- Research article
- Open Access
Cobalt oxide nanoparticles aggravate DNA damage and cell death in eggplant via mitochondrial swelling and NO signaling pathway
Biological Researchvolume 49, Article number: 20 (2016)
Despite manifold benefits of nanoparticles (NPs), less information on the risks of NPs to human health and environment has been studied. Cobalt oxide nanoparticles (Co3O4-NPs) have been reported to cause toxicity in several organisms. In this study, we have investigated the role of Co3O4-NPs in inducing phytotoxicity, cellular DNA damage and apoptosis in eggplant (Solanum melongena L. cv. Violetta lunga 2). To the best of our knowledge, this is the first report on Co3O4-NPs showing phytotoxicity in eggplant.
The data revealed that eggplant seeds treated with Co3O4-NPs for 2 h at a concentration of 1.0 mg/ml retarded root length by 81.5 % upon 7 days incubation in a moist chamber. Ultrastructural analysis by transmission electron microscopy (TEM) demonstrated the uptake and translocation of Co3O4-NPs into the cytoplasm. Intracellular presence of Co3O4-NPs triggered subcellular changes such as degeneration of mitochondrial cristae, abundance of peroxisomes and excessive vacuolization. Flow cytometric analysis of Co3O4-NPs (1.0 mg/ml) treated root protoplasts revealed 157, 282 and 178 % increase in reactive oxygen species (ROS), membrane potential (ΔΨm) and nitric oxide (NO), respectively. Besides, the esterase activity in treated protoplasts was also found compromised. About 2.4-fold greater level of DNA damage, as compared to untreated control was observed in Comet assay, and 73.2 % of Co3O4-NPs treated cells appeared apoptotic in flow cytometry based cell cycle analysis.
This study demonstrate the phytotoxic potential of Co3O4-NPs in terms of reduction in seed germination, root growth, greater level of DNA and mitochondrial damage, oxidative stress and cell death in eggplant. The data generated from this study will provide a strong background to draw attention on Co3O4-NPs environmental hazards to vegetable crops.
Over a last decade, nanotechnology has gained an immense research interest due to its applications in public health, medicine, industry and agriculture. The incessant use of nanoparticles (NPs) in a multitude of sectors presents a risk of their release into the environment, which may pose serious threats on ecosystem and adversely affect its living entity . Particularly, plants are at maximum risk due to the concentration build-up of NPs in natural sediments, agricultural soils, and aquatic environments [1, 2]. Recent evidences on the NPs toxicity demonstrated the cellular uptake of Ag-NPs in Oryza Sativa and Cu/CuO-NPs in Lactuca sativa [3, 4]. Vicia faba exposed to multiwalled carbon nano tubes exhibited imbalance of nutrient elements, leaves damage and oxidative stress . The uptake and translocation of TiO2-NPs in Allium cepa induces heavy ROS generation, sticky, multipolar and laggard chromosomes, including micronucleus formation and DNA damage . These effects of NPs are primarily associated with their increased surface area and reactivity, ROS generation and the tendency to form agglomerates . We have selected Co3O4-NPs for the current investigation due to its unique physical properties, applications in pigments, catalysis, sensors, electrochemistry, magnetism and energy storage . In addition, the composites of Co3O4-NPs with multiwalled carbon nanotubes have been proposed for fabricating high-performance electronic devices .
Till date, only a solitary report on Co3O4-NPs demonstrated the reduction of root length in A. cepa, without much elaboration on the nature of cellular damage and mechanism of the phytotoxicity . Therefore, in this study, we have investigated the mechanistic aspects of Co3O4-NPs toxicity in eggplant (Solanum melongena L. cv. Violetta lunga 2), an economically important vegetable crop, as a model, using state-of-the-art techniques like transmission electron microscopy (TEM), comet assay and flow cytometry. This will help in understanding as to how the plant responds to NPs exposure and regulates the molecular mechanism of cell death pathways. Since no systematic study has been attempted so far, describing the mechanism of Co3O4-NPs induced phytotoxicity in eggplant at cellular and molecular levels, we have investigated the effect of Co3O4-NPs on eggplant cells to assess the (1) phytotoxicity, (2) translocation of Co3O4-NPs in root cells and subcellular anomalies, (3) intracellular ROS generation and mitochondrial dysfunction (ΔΨm), (4) DNA damage (5) cell cycle alterations, NO generation and esterase activity.
