Genotoxicity and oxidative stress induced by the orally administered nanosized nickel and cobalt oxides in male albino rats
The Journal of Basic and Applied Zoology volume 80, Article number: 2 (2019)
Nanoparticles (NPs) are extensively used in many areas of our daily life. Thus, human exposure to a mixture of the NPs is likely to occur. However, most of the previous studies have investigated the toxicity of the individual NPs. Therefore, the current study investigated the genotoxicity and oxidative stress induced by an acute oral administration of the nano-sized nickel oxide (NiO) and/or cobalt oxide (Co3O4) in the brain, liver, and kidney of the rats.
After 1 day of an administration with NiO-NPs or Co3O4-NPs, at the dose levels of 0.5 and 1.0 g/kg, remarkable elevations in malondialdehyde (MDA) levels, percentage of DNA damage (%DNA), tail length (TL), and tail moment (TM), accompanied by marked reductions in the levels of zinc (Zn), glutathione (GSH) as well as the activities and expression levels of the superoxide dismutase (SOD) were recorded in all the studied groups, as compared to the controls. The changes in the levels of all the studied parameters were in a time- and dose-dependent manner. Excessive productions of the reactive oxygen species (ROS) associated with the genomic DNA fragmentation were observed in the experimental groups, as compared to the controls. However, in the groups administered with NiO-NPs and Co3O4-NPs together, the alterations in all the studied parameters were improved as compared to those administered NiO-NPs or Co3O4-NPs solely.
The NiO-NPs and Co3O4-NPs antagonized each other leading to an alleviation of the genotoxicity induced by each of them.
Nanoparticles (NPs), the particles with one of their dimensions at least less than 100 nm, are extensively used in every field of our life (Morsy, Abou El-Ala, & Ali, 2016b). Metal oxide nanoparticles (MNPs) including Co3O4-NPs and NiO-NPS possess unique physical properties including higher activity, larger surface area to volume ratio, and higher absorption compared to their bulk materials (Biener et al., 2009). NiO-NPs are involved in many applications including batteries, sensors, and catalyzers (Magaye et al., 2016). Co3O4-NPs are applied in the fields of electronics, battery, and superconductor synthesis as well as used as a drug carrier (Sundar et al., 2017). Moreover, Co3O4-NPs are intensively used in many biomedical applications including imaging, cancer therapy, and gene therapy (Magaye, Zhao, Bowman, & Ding, 2012). However, the wide application of these MNPs led to their release into the environment in various ways resulting in an increased human exposure to these NPs via inhalation, oral ingestion, and dermal contact (Kirkland et al., 2015). Upon exposure, NPs can penetrate cells more rapidly and provide unprecedented toxicological interactions with cell biomolecules (Jeon, Park, Rhee, & Lee, 2010).
NiO showed relatively low toxicity as compared to the other Ni compounds (Zhao et al., 2009). However, several studies have evidenced that NiO-NPs caused cytotoxic and apoptotic effects in various mammalian cell lines (Lu et al., 2008; Ada et al., 2010 and Pietruska et al., 2011). Furthermore, NiO-NP-induced toxicity has been demonstrated in microorganisms such as bacteria (Baek & An, 2011), algae (Gong et al., 2011), and plants (Faisal et al., 2013). Moreover, intratracheal instillation of NiO-NPs induced inflammation in the lungs of rats (Horie et al., 2011 and Morimoto et al., 2011). Likewise, acute oral administration of NiO-NPs-induced chromosomal aberration, micronuclei formation, and DNA damage were observed in rats (Dumala et al., 2017).
In vitro studies showed that Co3O4-NPs induced micronucleus and oxidative DNA damage (Alarifi et al., 2013; Cavallo et al., 2015 and Uboldi et al., 2015). However, limited studies investigated the genotoxicity and carcinogenicity of Co3O4-NPs in vivo. The study by Bucher et al. (1999) revealed that rats administered Co3O4-NPs over 2 years induced benign bronchio-alveolar carcinoma, lung tumor, bronchio-alveolar adenomas, and adenocarcinomas. Moreover, oral administration of Co3O4-NPs resulted in genomic and mitochondrial DNA damage induction in mice (Mohamed & Hussien, 2018).
Both NiO-NPs and Co3O4-NPs are used together in mixed alloys to speed up their electrochemical activation (Schneiderová et al., 2017). Unfortunately, most of the previous studies were targeted to investigate the effects of individual NPs. Little is known about the interaction of NiO-NPs and Co3O4-NPs on the molecular level. Therefore, the current study was undertaken to study the genotoxicity and oxidative stress induced by an acute oral administration of Co3O4-NPs or/and NiO-NPs in male albino rats.
