Abstract
Zinc oxide nanoparticles (ZnO NPs) are used in a wide range of applications including industry, commercial products and medicine field. Numerous mechanistic studies for ZnO NPs’ toxicity were performed on pristine (fresh) NPs. However, the cytotoxicity induced by the transformed (aged) ZnO NPs and the underlying mechanisms remain unclear. Here, we observed the physicochemical transformation of ZnO NPs underwent over time, followed by evaluating the cytotoxicity of fresh and aged NPs. We found that fresh ZnO NPs induced higher apoptosis level than their aged counterparts. Accordingly, RNA sequencing data from aged ZnO NP-treated human–hamster hybrid (AL) cells showed that p53, PI3k–Akt, FoXO, Glutathione, ErbB, HIF-1, Oxytocin and Jak-STAT signaling pathways were enriched but no apoptosis pathway. Quantitative PCR results revealed the significantly higher mRNA level of IL1B and CD69 in fresh NP-treated groups compared to that of aged ZnO NP- and zinc chloride-treated groups. The above results indicated that the lower cytotoxicity of aged ZnO NPs is partially attributed to their reduced potency in inducing apoptosis. The transcriptional regulation of multiple signal pathways activated by aged NPs may help to build the cellular homeostasis. Taken together, our findings highlight the influence of aging (environmental transformation) process of ZnO NPs on their toxicities and biological consequences.
Introduction
With the rapid development of nanotechnology over the past decades, nanoparticles (NPs) have been applied in various fields, including industry, human daily life and nanomedicine [1, 2]. The Nanotechnology Consumer Product Inventory (CPI) shows a 30-fold increase between 2005 and 2015 in the numbers of nano-products, including 762 health (fitness) products, 72 food (beverages) and 23 baby products [2]. The growing application of NPs in consumer products and various fields increased the possibility of NPs entering into the environment, which raises safety concerns with regard to their potential adverse impacts. Zinc oxide (ZnO) NPs are among the most commonly-used NPs, and its global annual output has reached nearly 3400 tons [3, 4]. Some substances that are previously considered as biologically inert could become toxic in their nanoparticulate state. An increasing number of studies elucidated that ZnO NPs may pose significant risks to mammalian cells and animals by inducing significant toxicity [5,6,7].
Various strategies including coating, surface functionalization and oxidation state modification have been used to attenuate the potential toxicity of NPs by modifying the physical and chemical properties of them (such as the dissolution, agglomeration and perturbation of cell membranes) [8,9,10,11]. Although these modifications of NPs weaken their toxic effects in certain degree, the uses of NPs are not always safe, especially under certain exposure conditions and environments [12,13,14]. Actually, many kinds of NPs are not stable and inclined to undergo “aging” or “environmental transformation” after being intentionally or unintentionally released into the natural environment [14,15,16,17]. In recent years, lots of work were carried out to explore the environmental transformation process of NPs; however, the research on the toxic effects of “transformed (aged)” NPs is still very limited, let alone their toxic mechanisms.
As the typical representative of non-persistent NPs, ZnO NPs have very high reactivity, and are prone to transform in physical and chemical properties and occurrence state after being released into the environment or ingested by animals, which could significantly affect their toxicological effects [17, 18]. For example, studies have shown that the sulfidation process of ZnO NPs changed the charge, hydrophobicity and aggregation state, resulting in the adsorption of sulfide state NPs in human saliva, sweat and bronchoalveolar lavage fluid. Furthermore, the protein adsorbed by ZnO NPs forms a special protein crown that usually affects its biological effect [19]. Phosphates in physiological solutions could convert ZnO NPs into metastable ZnHPO4 and Zn3(PO4)2within about 5–10 h [20]. The process of complete transformation of ZnO NPs (≤ 3 μg/mL) in the in vitro exposure system to human T lymphocytes (37 °C, cell culture medium RPMI1640 containing 10% FBS for 24 h) was investigated by using synchrotron radiation X-ray absorption near-edge structure spectroscopy (XANES) [21]. The above studies suggest the underestimation of ZnO NPs’ environmental and health risks by solely evaluating the biological effects of pristine (fresh) ZnO NPs. In the light of this problem, there is an urgent need to comprehensively understand the aging and environmental transformation processes of NPs [22].