Results and discussion
Size and morphology of Co3O4-NPs were examined by TEM and AFM analyses. TEM image in Fig. 1 revealed the morphology of Co3O4-NPs as crystallite spheres with polyhedral structure, and aggregates have been observed. The average particle size of Co3O4-NPs determined from six different TEM images were 21.3 nm (Fig. 1a). AFM analysis of Co3O4-NPs exhibited the size of NPs to be 40 nm (Fig. 1b). Since, the sizes of NPs are regarded as important parameters for cellular toxicity; the behavior of Co3O4-NPs in treatment solutions was examined through DLS, to understand the extent of aggregation and secondary size of NPs. The data revealed large particle aggregates of 359.7 ± 2.1 nm with ζ-potential of −6.2 ± 1.3 mv (Fig. 1c, d). DLS is widely used to determine the size of Brownian NPs in colloidal suspensions in the nano and submicron ranges . The average hydrodynamic particle’s diameter in water indicates particle aggregation. Our characterization data corroborates well with the recent report on agglomeration of NPs in an aqueous environment .
Co3O4-NPs treatment retarded the root growth of eggplant
Co3O4-NPs treated seeds exhibited a tendency to adsorb on the seed coat in a concentration dependent manner, while bulk Co3O4 did not display adsorption behavior on the seeds (Fig. 2a). These observations are in line with our previous report exhibiting the adsorption tendency NiO-NPs on the tomato seeds . Such behavior could be due to the physical attachment of particles on a rough seed surface, electrostatic attraction and hydrophobic interactions between seeds and NP agglomerates. It is likely that the adsorption of NPs may facilitate the release of ions locally to enhance phytotoxic effects . Exposure concentrations for Co3O4-NPs were selected based on the screening of low to high concentrations (0.025–1.0 mg/ml) of Co3O4-NPs to affect the root length. Since, the primary objective of this study was to assess the toxicity of Co3O4-NPs. Therefore, the non-significant concentrations (0.025–0.1 mg/ml) in terms of repression of root lengths were excluded from further toxicity experiments. After 7 days of incubation, average root lengths recorded at 0.5 and 1.0 mg/ml of Co3O4-NPs were 1.0 ± 0.16 and 0.70 ± 0.18 cm (p < 0.01) respectively. The root length in untreated control was 3.80 ± 0.24 cm (Fig. 2b). Under similar experimental conditions, bulk Co3O4 did not induce repression of root length (Fig. 2b). Phenotypic analysis of roots revealed that Co3O4-NPs (0.25, 0.5 and 1.0 mg/ml) treated groups exhibited a dose-dependent reduction in root length along with thickening, stunted growth and absence of root hairs. However, no such changes have been observed in bulk Co3O4 treated groups (Fig. 2c). Due to the non-significant effects of bulk Co3O4 on eggplant root length, we have excluded bulk Co3O4 in further experiments. Comparison of data with our recently published studies on NiO-NPs induced toxicity in tomato, suggested that Co3O4-NPs are more growth inhibitory at the highest concentration of 1.0 mg/ml and exhibited 2.14-fold greater repression of root length in eggplant. Thickening and stunted roots were observed at all treatment concentrations of Co3O4-NPs after 7 days, while the NiO-NPs treated tomato roots were found thickened and stunted only at greater concentrations of 1.5 and 2 mg/ml after 10 days of exposure , thus, suggesting the higher toxicity of Co3O4-NPs. The differences in toxicity of Co3O4-NPs over NiO-NPs can be attributed to the difference in seed size of the two plants. Indeed, the interactions of similar-sized NPs might be greater for the smaller seeds of eggplant as compared to the larger sized tomato seeds, largely due to greater surface-to-volume ratio of the small-sized seeds to that of the large-sized seeds . These observations corroborate well with earlier literature suggesting greater phytotoxicity of rare earth oxide NPs to the smaller seeds (rape, cabbage, radish), as compared to the larger seeds of wheat . Nonetheless, our results are in agreement with some recent findings, which have also demonstrated the repression of root length by CuO and Ag-NPs in Arabidopsis thaliana [3, 14]. Seed coat provides first line of defense to the seed from NPs during the germination. However, in this study we have demonstrated that seedling roots after piercing the seed coat, become the main organ to confront Co3O4-NPs. Therefore, the toxic symptoms were more evident in roots than in other parts of seedlings. In addition, seeds rough surface, electrostatic attraction and hydrophobic interactions contributed towards NPs adsorption on the seeds. Such adsorption may facilitate the release of ions from NPs and enhance the phytotoxicity .