The animals were randomly separated into the seven groups with fifteen rats per each group as displayed in Table 1. The applied doses were chosen depending on a previous study by our work group (Ali, 2018).
At each time interval, five rats were selected from each group and were immediately sacrificed after euthanasia using an overdose of sodium pentobarbital (150 mg/kg). The rats were dissected immediately to take the brain, liver, and kidney. The tissues were kept in deep freeze at − 80 °C, after being weighted till further processing.
The studied NPs were purchased from Sigma Aldrich (Ward Hill, Massachusetts, USA). According to the manufacturing data sheets, the average particle sizes of the nano-sized NiO (black, 99.8% pure) and Co3O4 (dark gray, 99.5% pure) were less than 50 nm. Characterization was executed in a separate work to study the surface charge, X-ray diffraction pattern, and hydrodynamic diameter of these NPs (Ali, 2018).
Stock solutions of the NiO-NPs and Co3O4-NPs were prepared by being suspended in 0.5% carboxymethyl cellulose (CMC). Immediately before the administration, NP suspensions were ultra-sonicated for 15 min using ultrasonic homogenizer (BioLogics, Inc., Manassas, VA, USA). Each dose had the volume of 2 ml of NP suspension per 100 g of body weight.
Healthy male Wistar rats, Rattus norvegicus, were obtained with an average body weight of 120 g from the National Research Center (NRC), Dokki, Giza, Egypt. Rats were acclimatized for 7 days in polyethylene cages at room temperature and subjected to normal 12/12 h light-dark cycle inside the animal house of Zoology Department, Faculty of Science, Cairo University. The rats were supplied with a standard rodent chow as well as a free access to water. The cages were cleaned day after day from feces and debris.
Measurement of lipid peroxide in tissues
To estimate the levels of malondialdehyde (MDA) in the brain, liver, and kidney, small pieces from each tissue were homogenized in cold potassium phosphate buffer (50 mM, pH 7.5), and then was centrifuged for 15 min at speed of 4000 rpm. The levels of MDA were estimated in the resultant supernatant according to the technique described by Ohkawa, Ohishi, and Yagi (1979). The principle of this method depends on the reaction of the liberated MDA after lipid peroxidation of the cell membranes with thiobarbituric acid in acidic medium.
Measurement of non-enzymatic and enzymatic antioxidants
A small piece from each organ was homogenized in a tube containing cold potassium phosphate buffer (50 mM, pH 7.5) with 1 mM EDTA. Then, the tubes were centrifugated for 15 min at a speed of 9000 rpm at 4 °C. The levels of glutathione (GSH) and activity of superoxide dismutase (SOD) were measured in the produced supernatant. The estimation of GSH was based on the reaction between GSH and 5,5′-dithiobis-2-nitrobenzoic acid (Beutler, Duron, & Kelly, 1963) However, the method for determination of SOD was based on the ability of SOD to inhibit nitroblue tetrazolium dye (Nishikimi, Roa, & Yogi, 1972).
Quantification of the copper-zinc SOD expression level
To determine the expression level of Cu/Zn-SOD in the brain, liver, and kidney of all rats, total RNA was firstly extracted from tissues using GeneJET RNA Purification Kit (Thermo Scientific, USA). DNase I (Thermo Scientific, USA) was applied to remove any residual DNA. Complementary DNA (cDNA) transcripts were synthesized from the purified RNA using Revert Aid First Strand cDNA synthesis kit (Thermo Scientific, USA). Then, real time-polymerase chain reaction (RT-PCR) was performed using the Step One Plus 7500 Fast system (Applied Biosystem 7500, Clinilab, Cairo, Egypt) to quantitatively detect SOD gene expression levels. A 12-μL of the RT-PCR reaction mixture was prepared for each sample containing 2× SYBR Green master mix (Thermo Scientific, USA) and forward 5′-GGTGGTCCACGAGAAACAAG-3′ and reverse CAATCACCACAAGCCAAG-3′ primers for Cu/Zn-SOD gene (Jiménez-Ortega, Cano, Cardinali, & Esquifino, 2009). For amplification, RT-PCR reaction was initiated with initial denaturation at 95 °C for 15 min then 35 cycles of denaturation at 95 °C for 15 s, annealing at 60 °C for 30 s, and extension at 72 °C for 1 min was done. The expression levels of the amplified Cu/Zn-SOD gene were standardized using the housekeeping gene GAPDH as a reference gene. GAPDH was amplified using the primer sequences forward 5′-AGGTGGAAGAATGGGAGTTG and reverse TCAAGAAGGTGGTGAAGCAG (Zhang et al., 2012). Results were interpreted and expression of Cu/Zn-SOD was determined using the comparative Ct (DDCt) and expressed as fold change in the expression level as compared to the untreated control level.