Our previous study revealed that ZnO NPs aged for 40–120 days in ultrapure water undergo physicochemical transformation and turn into Zn5(CO3)2(OH)6, Zn (OH)2, and Zn2+ [23]. Interestingly, aged ZnO NPs exhibited lower cytotoxicity than the fresh counterparts [23], yet the toxicity mechanisms of such kind of variation are unclear. In the present study, we set out to explore the underlying reasons of different cytotoxicities between fresh and aged ZnO NPs. ZnO NPs with two different particle sizes (20 nm and 90–200 nm) were applied systematically. The cytotoxicity assays demonstrated that aged ZnO NPs induced less pronounced morphological abnormalities and relatively higher cell viabilities than their fresh counterparts. RNA sequencing data revealed that apoptotic genes were enriched in fresh ZnO NP-treated cells, whereas these genes were much less affected by aged ZnO NP-treatments. In addition, the cells exposed to aged ZnO NPs showed reduced level of cleaved Caspase-3 protein, further indicating the higher potency of fresh ZnO NPs in eliciting apoptosis in cultured cells. Combined with our previous findings, this study suggested that the decreased cytotoxicity of aged ZnO NPs is attributed to their attenuated ability in triggering cell apoptosis.
Materials and Methods
Nanoparticles and Reagents
The commercially available ZnO nanopowders (ZnO NPs), with manufacturer’s reported average size 20 nm (99.5% purity, nearly spherical) and 90–200 nm (99.9% purity, irregular morphology), were purchased from Nanostructured & Amorphous Materials (Houston, TX). Except for otherwise noted, all the reagents and chemicals used in this study were purchased from Sigma-Aldrich (Shanghai, China).
Nanoparticle Dispersion, Aging and Characterization
ZnO NPs stock suspensions (1 mg/mL) were prepared by suspending dry nanopowders in Milli-Q H2O (Millipore, 18 MΩ cm) and sterilized by autoclaving (120 °C, 30 min) and then stored at 25 °C for natural aging period ranging from 0 to 60 days. The 0- and 60-days’ naturally transformed ZnO NPs were designated as fresh and aged NPs, respectively. To ensure proper dispersion, the fresh and aged suspensions were sonicated (100 W) for 30 min in an ultrasonic bath before characterization or incubation with cells. The morphology, particle size and aggregation of fresh and aged ZnO NPs were characterized by using transmission electron microscopy (TEM, JEOL JEM-2010, Tokyo, Japan). The crystal structure of fresh and aged ZnO NPs was determined using power X-ray diffraction (XRD, PANalytical B. V., Shanghai, China) by comparing to authentic standards. The details of natural aging process and characterization on ZnO NPs have been described previously [23].
Cell Culture and Treatment with ZnO NPs
AL cell line, a kind of human–hamster hybrid cells formed by fusion of the gly2A mutant of Chinese hamster ovary (CHO) and human fibroblasts was used in this study. These hybrid cells contained a standard set of CHO-K1 chromosomes and a single copy of human chromosome 11 and were cultured in Ham’s F12 medium (Hyclone, Grand Island, NY) supplemented with fetal bovine serum (8%, Hyclone, Grand Island, NY), gentamicin (25 g/mL) and glycine (2 × 10–4 M) at 37 °C in a humidified 5% CO2 incubator [24]. The stock suspensions of fresh and aged ZnO NPs were dispersed by 30 min of ultrasonication (100 W) to prevent agglomeration, subsequently diluted to appropriate concentrations with cell culture media for the exposure of cells. Cells maintained in cell culture media without NPs were served as control in each experiment.
Assay for Detecting the Cytotoxicity
AL cells at a logarithmic phase of growth were cultured on glass slides in 35-mm Petri dishes (6 × 104 cells/dish) for 24 h before stimulation, followed by treatment with 2 mL of culture medium containing 1, 5, 10, 12, 15 and 20 µg/mL fresh or aged ZnO NPs 72 h. After the completion of treatment time, the images of cell morphology were obtained using a Leica DM4B microscope (Leica, Germany). ZnCl2 was included as zinc ions reference for comparing the cytotoxicity with ZnO NPs.