Co3O4-NPs uptake and translocation
To confirm the translocation of Co3O4-NPs, ultrathin sections of root tissues from elongation zone were evaluated by TEM (Fig. 3a–f). Root elongation zone consists of newly formed differentiated cells, which elongate at a rapid rate and exhibit enhanced cell cycle activity. Co3O4-NPs were observed in the cytoplasm and exterior region of confluent parenchymal cells (Fig. 3c, d). NPs were recognized as dark dots and aggregates entrapped in cell vacuoles. Our TEM data on Co3O4-NPs corroborate with recent studies exhibiting the translocation of Ag and ZnO-NPs Triticum aestivum and Schoenoplectus tabernaemontani [16, 17]. In addition, enhanced number of peroxisomes and mitochondria with degenerated cristae has also been encountered (Fig. 3c, e, f). These subcellular anomalies are found identical as observed in plants exposed to ozone . Interestingly, the eukaryotic microorganism (yeast) has also demonstrated these common properties of peroxisome biogenesis as a consequence of mitochondrial dysfunction .
Intracellular ROS production and mitochondrial dysfunction
Qualitative evaluation of Co3O4-NPs treated roots exhibited a conspicuous increase in DCF fluorescence. Eggplant roots stained with fluorescent dye DCFH-DA revealed a typical pattern of ROS localization as a function of Co3O4-NPs concentration. Compared to the untreated control, Co3O4-NPs at 0.25 and 0.5 mg/ml showed ROS localization around apical root meristem. Subsequently, the ROS localization becomes more intense towards root elongation zone at 1.0 mg/ml. (Figure 4a). Protoplasts quantitatively analyzed on flow cytometry also revealed higher levels of intracellular ROS. Relative to 100 % DCF fluorescence in control, Co3O4-NPs (0.25, 0.5 and 1.0 mg/ml) treatments resulted in 167.0, 177.4 and 157.6 % greater ROS generation (Fig. 4b, c). Our ROS data is in line with a previous study demonstrated oxidative stress in Oryza sativa treated with multiwalled carbon nanotubes . It is well established that ROS rapidly interacts with distant cellular organelles and may result in DNA strand breaks, purine oxidation, protein modifications, protein-DNA cross links and mitochondrial damage [21, 22].
The interplay of ROS and mitochondria has further lead us to analyze ΔΨm using mitochondrial specific dye Rh123. Qualitative evaluation of seedling roots from Co3O4-NPs treatment groups exhibited enhancement in the fluorescence intensity of Rh123 (Fig. 5a). A similar pattern of fluorescence enhancement has been observed in the protoplasts of Co3O4-NPs exposed groups. Flow cytometric analysis of protoplasts revealed 136.6, 144.2 and 282.4 % greater fluorescence at 0.25, 0.5 and 1.0 mg/ml concentrations (Fig. 5b, c). Mitochondrial dysfunction as a consequence of oxidative stress is an important factor in cell death [23, 24]. Fluorescence enhancement of Rh123 dye is related to the variation in ΔΨm, which results as a consequence of swelling and shrinking properties of mitochondria . Due to these morphological alterations, preferably by swelling, Rh123 leaks out from mitochondria to the cytoplasm . Therefore, Co3O4-NPs mediated enhancement of Rh123 florescence confirm mitochondrial swelling in eggplant and the leakage of dye thus causing Rh123 hyperpolarization in cytoplasm.
NO and esterase analysis
Flow cytometric analysis of Co3O4-NPs treated protoplasts exhibited an increase in intracellular NO generation. Relative to 100 % fluorescence in control, protoplasts isolated from 0.25, 0.5 and 1.0 mg/ml Co3O4-NPs treated cells showed 169.8, 242.5 and 178.7 % (p < 0.01) higher fluorescence of DAF2-DA (Fig. 6a, b). Our data is in line with earlier studies, which also suggested an elevated level of NO generation in Lupinus luteus and Glycine max exposed to Cd++ [27, 28]. NO has been regarded as an effective inducer of cell death by interfering with mitochondria functionality and promoting imbalance between ROS generation and scavenging . Furthermore, NO has been described as a small signaling molecule in plants taking part in several events throughout the life cycle, as well as in defense against biotic and abiotic stresses .