Measurement of zinc levels in tissues
The levels of Zn were measured in the brain, liver, and kidney of the experimental rats according to the method described by Demirbaş, (1999). In brief, tissues were washed with cold phosphate-buffered saline and approximately 0.5–1.5 g of tissues were digested using an acid mixture (HNO3:HClO4 = 4:1, v:v). Then, the volume of digest was completed to 25 ml with demineralized water and Zn concentrations was measured using inductively coupled plasma mass spectrometry (ICP-MS, USA) against blanks and standard solutions.
Estimation of DNA damage using alkaline comet assay
The extent of DNA damage was measured in the brain, liver, and kidney of all the studied groups using alkaline comet assay (Tice et al., 2000). Small pieces of the desired tissue were gently homogenized into cold mincing solutions then mixed with 75 μl of 0.5% low melting agarose. Each 10 μl of cell suspension is containing about 10,000 cells. The cells were spread with agarose on a slide pre-dipped in normal 1% melting agarose and allowed to dry. Then, slides were incubated in cold lysis buffer (2.5 M NaCl, 100 mM EDTA, and 10 mM Tris, pH 10, with freshly added 10% DMSO and 1% Triton X-100) at 4 °C in darkness for 24 h. After lysis, slides were incubated for 20 min in a fresh alkaline buffer (300 mM NaOH and 1 mM EDTA, pH > 13), electrophoresed for 30 min at 25 V and 300 mA. DNA was neutralized by dipping slides in 0.4 M Trizma base (pH 7.5) and fixed in 100% cold ethanol. The slides were dried and stored at room temperature until they were scored. Before the imaging, slides were stained with ethidium bromide and 50 comet cells per animal were analyzed using a TriTek CometScore™ Freeware v1.5 scoring software. %DNA in the tail, TL, and TM were used as indicators for DNA damage.
Laddered DNA fragmentation assay
Laddered DNA fragmentation technique was executed to assess the apoptotic DNA fragmentation in the studied tissues according to the protocol described by Sriram, Kanth, Kalishwaralal, and Gurunathan (2010). A small piece of each tissue was homogenized and lysed in Tris EDTA buffer containing 0.5% sodium dodecyl sulfate and RNase A. Then, samples were incubated at 37 °C for 1 h and proteinase K was added. Samples were incubated again overnight at 50 °C. Genomic DNA was extracted by phenol extraction method and precipitated by ammonium acetate and isopropanol. Finally, 3 μg/15 μL of the extracted DNA with 5 μL of loading dye were electrophoresed in 1% agarose gel at 70 V then visualized using a UV transilluminator and photographed.
Estimation of intracellular ROS generation
The production of ROS was estimated in the brain, liver, and kidney using the method described by Wang & Joseph (1999) and Siddiqui et al. (2010). The technique depends on using 2,7-dichlorofluorescin diacetate (DCFH-DA) that enters the cell passively and reacts with ROS to form the highly fluorescent compound dichlorofluorescein (DCF). The DCFH-DA (20 mM) was added to the cell suspension and samples were incubated in dark for 30 min then visualized and imaged the cells using epi-fluorescent at × 20 magnification.
Data were analyzed using Statistical Package of the Social Sciences; SPSS version 22 (copyrighted by IBM SPSS software, USA). Duncan and least significant difference (LSD) tests were utilized to estimate the similarities among all the experimental groups and significant differences between the experimental intervals. Regression analysis and Pearson’s correlation coefficient were applied to study the relationships between the studied variables. Data is presented as a mean ± standard error of mean (SEM).
Effect of nanoparticles on lipid peroxidation and endogenous antioxidants
In Table 2, the levels of MDA and GSH of all the studied organs of all experimental rats throughout the experiments were displayed. In all organs of groups II to VII, the MDA levels were significantly higher than in group I at the first day. At most intervals, the MDA levels in organs of groups II and V were markedly lower than in groups III and IV, respectively. On the fourteenth day, the levels of MDA in most organs of all groups were markedly declined than at the first day and became similar to the controls, except in groups V and VI.