The cell counting kit (CCK-8) (APExBIO, Shanghai, China) was used for detecting the cell viability. In details, AL cells were seeded into 96-well plates (4 × 103 cells/well) with cell culture media for 24 h and treated with medium containing various concentrations of ZnCl2, fresh and aged ZnO NPs for 24, 48 and 72 h, respectively. For working solution, the volume of added NPs from the stock suspension was less than 5% of the total volume of the culture medium in each well. After the completion of treatment time, the culture medium was aspirated, and the cells were incubated with 100 µL CCK-8 working solution for 2 h at 37 °C following the manufacturer’s instructions. Then, the absorbance was recorded at 450 nm using a Spectra Max M2 fluorescence reader (Molecular Devices, Wokingham, Berks, UK). Cell viability was calculated as a percentage of absorbance in wells, with each concentration of NPs normalized to the absorbance of control cells (100%).
RNA Extraction, Reverse Transcription and Quantitative PCR
AL cells at a logarithmic phase of growth were seeded into 35-mm-diameter Petri dish (6 × 104 cells/dish) with cell culture media for 24 h. Then, the medium was replaced with 2 mL of culture medium containing 12 µg/mL ZnCl2, fresh and aged ZnO NPs for 72 h. After the completion of treatment time, the culture medium was aspirated, and cells were washed 3 times with PBS. Subsequently, 1 mL of Trizol reagent (Invitrogen, Carlsbad, CA, USA) was added to each dish to extract total RNA according to the manufacturer’s instructions. Concentration and purity of total RNA obtained after the extraction were quantified using a Q5000UV-Vis Spectrophotometer (Quawell, USA). After quantification, reverse transcription was performed using TransGene RT-PCR kit (TransGene Biotech, Beijing, China) to obtain cDNA from the RNA template according to the manufacturer’s protocols. The resulting cDNA samples were quantified by using the Q5000 UV–Vis Spectrophotometer and then analyzed using SYBR-Green as fluorescence dye (TransGene Biotech, Beijing, China) on Roche RT-PCR system (Applied Biosystems) [25].
The housekeeping gene encoding Glyceraldehyde-3-phosphate Dehydrogenase (Gapdh) was used as internal control for evaluatingIl-1α, Il-1β, Caspase 3, CD69, Jun and MT1 mRNA expression. The results were expressed as the relative expression ratio between the targeted gene and Gapdh. The primer sequences used in this study are provided in Table 1.
RNA Sequencing Data Analysis
The total RNA samples of AL cells from control group, aged ZnO NP-treated group and ZnCl2 treated group were sequenced by BangFei Bioscience (Beijing, China). Briefly, the total RNA of AL cells was extracted following the TRIZOL protocols, until the isoproponal precipitation. Then, the RNA samples were resuspended in the extraction buffer before sequencing. The raw count RNA sequencing data were analyzed using R package Deseq2 [Eric1]. The venn diagram was generated by R package VennDiagram [Eric1.2]. The significantly changed genes were used for further pathway enrichment analysis. Experiments were done three independent replicates. rRNA genes, mitochondrial genes and the genes detected less than 40 bp were excluded from the analysis.
The RNA sequencing data, reference series GSE97852, GSE60159 and GSE39444, were obtained from Gene Expression Omnibus [Eric 2, 3, 4]. The Gene Set Enrichment Analysis plot was generated by R (version 3.6.2) using package fgsea [Eric 5]. The apoptosis genes with 1.5-fold significant change & p value < 0.05 were used for further analysis. The heatmap with gene tree was generated by R package “ComplexHeatmap” [Eric 6]. Average linkage was used as the clustering method, and Euclidean was used as a distance measurement method. The pathway enrichment analysis was preceded using STRING2.0 [Eric 7].