We further investigated the level of intracellular esterases, regarded as a prevalent biomarker to assess the viability of cells . Relative to 100 % fluorescence of CFDA in control, Co3O4-NPs treated root cells at the concentrations of 0.5 and 1.0 mg/ml exhibited a decline by 29.7 and 45.2 %, respectively. However, no significant change in the esterase level has been observed at 0.25 mg/ml (Fig. 6c, d). CFDA fluoresces strongly when de-esterified to carboxyfluorescein (CF). Conversion to CF by cells indicates the integrity of the plasma membrane. An intact membrane prevents leakage of the polar dye into the medium and maintains cytoplasmic milieu, which is needed to support esterase activity . Therefore, the suppressed esterase level in this study primarily suggests that Co3O4-NPs induce membrane damage in protoplasts and in mitochondria of eggplant cells.
Co3O4-NPs induced DNA damage
Alkaline single cell gel electrophoresis (comet assay) data showed Co3O4-NPs-induced single strand breaks in DNA of eggplant cells. The representative digitized image of comet tail in Co3O4-NPs (1.0 mg/ml) treated group clearly demonstrates the extent of broken DNA liberated from head of the comet during electrophoresis (Fig. 7 inset). However, under identical condition the control cell exhibited round boundary of nuclear head DNA. A conspicuous tail in positive control ethyl methanesulfonate (EMS 2 mM) confirms the proper functioning of comet setup (Fig. 7 inset). Compared to the olive tail moment (OTM) value of 1.22 ± 0.12 in control, the quantitative data obtained from 150 cells of Co3O4-NPs (0.25, 0.5 and 1.0 mg/ml) treatment groups exhibited an increase of 2.6 ± 0.49, 3.0 ± 0.14 and 3.2 ± 0.35 (p < 0.01), respectively, over control (Fig. 7). The DNA damaging activity of Co3O4-NPs has been found to be similar to the DNA damaging effect of TiO2 and ZnO-NPs reported in A. cepa . Thus, the results substantiate the hypothesis that plant-NPs interaction is associated with the genotoxicity and concurs well with the earlier reports. Metal oxides as well as metals are involved in ROS formation, which can interact directly or indirectly with plant DNA to induce strand breaks [33, 34]. However, on the basis of our data we suggest that Co3O4-NPs may have indirectly induce DNA damage in eggplant, as evident from increase in the ROS, mitochondrial membrane damage and elevated esterase level. On the contrary, the NiO-NPs may have directly interacted with the DNA to induce non-repairable heavy damage; as a result an increasing number of apoptotic/necrotic cells were appeared in the comet assay of tomato cells . Thus, an in-depth investigation is warranted in order to ascertain the extent and nature of direct interactions of Co3O4-NPs using spectrofluorometric, spectrophotometric biophysical and bioinformatics tools.
Flow cytometric analysis of apoptosis
In order to assess Co3O4-NPs induced cell death, the apoptotic events occurred in treated eggplants cells were captured by use of a flow cytometer. The propiodium iodide (PI) stained nuclei of Co3O4-NPs treatment groups indicated a concentration dependent increase in apoptotic sub-G1 peak (Fig. 8a). In comparison with 24.4 % of background apoptotic cells in control, Co3O4-NPs at 0.25, 0.5 and 1.0 mg/ml exhibited 44.4, 69.8 and 73.2 % of apoptotic population (Fig. 8b). A similar mode of cell death has also been observed in our earlier report on tomato cells exposed to NiO-NPs . Furthermore, our ongoing studies on cultured human cell lines with Co3O4-NPs have demonstrated that these NPs have the potential to induce apoptosis in the human cell lines (data unpublished). It is widely accepted that apoptotic mechanisms in plants and animals share some common components leading to conserved cellular events [35, 36]. Therefore, it is likely that eggplant root cells may activate a similar mechanism of cell death.