On contrary, at the first and seventh days, the GSH content of all tissues of all groups II to VII was significantly depleted, as compared to group I. GSH levels of organs of groups III and IV were remarkably lower than in groups II and V, at most experimental periods. By the fourteenth day, most organs of groups II to VII exhibited marked elevations in the GSH content, as compared to the first day. GSH content was returned to the control values except in groups III and IV. In all the rats administered NiO-NPs or/and Co3O4-NPs, the MDA levels were negatively correlated with the levels of GSH in all organs (Table 4).
The activities of SOD and expression levels of SOD gene in all tissues of experimental rats were demonstrated in Table 3. At most intervals, SOD activities and gene expression levels of tested organs in all experimental groups were markedly inhibited, as compared to group I. In groups II and V, SOD activity and SOD gene expression levels in all tissues, at most times, were markedly higher than in groups III and IV, respectively. By the fourteenth day, rats of groups II to V showed significant elevations in all organ activities of SOD and SOD gene expression levels toward the control value. In most organs of groups VI and VII, by the fourteenth day, SOD activity and SOD gene expression levels became similar to group I. Negative relationships were recorded between the activity of SOD and MDA levels, in all organs of rats treated with NiO-NPs or/and Co3O4-NPs (Table 4). Significant positive correlations were observed between the expression levels of SOD gene and the SOD activities in all tissues of all rats administered NiO-NPs or/and Co3O4-NPs (Table 5).
Effect of nanoparticles on zinc levels in tissues
The concentrations of Zn in all tissues of the experimental rats, throughout the experiments, were shown in Table 3. In most organs of groups II to VII, Zn levels were markedly lower than in group I, at all periods. By the fourteenth day, Zn levels in all tissues of all groups were significantly increased, as compared to the first day, and reached control levels except in brain of groups II and V as well as all organs of groups III and IV. In all organs of rats administered NiO-NPs or/and Co3O4-NPs, direct relationships were reported between the activities of SOD and the levels of Zn (Table 5).
Effect of nanoparticles on comet parameters
The comet assay results of all the experimental groups were clarified in Table 6. In all organs of groups II to VII, the %DNA damage, TL and TM, were markedly higher than in group I, at most durations. By the fourteenth day, %DNA damage, TL, and TM in tested organs of all groups were significantly declined, as compared to the first day. In all organs of groups III and IV, all comet parameters were mostly higher than those of groups II and V, respectively.
Effect of nanoparticles on the DNA fragmentation
The electrophoresed pattern of genomic DNA was obtained from the brain, hepatic, and renal tissues of all rats (Fig. 1). In consistence with the comet assay results, by the first and seventh days, the degree of DNA fragmentation in the liver and kidney of all groups from II to VII were more obvious than in the brain, as compared to the corresponding controls. By the fourteenth day, the degree of DNA damage was declined in most tissues of the studied groups.
Effect of nanoparticles on the reactive oxygen species production
In Fig. 2, the results of ROS generation in the studied organs of all groups were presented. As compared to group I, the fluorescence microscopic images all organs of groups II to VII revealed excessive productions of intracellular ROS, at all intervals, as represented by the high intensity of fluorescence.
The present study represents a continuation of a recent work in which the median lethal doses of the NiO-NPs or/and Co3O4-NPs as well as the accumulation patterns and toxicokinetics of their metal ions were estimated (Ali, 2018). The objective of the current work was to evaluate the genotoxicity and oxidative stress induced by NiO-NPs or/and Co3O4-NPs in the brain, liver, and kidney of male albino rats. All the alterations in the present study were in consistence with the accumulation pattern of NiO-NPs and Co3O4-NPs, in our recent study (Ali, 2018).