Western Blotting
AL cells at a logarithmic phase of growth were seeded into 60-mm-diameter Petri dish (1.5 × 105 cells/dish) with cell culture media for 24 h. Then, the medium was replaced with 4 mL of culture medium containing 12 µg/mL fresh or aged ZnO NPs for 24 h. At the end of exposure period, the culture medium was aspirated, and then, cells were washed 3 times with PBS and lysed on ice with RIPA lysis buffer (Beyotime, China) to collect cellular proteins. Equal amounts of cellular proteins were separated on 12% SDS-PAGE gels and then transferred to a polyvinylidene fluoride (PVDF) membrane (Roche, Swiss). Briefly, after 2 h blocking with 5% nonfat milk in TBST at 25 °C, the membranes were subsequently incubated with primary antibody at appropriate dilutions (according to the manufacturer’s protocols) at 4 °C overnight, followed by incubating with HRP-conjugated secondary antibodies (1:5000, Promega, Madison, USA) for 2 h at 25 °C. Finally, immunolabeling was detected using an enhanced chemiluminescence (ECL) (BOSTER, China) solution. The primary antibodies of anti-pro/cleaved Caspase-3 and anti-Actin were purchased from Cell Signaling Technology and ImmunoWay, respectively.
Statistics
Statistical analysis was compiled on the means of the results obtained from at least three independent experiments. All Data were presented as means ± standard deviation (SD) and statistically compared using one-way analysis of variance (ANOVA). In all plots p values < 0.05 were showed as * and considered to be statistically significant.
Results
Characterization of ZnO NPs
To determine the differences in detailed physicochemical characteristics between fresh and aged ZnO NPs, we first observed the morphology of NPs using TEM (Fig. 1A). Our results indicated that 20 nm fresh ZnO NPs were nearly spherical crystals and 90–200 nm fresh ZnO NPs were irregularly rod-like/cubical crystals. The single particle size was consistent with the size provided by the manufacturer. Obviously, both 20 nm and 90–200 nm ZnO NPs were inclined to aggregate in ultrapure water. Also, regardless of the shape and size of the original NPs, both 20 nm and 90–200 nm ZnO NPs’ microstructure was dramatically changed from a clear crystal structure to an amorphous or sheet-/needle-like state after aged for 60 days. Furthermore, the crystalline nature and phase purity of both fresh and aged NPs were determined by using X-ray diffraction (XRD) with Cu Kα radiation (λ = 0.15418 nm) approach at 25 °C, as shown in Fig. 1B. The XRD pattern of fresh ZnO NPs indicated that the samples were comprised of crystalline wurtzite structure and no characteristic impurity peaks were identified, suggesting a high quality of fresh NPs. For aged NPs, the XRD pattern exhibited the neoformation of Zn5(CO3)2(OH)6 (card number 00-011-0287) and Zn (OH)2 (card number 00-003-0888) solid phases, indicating the chemical transformation of ZnO NPs (20 and 90–200 nm) during the aging process.
Morphological Observation of A L Cells Exposed to Fresh and Aged ZnO NPs
NPs’ treatment results in a noticeable change in cellular shape, or morphology, in vitro [26]. Therefore, AL cells exposed to fresh or aged ZnO NPs at 10 & 15 µg/mL for 72 h were examined under a stereoscopic microscope. As shown in Fig. 2, cell morphology in the control group remained normal. The cells adhered well, with most attaching within 2 h. Most cells were spindle shaped or polygonal, with a few newly dividing cells showing a more transparent cytoplasm and better dispersion during the process of adhering. Treatment with 12 μg/mL fresh ZnO NPs (20 nm & 90–200 nm) for 72 h significantly changed cell morphology. Although most cells adhered within 3–5 h, they could not spread well, and some cells became rounded and lost the polygonal shape. When the concentration of ZnO NPs was increased to 15 μg/mL, the treated cells atrophied and could not adhere, suggesting their significantly lower cell viability than that of the cells treated with 10 μg/mL. These results indicated that the LC100 for fresh ZnO NPs is probably less than 15 μg/mL by a 72-h treatment. In contrast, cell morphology in 20 nm and 90–200 nm aged NP-treated groups (15 μg/mL) was not significantly affected, and most of the surviving cells could adhere and spread, with less than half dead cells observed, unveiling that aged ZnO NPs are much lower cytotoxic than fresh ZnO NPs.