In conclusion, our study demonstrates that eggplant exposed to Co3O4-NPs exhibited a significant repression of root growth due to phytotoxic properties of NPs. Ultrastructural analysis suggests the subcellular localization of Co3O4-NPs to induce organelles damage. Fluorescence imaging and flow cytometric data supported the fact that ROS plays a crucial role in mitochondrial damage to trigger apoptosis in eggplant. Higher level of NO and mitochondrial membrane damage revealed that Co3O4-NPs trigger cell death in eggplant via mitochondrial swelling and stimulation of NO signaling pathway. Furthermore, the depletion of esterase activities in cells could serve as a useful biomarker of Co3O4-NPs mediated cellular stress. Presumably, the root cells exhibiting NPs induced cell death may share some similar apoptotic characters, as observed in animals. Nonetheless, a deep investigation is warranted on transcriptome analysis to investigate the possible connection between different apoptotic factors. Finally, we conclude with the remark that the current findings will provide strong background to explore NPs induced toxicity at field or farm level to determine a realistic exposure scenario for other crops.
Characterization of nanoparticles
Co3O4-NPs (1 mg/ml) (Cat. No. 637025, Sigma-Aldrich, St. Louis, MO, USA) were sonicated in ultrapure water for 10 min at 50 W, and the solution was dropped on copper grids of the transmission electron microscope (TEM). A total of six grids of Co3O4-NPs were prepared and subjected to TEM analysis at 200 keV. Characterizations of Co3O4-NPs were further done by analyzing the surface topography of powdered Co3O4-NPs using atomic force microscope (AFM) (Veeco Instruments, USA) in non-contact tapping mode. The topographical images were obtained in tapping mode with a resonance frequency of 218 kHz. Characterization of Co3O4-NPs was further done in liquid environment by measuring the dynamic light scattering (DLS) and zeta (ζ)-potential using Zetasizer 2000 (ZetaSizer-HT, Malvern, UK). Briefly, Co3O4-NPs stock suspension of 10 µg/ml was prepared in ultrapure water, sonicated for 15 min at 40 W and the solutions were analyzed for DLS and ζ-potential, values presented were the average of 10 readings.
Eggplant root length retardation by Co3O4-NPs and bulk Co3O4
To determine the phytotoxicity in Solanum melongena L. cv. Violetta lunga 2. (eggplant), we have selected Co3O4-NPs and its bulk counterpart Co3O4 (Cat. No. 221643, Sigma-Aldrich, St. Louis, MO, USA). Seeds of eggplant were surface sterilized in Clorox solution (5 % v/v) for 10 min followed by through washing with distilled water. The exposure concentrations of Co3O4-NPs were selected from initial experiments based on the root elongation assay. For each set of experiment, 20 seeds were treated with 0.025, 0.05, 0.1, 0.25, 0.5 and 1.0 mg/ml of Co3O4-NPs (<50 nm) and bulk Co3O4 (<10 µm) suspensions for 2 h on a rotary shaker. Parallel untreated controls were run under identical conditions. After treatment, seeds were thoroughly washed with distilled water and transferred to Petri dishes containing wet filter papers. Petri dishes were kept in the growth chamber at 25 ± 2 °C for 7 days for seed germination and growth.
Uptake of Co3O4-NPs
Subcellular changes in eggplant root cells were analyzed by use of TEM. Root tissues from control and Co3O4-NPs (1.0 mg/ml) groups were fixed in glutaraldehyde for 10 min; followed by re-suspension of root sections in OsO4 (1 %) for 1 h at 4 °C. An additional incubation of 1 h was given for each section in 2 % aqueous uranyl acetate pursued by the dehydration of sections using ascending grade of ethanol. Root sections were finally embedded in low viscosity araldite resin and ultrathin sections of 80 nm were made from elongation zone for TEM analysis under high vacuum (100 kV).
Flow cytometric analysis of intracellular ROS and mitochondrial dysfunction (ΔΨm)
For qualitative analysis of ROS and ΔΨm, Co3O4-NPs treated seedling roots were stained with 2′,7′-dichlorofluorescin diacetate (DCFH-DA) (0.25 µM) and 1 µg/ml of rhodamine 123 (Rh123) for 15 min. Roots were washed three times with PBS, and images were captured using a fluorescence microscope (Nikon Eclipse 80i, Japan) [10, 11]. Quantitative estimation of intracellular ROS and ΔΨm was done in protoplasts isolated from control and Co3O4-NPs treated groups according to the method of Imanishi et al. , with slight modification . In brief, 10 root tissues from each of control and treated samples were incubated in 1.5 % cellulose, 0.5 % pectinase (Sigma) in Galbraith buffer (45 mM MgCl2, 30 mM sodium citrate, 20 mM MOPS, 0.1 % (v/v) Triton X-100, pH 7.0) for overnight in the dark at 26 °C. The digested root/enzyme solution was filtered through a 100 µm sieve and viable cells recovered by flotation after centrifugation in Galbraith buffer. Centrifugation and recovery steps of intact cells were repeated thrice to remove enzymes. Protoplasts from control and Co3O4-NPs treated groups were separately stained with DCFH-DA (5 µM) and Rh123 (5 µg/ml) for 1 h in the dark at room temperature. Fluorescence of 10,000 protoplasts from each dye treatment was recorded on Beckman Coulter flow cytometer (Coulter Epics XL/Xl-MCL, USA) following our previously described methods [38, 39].