The present data revealed remarkable elevations of %DNA, TL, and TM in all organs of rats administered NiO-NPs or Co3O4-NPs solely. Single- and double-stranded breaks were evident in the genomic DNA after intake of NPs (Morsy et al., 2016a). Similarly, several previous studies reported DNA damage following exposure to NiO-NPs (Horie et al., 2011; Morimoto et al., 2011 and Dumala et al., 2017) and Co3O4-NPs (Alarifi et al., 2013; Uboldi et al., 2015 and Mohamed & Hussien, 2018). Due to their high surface area and subsequent increased reactivity, NPs can induce the production of ROS (Liu, Xu, Zhang, Ren, & Yang, 2010). Therefore, disturbances in DNA strand can be linked to the excessive generation of ROS (Rowe, Degtyareva, & Doetsch, 2008 and Kang, So, Simons, Spitz, & Ouchi, 2012). This was confirmed by the fluorescence microscopic images of the brain, liver, and kidney of the rats treated with NiO-NPs or Co3O4-NPs which demonstrated an overproduction of the intracellular ROS, in the current results. Moreover, the single- and double-stranded breaks of DNA can eventually trigger apoptosis (Green, 2011). This can explain the observed apoptotic DNA damages demonstrated by the electrophoresed pattern of genomic DNA in all tested tissues of rats administered NiO-NPs or Co3O4-NPs, individually. In the present data, the kidney and liver exhibited substantial DNA fragmentations as compared to the brain. This can be attributed to their ability to accumulate more NPs for further elimination (Morsy et al., 2016b).
Lipid peroxidation (LPO) represents the chief biomarker of the oxidative damage (Abdel Wahab, 2012). Once LPO is initiated, a chain of free radical-mediated reactions proceeds to produce several toxic byproducts such as the MDA (Prabhakar et al., 2012). The present study revealed remarkable elevations in MDA levels accompanied with significant depletions in the GSH content and SOD activity in the studied organs of rats administered NiO-NPs (with increasing dose) or Co3O4-NPs (with decreasing dose). Such disturbances in the endogenous homeostasis can be ascribed to direct action of accumulated NPs or their ions (Morsy, Abou El-Ala, & Ali, 2016a). In the same line, Ali (2018) reported that in all tissues of rats, the levels of accumulated Ni2+ were positively correlated with the doses of NiO-NPs whereas the accumulated levels of Co2+ were negatively correlated with administered doses of Co3O4-NPs. This was attributed to the high tendency of Co3O4-NPs, in biological fluids, more than NiO-NPs leading to reduced ionization of the former. Additionally, the present findings can be linked to the increased production of ROS that strongly attacks the double bonds of the polyunsaturated fatty acids giving rise to several products including the MDA (Sánchez-Iglesias et al., 2009). Moreover, MDA molecules can attack and combine with many functional groups on macromolecules including proteins, lipoproteins, and even DNA generating further DNA damage (Marnett, 2002), leading to the destruction of endogenous antioxidants including GSH and SOD which are mainly proteins. This was ensured, in the present results, by the inverse relationships of MDA levels with the GSH content and SOD activity. In addition, Zn is an essential element for the action of the cytoplasmic SOD (El-Khawaga & El-Sayed, 2012) as well as for the biosynthesis of GSH (Cortese, Suschek, Wetzel, Kroncke, & Kolb-Bachofen, 2008 and Li et al. 2010) Accordingly, the reduced activity of SOD and levels of GSH may be also attributed to the ability of NPs to interfere with Zn availability, as confirmed by the reduced tissue levels of Zn, in the present study. This was supported by the recorded direct relationships between Zn levels and SOD ativities, in the present study. Furthermore, the reduced activity of SOD can be related to the capability of NiO-NPs and Co3O4-NPs to reduce the expression levels of the Cu/Zn-SOD gene, as shown in the present data. On the contrary, by increasing the experimental time, GSH level and SOD activity were markedly increased concurrently with the increment of Zn and expression of Cu/Zn-SOD levels in tissues. Moreover, the remarkable depletion in the GSH levels as well as SOD activity can allow the increased production of ROS and subsequently an increased MDA levels.
Comet parameters in tested organs of rats administered NiO-NPs in combination with Co3O4-NPs were markedly lower than in groups administered NiO-NPs or Co3O4-NPs solely. This reflects that the concurrent administration of these NPs caused recurrence of normal DNA integrity leading to reduced genotoxicity. This was ensured by the observed partial DNA damages in electrophoresed tissues of the mixed groups. The reduced DNA damage can be linked to the recorded reduction in MDA levels and increased levels of GSH in tissues of these rats. Moreover, the relapse of the normal integrity of DNA can cause the reported remarkable elevations in the Cu/Zn-SOD expression levels and consequently elevated SOD activity. The recorded reduction of MDA levels may be also attributed to the ability of these NPs to diminish the accumulation whereas to enhance the elimination of each other from tissues (Ali, 2018). This can be achieved via competition between their ions on the same receptors on tissues (Vijver, Peijnenburg, & De Snoo, 2010).