Aged ZnO NPs Induced Lower Cytotoxicity than Fresh NPs
To further investigate the difference in cytotoxicity between fresh and aged ZnO NPs, we examined the cell viability by using CCK-8 kits. As shown in Fig. 3, incubation AL cells with gradient doses of fresh and aged ZnO NPs (ranging from 0 to 20 μg/mL, 20 nm and 90–200 nm) for 24 h, 48 h or 72 h showed a dose-dependent decrease in cell viability. No obvious cytotoxicity was observed by treating cells with ZnO NPs ≤ 10 μg/mL. When the dosage of fresh and aged ZnO NPs elevated to 12 and 15 μg/mL, the cell viability showed a time-dependent decrease tendency. Obviously, the cell viability in aged NP-treated groups was significantly higher than fresh NP-treated groups. In addition, ZnCl2-treatment also compromised cell viability in a dose- and time-dependent manner, whereas the cytotoxicity of ZnCl2 was much less than that of both fresh and aged ZnO NPs.
Fresh ZnO NPs’ Treatment Activated Apoptosis Pathways and Up-Regulated the Expression of Apoptotic Genes
To unveil the underlying mechanisms leading to the lower cytotoxicity of aged NPs, we analyzed RNA sequencing data from both fresh and aged ZnO NPs. As shown in Fig. 4A, B, after treatment with fresh ZnO NPs, apoptosis pathway was activated in Jurkat cells (p = 0.017) and HMDM cells (p = 0.041). The apoptosis genes: ANXA1, CYLD, TNFSF10, IER3, CDKN1A, JUN, SAT1, PMAIP1, CD38 and ISG20 were significantly enriched in fresh ZnO NP-treated Jurkat cells. The apoptosis genes: CD38, TNFRSF12A, CCNA1, BMP2, PPP2R5B, EREG, IFNGR1, CD44, CD14, GNA15, GCH1, TIMP1, BTG2, IL1B, IL1A, BTG3, BCL2L11, SC5D and SPTAN1 were significantly enriched in fresh ZnO NP-treated HMDM cells (Fig. 4C, D). Since Jurket cells (peripheral blood T lymphocyte cells) and HMDM cells (human monocyte-derived macrophages) are different kinds of cells, the way they trigger apoptosis might be different. In sum, these results showed that fresh ZnO NPs’ exposure could activate different apoptosis pathways in various kinds of cells.
Aged ZnO NPs Did Not Up-Regulate the Expression of Apoptotic Genes as Fresh ZnO NPs
Our RNA sequencing data from aged ZnO NP-treated AL cells showed that p53, PI3k–Akt, FoXO, Glutathione, ErbB, HIF-1, Oxytocin and Jak-STAT signaling pathway were enriched (Fig. 5A). The apoptosis genes enriched in Jurket and HMDM cells were not significantly affected in the aged ZnO NP-treated cells (Fig. 5B). To further confirm the findings, we tested the expression of related genes by real time PCR. We found that some of the apoptosis genes: BMP2, PMAIP1, IL1α, CD69, CCNA1, CD38 and IL1β were undetectable in aged ZnO NPs-treated AL cells (data not shown), probably because most of these genes are expressed in immune system cells. The other up-regulated apoptosis genes (IL1α, IL1β and CD59) observed in fresh ZnO NP-treated groups were not significantly changed in expression levels by aged ZnO NPs’ treatment. While the MT1 that serve as a positive control was significantly increased in an expression level, the expression of Caspase 3 was not significantly changed (Fig. 5C). These data suggested that aged ZnO NPs, unlike their fresh counterparts, are less potent in activating apoptosis pathway genes in AL cells.