Assessment of NO and esterase activity by flow cytometer
Intracellular NO and esterase activities in protoplasts were measured using flow cytometry. Protoplasts isolated from Co3O4-NPs treated, and untreated eggplant seedling roots were washed twice with PBS and incubated with NO specific dye 4,5-diaminofluorescein diacetate (DAF2-DA, 5 µM) and esterase specific carboxyfluorescein diacetate (CFDA, 5 µM) for 60 min in the dark at room temperature. The protoplast suspensions were pelleted, followed by two successive washes with PBS at 3000 rpm at 4 °C for 4 min. The protoplasts were re-suspended in a final volume of 500 µl of PBS and the fluorescence of DAF2-DA and CFDA was measured in 10,000 protoplasts using a flow cytometer at log scale (FL-1, 530 nm).
DNA damage analysis by alkaline comet assay
The comet assay was performed to analyze the DNA damage in nuclei following the method described by Faisal et al. . Nuclei were isolated by chopping the root tissues using a sharp scalpel blade in 1.0 ml of Galbraith buffer (45 mM MgCl2, 30 mM sodium citrate, 20 mM MOPS, 0.1 % (v/v) Triton X-100, pH 7.0). Comet slides were prepared following our previously described method .
Flow cytometric analysis of apoptosis in eggplant
Apoptosis analysis in eggplant roots was done using flow cytometry following our previously described method . Nuclei suspensions (1.0 ml) from control and Co3O4-NPs treated groups were stained with 10 µg/ml of DNA intercalating fluorescent dye (propidium iodide, PI) and RNAase A (50 µg/ml) solutions for 10 min on ice. Red fluorescence of 100,000 events of PI stained nuclei were acquired in FL4 Log channel through a 675 nm band-pass filter . Data were analyzed excluding the cell debris, characterized by a low FSC/SSC, using Beckman Coulter flow cytometer (Coulter Epics XL/Xl-MCL, USA and System II Software, Version 3.0).
Data were expressed as mean ± standard deviation (SD) for the values obtained from at least three independent experiments using 20 seeds/concentration. Statistical analysis was performed by one-way analysis of variance (ANOVA) followed by Dunnett’s multiple comparisons test (Sigma Plot 11.0, USA). The level of statistical significance chosen was p < 0.05, unless otherwise stated.
Navarro E, Baun A, Behra R, Hartmann NB, Filser J, Miao AJ, Quigg A, Santschi PH, Sigg L. Environmental behavior and ecotoxicity of engineered nanoparticles to algae, plants, and fungi. Ecotoxicology. 2008;17:372–86.
Liu HH, Cohen Y. Multimedia environmental distribution of engineered nano-materials. Environ Sci Technol. 2014;48:3281–92.
Thuesombat P, Hannongbua S, Akasit S, Chadchawan S. Effect of silver nanoparticles on rice (Oryza sativa L. cv. KDML 105) seed germination and seedling growth. Ecotoxicol Environ Saf. 2014;104:302–9.
Trujillo-Reyes J, Majumdar S, Botez CE, Peralta-Videa JR, Gardea-Torresdey JL. Exposure studies of core-shell Fe/Fe(3)O(4) and Cu/CuO NPs to lettuce (Lactuca sativa) plants: are they a potential physiological and nutritional hazard? J Hazard Mater. 2014;267:255–63.
Wang C, Liu H, Chen J, Tian Y, Shi J, Li D, Guo C, Ma Q. Carboxylated multi-walled carbon nanotubes aggravated biochemical and subcellular damages in leaves of broad bean (Vicia faba L.) seedlings under combined stress of lead and cadmium. J Hazard Mater. 2014;274:404–12.
