica crystals and aluminum salts activate the NALP3 inflammasome through phagosomal destabilization. Nat Immunol. 2008:9(8):847–856. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 85. Jiao X, Yang K, An Y, Teng X, Teng X. Alleviation of lead-induced oxidative stress and immune damage by selenium in chicken bursa of Fabricius. Environ Sci Pollut Res. 2017:24(8):7555–7564. [DOI] [PubMed] [Google Scholar]
  • 86. Rayman MP. Food-chain selenium and human health: emphasis on intake. Br J Nutr. 2008:100(2):254–268. [DOI] [PubMed] [Google Scholar]
  • 87. Roman M, Jitaru P, Barbante C. Selenium biochemistry and its role for human health. Metallomics. 2014:6(1):25–54. [DOI] [PubMed] [Google Scholar]
  • 88. Manzanares Castro W. Selenio en los pacientes críticos con respuesta inflamatoria sistémica. Nutr Hosp. 2007:22:295–306. [PubMed] [Google Scholar]
  • 89. Leite HP, Nogueira PCK, Oliveira Iglesias SB, Oliveira SV, Sarni ROS. Increased plasma selenium is associated with better outcomes in children with systemic inflammation. Nutrition. 2015:31(3):485–490. [DOI] [PubMed] [Google Scholar]
  • 90. Ju W, Li X, Li Z, Wu GR, Fu XF, Yang XM, Zhang XQ, Gao XB. The effect of selenium supplementation on coronary heart disease: a systematic review and meta-analysis of randomized controlled trials. J Trace Elem Med Biol. 2017:44:8–16. [DOI] [PubMed] [Google Scholar]
  • 91. Stupin A, Cosic A, Novak S, Vesel M, Jukic I, Popovic B, Karalic K, Loncaric Z, Drenjancevic I. Reduced dietary selenium impairs vascular function by increasing oxidative stress in Sprague-Dawley rat aortas. Int J Environ Res Public Health. 2017:14(6):591. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 92. Zwolak I. The role of selenium in arsenic and cadmium toxicity: an updated review of scientific literature. Biol Trace Elem Res. 2020:193(1):44–63. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 93. Chaâbane M, Tir M, Hamdi S, Boudawara O, Jamoussi K, Boudawara T, Ghorbel RE, Zeghal N, Soudani N. Improvement of heart redox states contributes to the beneficial effects of selenium against penconazole-induced cardiotoxicity in adult rats. Biol Trace Elem Res. 2016:169(2):261–270. [DOI] [PubMed] [Google Scholar]
  • 94. Li X, Zhang Y, Yuan Y, Sun Y, Qin Y, Deng Z, Li H. Protective effects of selenium, vitamin E, and purple carrot anthocyanins on D-galactose-induced oxidative damage in blood, liver, heart and kidney rats. Biol Trace Elem Res. 2016:173(2):433–442. [DOI] [PubMed] [Google Scholar]
  • 95. Karthik L, Kumar G, Keswani T, Bhattacharyya A, Chandar SS, Bhaskara Rao KV. Protease inhibitors from marine actinobacteria as a potential source for antimalarial compound. PLoS One. 2014:9(3):e90972. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 96. Merkord J, Görl N, Lemke M, Berg A, Weber H, Ramer R, Hennighausen G. Influence of daily oral prophylactic selenium treatment on the dibutyltin dichloride (DBTC)-induced pancreatitis in rats. EXCLI J. 2017:16:89–100. [DOI] [PMC free article] [PubMed] [Google Scholar]

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