Fresh But Not Aged ZnO NPs Increased the Expression Level of the Activated Caspase 3 Protein
Detection of gene expression of Caspase 3 alone cannot directly indicate the activation of apoptosis pathway. To further analysis whether ZnO NPs’ treatment could change apoptotic proteins’ level, the expression of cleaved Caspase 3 protein, a commonly used biomarker to indicate the activation of cell apoptosis [27], was examined by Western blotting analysis. As shown in Fig. 6, compared to the control group, fresh ZnO NPs (20 nm) treatment increased the cellular level of cleaved Caspase 3 protein by 1.31 ± 0.023-fold, which was significantly higher than that of aged 20 nm ZnO NPs-treated group (1.12 ± 0.039-fold). When the particle size of fresh ZnO NPs was increased to 90–200 nm, the expression of cleaved Caspase 3 protein induced by fresh NPs was increased by 1.46 ± 0.078-fold, significantly greater than that of aged NPs (1.07 ± 0.075-fold). These data further illustrated the higher potency of fresh ZnO NPs in inducing cell apoptosis, in comparison with their aged counterparts.
Discussion
ZnO NPs were reported to undergo physicochemical transformation into Zn5(CO3)2(OH)6 with the release of Zn2+ during the natural aging process [23, 28]. However, the cytotoxicity induced by the transformed (aged) ZnO NPs and the underlying mechanisms remain unclear. Here, to unveil the mechanism of diverse cytotoxicity between fresh and aged ZnO NPs, RNA sequencing analysis and RT-PCR test were conducted. Also, Western blotting was applied to examine the protein level of Caspase 3, the key executor in cell apoptosis.
Our data showed that aged ZnO NPs induced much less cytotoxicity than fresh ZnO NPs in AL cells. The LC100 of both fresh ZnO NPs (90–200 nm and 20 nm) in our present study was lower than 15 μg/mL (Fig. 3), which was consistent with previous findings that the LC100 of ZnO NPs with 19–36 nm to NIH-3T3 or MSTO cell is about 15 μg/mL [29]. We confirmed that the environmental transformations of physicochemical properties in NPs can dramatically alter their toxicity. It has been reported that the sulfidation process of ZnO NPs changes their charge, hydrophobicity and aggregation state, resulting in the adsorption of sulfide state NPs in human saliva, sweat and bronchoalveolar lavage fluid. And the protein adsorbed by ZnO NPs formed a special protein crown, which affected its biological effect [19]. Phosphates widely present in physiological solutions (such as saliva) could convert ZnO NPs into metastable ZnHPO4 and Zn3(PO4)2 within about 5–10 h and showed cytotoxicity to digestive tract epithelial cells [20]. Ivask et al. proved the occurrence of complete transformation of ZnO NPs (≤ 3 μg/mL) in the in vitro exposure system to human T lymphocytes (37 °C, cell culture medium RPMI1640 containing 10% FBS for 24 h) using synchrotron radiation X-ray absorption near-edge structure spectroscopy (XANES). The spectrum and cytotoxicity of the transformation products were consistent with those of ZnSO4 [21]. Our results revealed the dose- and time-dependent toxicity of ZnCl2 to AL cells, where its cytotoxicity is much lower than both fresh and aged ZnO NPs (Fig. 3). The observation further explains the finding that the cytotoxicity of fresh ZnO NP is not fully attributed to its released Zn2+ [30].
Our previous study also showed that aged ZnO NPs exhibit a higher potency in eliciting ROS (reactive oxygen species), as well as an attenuated ability in killing cells compared to fresh ZnO NPs [23]. We reason that the lower cytotoxicity induced by aged ZnO NPs could be more tolerable in mammalian cells. The present study of RNA sequencing data illustrated that apoptotic genes have been up-regulated in fresh ZnO NP-treated cells, where they were much less affected in aged NP-treated groups. IL1α and IL1β are members of the interleukin 1 cytokine family. The release of IL1α and IL1β activates Caspase 8 partially dependent apoptosis [31]. CD69 encodes a member of the calcium-dependent lectin superfamily of type II transmembrane receptors. Increased CD69 expression was associated with an increased expression of the apoptosis annexin V and CD95 (Fas) marker [32]. JUN is an AP-1 transcription factor subunit. Increased JUN activity proteolytically cleavages alpha-fodrin, a substrate of the interleukin 1beta-converting enzyme (ICE), and CED-3 family of cysteine proteases, which further causes programmed cell death [33]. The increased expression of these apoptotic genes revealed that fresh NPs trigger apoptosis in several different ways. After the elevation of these apoptotic gene expressions, apoptosis processes are eventually executed by apoptotic proteins (Fig. 7). Caspase 3 is the core protease for various apoptotic scenarios; cleavage of this protein is necessary to activate both extrinsic and intrinsic apoptotic pathways [34, 35]. Therefore, detection of cleaved caspase 3 is a common method for identifying apoptosis induced by a wide variety of apoptotic signals [36]. Our Western blotting data revealed that, for both 20 nm and 90–200 nm ZnO NPs, sublethal exposure did not alter the level of Pro caspase 3 in all treatment groups. In contrast, cleaved Caspase 3 was significantly elevated by fresh NPs treatment, where aged NPs showed few (if any) effects on the level of cleaved caspase 3 (Fig. 6). Combined with RNA expression analysis, our results clearly elucidated the higher potency of fresh ZnO NPs in inducing cell apoptosis.