Pakrashi S, Jain N, Dalai S, Jayakumar J, Chandrasekaran PT, Raichur AM, Chandrasekaran N, Mukherjee A. In vivo genotoxicity assessment of titanium dioxide nanoparticles by Allium cepa root tip assay at high exposure concentrations. PLoS One. 2014;9:e87789.
Liu X, Qiu G, Li X. Shape-controlled synthesis and properties of uniform spinel cobalt oxide nanotubes. Nanotechnology. 2005;16:3035–40.
Fu L, Liu Z, Liu Y, Han B, Hu P, Cao L, Zhu D. Beaded cobalt oxide beaded cobalt oxide nanoparticles along carbon nanotubes: towards more highly integrated electronic devices. Adv Mater. 2005;17:217–21.
Ghodake G, Seo YD, Lee DS. Hazardous phytotoxic nature of cobalt and zinc oxide nanoparticles assessed using Allium cepa. J Hazard Mater. 2010;186:952–9555.
Berne BJ, Pecora R. Dynamic light scattering: with applications to chemistry, biology and physics. Mineola: Dover Publications; 2000.
Faisal M, Saquib Q, Alatar AA, Al-Khedhairy AA, Hegazy AK, Musarrat J. Phytotoxic hazards of NiO-nanoparticles in tomato: a study on mechanism of cell death. J Hazard Mater. 2013;250–251:318–32.
Lin D, Xing B. Root uptake and phytotoxicity of ZnO nanoparticles. Environ Sci Technol. 2008;42:5580–5.
Ma Y, Kuang L, He X, Bai W, Ding Y, Zhang Z, Zhao Y, Chai Z. Effects of rare earth oxide nanoparticles on root elongation of plants. Chemosphere. 2010;78:273–9.
Nair PM, Chung IM. Impact of copper oxide nanoparticles exposure on Arabidopsis thaliana growth, root system development, root lignificaion, and molecular level changes. Environ Sci Pollut Res Int. 2014;21:12709–127022.
Atha DH, Wang H, Petersen EJ, Cleveland D, Holbrook RD, Jaruga P, Dizdaroglu M, Xing B, Nelson BC. Copper oxide nanoparticle mediated DNA damage in terrestrial plant models. Environ Sci Technol. 2012;46:1819–27.
Vannini C, Domingo G, Onelli E, De Mattia F, Bruni I, Marsoni M, Bracale M. Phytotoxic and genotoxic effects of silver nanoparticles exposure on germinating wheat seedlings. J Plant Physiol. 2014;171:1142–8. doi:10.1016/j.jplph.2014.05.002.
Zhang D, Hua T, Xiao F, Chen C, Gersberg RM, Liu Y, Stuckey D, Ng WJ, Tan SK. Phytotoxicity and bioaccumulation of ZnO nanoparticles in Schoenoplectus tabernaemontani. Chemosphere. 2014;120C:211–9.
Oksanen E, Häikiö E, Sober J, Karnosky DF. Ozone-induced H2O2 accumulation in field-grown aspen and birch is linked to foliar ultrastructure and peroxisomal activity. New Phytol. 2003;161:791–9.
Chelstowska A, Butow RA. RTG genes in yeast that function in communication between mitochondria and the nucleus are also required for expression of genes encoding peroxisomal proteins. J Biol Chem. 1995;270:18141–6.
Tan X, Lin C, Fugetsu B. Studies on toxicity of multi-walled carbon nanotubes on suspension rice cells. Carbon. 2009;47:3479–87.
Beckman KB, Ames BN. Oxidative decay of DNA. J Biol Chem. 1997;272:19633–6.
Marine A, Krager KJ, Aykin-Burns N, Macmillan-Crow LA. Peroxynitrite induced mitochondrial biogenesis following MnSOD knockdown in normal rat kidney (NRK) cells. Redox Biol. 2014;23:348–57.
Indo HP, Davidson M, Yen HC, Suenaga S, Tomita K, Nishii T, Higuchi M, Koga Y, Ozawa T, Majima HJ. Evidence of ROS generation by mitochondria in cells with impaired electron transport chain and mitochondrial DNA damage. Mitochondrion. 2007;7:106–18.
Yao N, Eisfelder BJ, Marvin J, Greenberg JT. The mitochondrion-an organelle commonly involved in programmed cell death in Arabidopsis thaliana. Plant J. 2004;40:596–610.
Petit PX. Flow cytometric analysis of rhodamine-123 fluorescence during modulation of the membrane potential in plant mitochondria. Plant Physiol. 1992;98:279–86.