Firstly, single oral administration of NiO-NPs or Co3O4-NPs caused DNA strand breaks, apoptotic damage, and ROS excessive generation that markedly increased the MDA levels whereas it significantly reduced the levels of Zn, GSH, and activity of SOD in the brain, liver, and kidney tissues. Secondly, the alterations in all the studied parameters in tissues of rats administered NiO-NPs or Co3O4-NPs were in time- and dose-dependent manner. Thirdly, the administration of NiO-NPs together with Co3O4-NPs substantially alleviated the genotoxicity and the oxidative stress induced by each of the NPs.
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Abdel Wahab, W. M. (2012). AlCl3-induced toxicity and oxidative stress in liver of male rats: protection by melatonin. Life Science Journal, 9(4), 1173–1182.
Ada, K., Turk, M., Oguztuzun, S., Kilic, M., Demirel, M., Tandogan, N., … Latif, O. (2010). Cytotoxicity and apoptotic effects of nickel oxide nanoparticles in cultured HeLa cells. Folia Histochemica et Cytobiologica, 48(4), 524–529.
Alarifi, S., Ali, D., Al Omar Suliman, Y., Ahamed, M., Siddiqui, M. A., & Al-Khedhairy, A. A. (2013). Oxidative stress contributes to cobalt oxide nanoparticles-induced cytotoxicity and DNA damage in human hepatocarcinoma cells. International Journal of Nanomedicine, 8, 189–199.
Ali, A. A. (2018). Bioaccumulation and toxicokinetics of the orally administered nanosized nickel and cobalt (II, III) oxides in male albino rats. Egyptian Journal of Zoology, (In Press).
Baek, Y. W., & An, Y. J. (2011). Microbial toxicity of metal oxide nanoparticles (CuO, NiO, ZnO, and Sb2O3) to Escherichia coli, Bacillus subtilis, and Streptococcus aureus. Science of the Total Environment, 409(8), 1603–1608.
Beutler, E., Duron, O., & Kelly, M. B. (1963). Improved method for the determination of blood glutathione. Journal of Laboratory and Clinical Medicine, 61, 882–888.
Biener, J., Wittstock, A., Baumann, T., Weissmüller, J., Bäumer, M., & Hamza, A. (2009). Surface chemistry in nanoscale materials. Materials, 2(4), 2404–2428.
Bucher, J. R., Hailey, J. R., Roycroft, J. R., Haseman, J. K., Sills, R. C., Grumbein, S. L., … Chou, B. J. (1999). Inhalation toxicity and carcinogenicity studies of cobalt sulfate. Toxicological Sciences, 49, 56–67.
Cavallo, D., Ciervo, A., Fresegna, A. M., Maiello, R., Tassone, P., Buresti, G., … Ursini, C. L. (2015). Investigation on cobalt-oxide nanoparticles cyto-genotoxicity and inflammatory response in two types of respiratory cells. Journal of Applied Toxicology, 35(10), 1102–1113.
Cortese, M. M., Suschek, C. V., Wetzel, W., Kroncke, K. D., & Kolb-Bachofen, V. (2008). Zinc protects endothelial cells from hydrogen peroxide via Nrf2-dependent stimulation of glutathione biosynthesis. Free Radical Biology and Medicine, 44, 2002–2012.
Demirbaş, A. (1999). Proximate and heavy metal composition in chicken meat and tissues. Food Chemistry, 67, 27–31.
Dumala, N., Mangalampalli, B., Chinde, S., Kumari, S. I., Mahoob, M., Rahman, M. F., & Grover, P. (2017). Genotoxicity study of nickel oxide nanoparticles in female Wister rats after acute oral exposure. Mutagenesis, 32, 417–427.
El-Khawaga, O. Y., & El-Sayed, I. H. (2012). Evaluation of trace elements and antioxidants in pre and post hemodialysis of chronic renal failure patients. International Journal of Natural Sciences, 3(3), 617–620.
Faisal, M., Saquib, Q., Alatar, A. A., Al-Khedhairy, A. A., Hegazy, A. K., & Musarrat, J. (2013). Phytotoxic hazards of NiO-nanoparticles in tomato: a study on mechanism of cell death. Journal of Hazardous Materials, 250, 318–332.
Gong, N., Shao, K., Feng, W., Lin, Z., Liang, C., & Sun, Y. (2011). Biotoxicity of nickel oxide nanoparticles and bio-remediation by microalgae Chlorella vulgaris. Chemosphere, 83(4), 510–516.
Green, D. (2011). Means to an end: apoptosis and other cell death mechanisms. Cold Spring Harbor: Cold Spring Harbor Laboratory Press ISBN 978-0-87969-888-1.
Horie, M., Fukui, H., Nishio, K., Endoh, S., Kato, H., Fujita, K., … Kinugasa, S. (2011). Evaluation of acute oxidative stress induced by NiO nanoparticles in vivo and in vitro. Journal of Occupational Health, 53(2), 64–74.
Jeon, Y. M., Park, S. K., Rhee, S. K., & Lee, M. Y. (2010). Proteomic profiling of the differentially expressed proteins by TiO2 nanoparticles in mouse kidney. Molecular and Cellular Toxicology, 6, 419–425.
Jiménez-Ortega, V., Cano, P., Cardinali, D. P., & Esquifino, A. I. (2009). 24-hour variation in gene expression of redox pathway enzymes in rat hypothalamus: effect of melatonin treatment. Redox Reports, 14(3), 132–138.
Kang, M. A., So, E. Y., Simons, A. L., Spitz, D. R., & Ouchi, T. (2012). DNA damage induces reactive oxygen species generation through the H2AX-Nox1/Rac1 pathway. Cell Death and Disease, 3(1), e249. https://doi.org/10.1038/cddis.2011.134.
Kirkland, D., Brock, T., Haddouk, H., Hargeaves, V., Lloyd, M., Mc Garry, S., … Sokolowski, A. (2015). New investigations into the genotoxicity of cobalt compounds and their impact on overall assessment of genotoxic risk. Regulatory Toxicology and Pharmacology, 73(1), 311–338.
Liu, S., Xu, L., Zhang, T., Ren, G., & Yang, Z. (2010). Oxidative stress and apoptosis induced by nanosized titanium dioxide in PC12 cells. Toxicology, 267(1–3), 172–177.
Lu, S., Duffin, R., Poland, C., Daly, P., Murphy, F., Drost, E., … Donaldson, K. (2008). Efficacy of simple short-term in vitro assays for predicting the potential of metal oxide nanoparticles to cause pulmonary inflammation. Environmental Health Perspectives, 117(2), 241–247.
Magaye, R., Gu, Y., Wang, Y., Su, H., Zhou, Q., Mao, G., … Zhao, J. (2016). In vitro and in vivo evaluation of the toxicities induced by metallic nickel nano and fine particles. Journal of Molecular Histology, 47(3), 273–286.
Magaye, R., Zhao, J., Bowman, L., & Ding, M. (2012). Genotoxicity and carcinogenicity of cobalt-, nickel-and copper-based nanoparticles. Experimental and Therapeutic Medicine, 4(4), 551–561.
Marnett, L. J. (2002). Lipid peroxidation—DNA damage by malondialdehyde. Mutation Research, 424, 83–95.
Mohamed, H. R. H., & Hussien, N. A. (2018). Amelioration of cobalt oxide nanoparticles induced genomic and mitochondrial DNA damage and oxidative stress by omega-3 co-administration in mice. Caryologia, 71(4), 357–364.
Morimoto, Y., Hirohashi, M., Ogami, A., Oyabu, T., Myojo, T., Hashiba, M., … Tanaka, I. (2011). Pulmonary toxicity following an intratracheal instillation of nickel oxide nanoparticle agglomerates. Journal of Occupational Health, 53(4), 293–295.
Morsy, G. M., Abou El-Ala, K. S., & Ali, A. A. (2016a). Studies on fate and toxicity of nanoalumina in male albino rats: oxidative stress in the brain, liver and kidney. Toxicology and industrial health, 32(2), 200-214.
Morsy, G. M., El-Ala, K. S. A., & Ali, A. A. (2016b). Studies on fate and toxicity of nanoalumina in male albino rats: lethality, bioaccumulation and genotoxicity. Toxicology and industrial health, 32(2), 344-359.
Nishikimi, M., Roa, N. A., & Yogi, K. (1972). Measurement of superoxide dismutase. Biochemical and Biophysical Research Communications, 46, 849–854.
Ohkawa, H., Ohishi, W., & Yagi, K. (1979). Assay for lipid peroxides in animal tissues by thiobarbituric acid reaction. Analytical Biochemistry, 95, 351–358.
Pietruska, J. R., Liu, X., Smith, A., McNeil, K., Weston, P., Zhitkovich, A., … Kane, A. B. (2011). Bioavailability, intracellular mobilization of nickel, and HIF-1α activation in human lung epithelial cells exposed to metallic nickel and nickel oxide nanoparticles. Toxicological Sciences, 124(1), 138–148.