Ouédraogo G, Morlière P, Santus R. Miranda Castell JV. Damage to mitochondria of cultured human skin fibroblasts photosensitized by fluoroquinolones. Photochem Photobiol. 2000;58:20–5.
Arasimowicz-Jelonek M, Floryszak-Wieczorek J, Deckert J, Rucińska-Sobkowiak R, Gzyl J, Pawlak-Sprada S, Abramowski D, Jelonek T, Gwóźdź EA. Nitric oxide implication in cadmium-induced programmed cell death in roots and signaling response of yellow lupine plants. Plant Physiol Biochem. 2012;58:124–34.
Kopyra M, Stachon-Wilk M, Gwozdz EA. Effects of exogenous nitric oxide on the antioxidant capacity of cadmium-treated soybean cell suspension. Acta Physiol Plant. 2006;28:525–36.
Zottini M, Costa A, De Michele R, Schiavo FL. Role of nitric oxide in programmed cell death. In: Hayat S, Mori M, Pichtel J, Ahmad A, editors. Nitric oxide in plant physiology. Weinheim: Wiley-VCH Verlag GmbH & Co. KGaA; 2010. p. 77–87.
Amano T, Hirsawa Ki, O’Donohue MJ, Shioi Y. A versatile assay for the accurate, time-resolved determination of cellular viability. Anal Biochem. 2003;314:1–7.
Gorokhova E, Mattsson L, Sundström AM. A comparison of TO-PRO-1 iodide and 5-CFDA-AM staining methods for assessing viability of planktonic algae with epifluorescence microscopy. J Microbiol Methods. 2012;89:216–21.
Demir E, Kaya N, Kaya B. Genotoxic effects of zinc oxide and titanium dioxide nanoparticles on root meristem cells of Allium cepa by comet assay. Turk J Biol. 2014;38:31–9.
Zhang H, Jiang Y, He Z, Ma M. Cadmium accumulation and oxidative burst in garlic (Allium sativum). J Plant Physiol. 2005;162:977–84.
Kumari M, Mukherjee A, Chandrasekaran N. Genotoxicity of silver nanoparticles in Allium cepa. Sci Total Environ. 2009;407:5243–6.
Del Pozo O, Lam E. Caspases and programmed cell death in the hypersensitive response of plants to pathogens. Curr Biol. 1998;88:1129–32.
Mlejnek P, Prochazka S. Activation of caspase-like proteases and induction of apoptosis by isopentenyladenosine in tobacco BY-2 cells. Planta. 2002;215:158–66.
Imanishi S, Momose J, Hiura I. Isolation and culture of Lycopersicon esculentum root protoplasts. Plant Tissue Cult Lett. 1985;2:25–6.
Saquib Q, Al-Khedhairy AA, Siddiqui MA, Abou-Tarboush FM, Azam A, Musarrat J. Titanium dioxide nanoparticles induced cytotoxicity, oxidative stress and DNA damage in human amnion epithelial (WISH) cells. Toxicol In Vitro. 2012;26:351–61.
Saquib Q, Musarrat J, Siddiqui MA, Dutta S, Dasgupta S, Giesy JP. Al-Khedhairy AA Cytotoxic and necrotic responses in human amniotic epithelial (WISH) cells exposed to organophosphate insecticide phorate. Mutat Res. 2012;744:125–34.
Saquib Q, Al-Khedhairy AA, Al-Arifi S, Dhawan A, Musarrat J. Assessment of methyl thiophanate-Cu (II) induced DNA damage in human lymphocytes. Toxicol In Vitro. 2009;23:848–54.
MF, QS both designed the study and drafted the manuscript. MF, QS both performed the seed germination, flow cytometric and DNA damage experiments. SMA, HAA performed the fluorescence microscopic studies. SD performed the physiochemical characterization of NPs. MA performed the TEM experiments. AAA, AAK contributed by reagents, materials, instrumentation and lab space. JM, SP analyzed the experimental data and contributed in discussion of experimental outcomes. All authors read and approved the final manuscript.
This project was funded by the National Plan for Science, Technology and Innovation (MAARIFAH), King Abdul Aziz City for Science and Technology, Kingdom of Saudi Arabia, Award Number 12-BIO2919-02.
The authors declare that they have no competing interests.
Mohammad Faisal and Quaiser Saquib contributed equally to this work