Prabhakar, P. V., Reddy, U. A., Singh, S. P., Balasubramanyam, A., Rahman, M. F., Indu Kumari, S., Mahboob, M. (2012). Oxidative stress induced by aluminum oxide nanomaterials after acute oral treatment in Wistar rats. Journal of Applied Toxicology, 32(6), 436–445.
Rowe, L. A., Degtyareva, N., & Doetsch, P. W. (2008). DNA damage-induced reactive oxygen species (ROS) stress response in Saccharomyces cerevisiae. Free Radical Biology and Medicine, 45(8), 1167–1177.
Sánchez-Iglesias, S., Méndez-Álvarez, E., Iglesias-González, J., Muñoz-Patiño, A., Sánchez-Sellero, I., Labandeira-García, J. L., & Soto-Otero, R. (2009). Brain oxidative stress and selective behaviour of aluminium in specific areas of rat brain: potential effects in a 6-OHDA-induced model of Parkinson’s disease. Journal of Neurochemistry, 109(3), 879–888.
Schneiderová, B., Demel, J., Zhigunov, A., Bohuslav, J., Tarábková, H., Janda, P., & Lang, K. (2017). Nickel-cobalt hydroxide nanosheets: synthesis, morphology and electrochemical properties. Journal of Colloid and Interface Science, 499, 138–144.
Siddiqui, M. A., Kashyap, M. P., Kumar, V., Al-Khedhairy, A. A., Musarrat, J., & Pant, A. B. (2010). Protective potential of trans-resveratrol against 4-hydroxynonenal induced damage in PC12 cells. Toxicology In Vitro, 24(6), 1592–1598.
Sriram, M. I., Kanth, S. B. M., Kalishwaralal, K., & Gurunathan, S. (2010). Antitumor activity of silver nanoparticles in Dalton’s lymphoma ascites tumor model. International Journal of Nanomedicine, 5, 753–762.
Sundar, L. S., Anjum, N. A., Ferro, M. C., Pereira, E., Singh, M. K., & Sousa, A. C. M. (2017). Biocompatibility and biotoxicity of in-situ synthesized carboxylated nanodiamond-cobalt oxide nanocomposite. Journal of Materials Science & Technology, 33(8), 879–888.
Tice, R. R., Agurell, E., Anderson, D., Burlinson, B., Hartmann, A., Kobayashi, H., … Sasaki, Y. F. (2000). Single cell gel/comet assay: guidelines for in vitro and in vivo genetic toxicology testing. Environmental and Molecular Mutagenesis, 35(3), 206–221.
Uboldi, C., Orsière, T., Darolles, C., Aloin, V., Tassistro, V., George, I., & Malard, V. (2015). Poorly soluble cobalt oxide particles trigger genotoxicity via multiple pathways. Particle and Fibre Toxicology, 13(1), 5–15.
Vijver, M. G., Peijnenburg, W. J., & De Snoo, G. R. (2010). Toxicological mixture models are based on inadequate assumptions. Environmental Science & Technology, 44, 4841–4842.
Wang, H., & Joseph, J. A. (1999). Quantifying cellular oxidative stress by dichlorofluorescein assay using microplate reader1. Free Radical Biology and Medicine, 27(5–6), 612–616.
Zhang, C. L., Zeng, T., Zhao, X. L., Yu, L. H., Zhu, Z. P., & Xie, K. Q. (2012). Protective effects of garlic oil on hepatocarcinoma induced by N-nitrosodiethylamine in rats. International Journal of Biological Sciences, 8(3), 363–374.
Zhao, J., Shi, X., Castranova, V., & Ding, M. (2009). Occupational toxicology of nickel and nickel compounds. Journal of Environmental Pathology, Toxicology and Oncology, 28(3),177-208.
We acknowledge the continuous support of our department and our colleagues.
Funding was provided by Faculty of Science, Cairo University.
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All data are available upon request.
All the applied procedures were approved by Cairo University- Institutional Animal Care and Use Committee (CU-IACUC), Giza, Egypt. The protocol approval number was CU/I/F/97/17 at November 2017. The animal handling was in accordance to the international guidelines of the laboratory animal care and use.
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Ali, A.AM., Mohamed, H.R.H. Genotoxicity and oxidative stress induced by the orally administered nanosized nickel and cobalt oxides in male albino rats. JoBAZ 80, 2 (2019). https://doi.org/10.1186/s41936-018-0072-0