Conclusions
In the present study, the natural physicochemical transformation of ZnO NPs in ultrapure water was confirmed, and variations in cytotoxicity induced by fresh & aged NPs were investigated. We focused on RNA sequencing data from our aged ZnO NP-treated AL cells and that of fresh NPs from database. We compared those signaling pathway specifically enriched in aged NP-treated group, which are different from that of fresh NP- or ZnCl2-treated groups. Our data indicated that the lower cytotoxicity of aged ZnO NPs is closely related to its attenuated ability in inducing apoptosis, while the transcriptional regulation of the multiple pathways activated by NPs promotes the establishment of cellular homeostasis in mammalian cells.
Availability of data and materials
Not applicable.
Abbreviations
- NPs:
-
Nanopowders
- ZnO:
-
Zinc oxide
- Zn5(CO3)2(OH)6 :
-
Hydrozincite
- Zn (OH)2 :
-
Zinc hydroxide
- ZnCl2 :
-
Zinc chloride
- ZnSO4 :
-
Zinc sulfide
- ZnHPO4 :
-
Zinc hydrogen phosphate
- Zn3(PO4)2 :
-
Zinc phosphate
- A L cells:
-
Human–hamster hybrid cells
- CHO cells:
-
Chinese hamster ovary cells
- Jurket cells:
-
Peripheral blood T lymphocyte cells
- HMDM cells:
-
Human monocyte-derived macrophages
- NIH-3T3cells:
-
Mouse embryonic cells
- MSTO cells:
-
Human lung cancer cells
- RPMI1640:
-
Roswell Park Memorial Institute 1640
- ICE:
-
Interleukin 1beta-converting enzyme
- CED-3:
-
Caenorhabditis elegans death gene
- IL1α:
-
Interleukin 1alpha
- IL1β:
-
Interleukin 1beta
- mRNA:
-
Messenger ribonucleic acid
- cDNA:
-
Complementary deoxyribonucleic acid
- FBS:
-
Fetal bovine serum
- TEM:
-
Transmission electron microscopy
- XRD:
-
X-ray diffraction
- RT-PCR:
-
Real-time polymerase chain reaction
- CPI:
-
The Nanotechnology Consumer Product Inventory
- XANES:
-
Synchrotron radiation X-ray absorption near-edge structure spectroscopy
- RIPA:
-
Radio immunoprecipitation assay
- SDS-PAGE:
-
Polyacrylamide gel electrophoresis
- PVDF:
-
Polyvinylidene fluoride
- ECL:
-
Enhanced chemiluminescence
- CCK-8:
-
Cell counting kit-8
References
Sohail MI, Waris AA, Ayub MA, Usman M, Rehman MZ, Sabir M, Faiz T (2019) Environmental application of nanomaterials: a promise to sustainable future. Compr Anal Chem 87:1–54. https://doi.org/10.1016/bs.coac.2019.10.002
Vance ME, Kuiken T, Vejerano EP, McGinnis SP, Hochella MF, Rejeski D, Hull MS (2015) Nanotechnology in the real world: redeveloping the nanomaterial consumer products inventory. Beilstein J Nanotechnol 6:1769–1780. https://doi.org/10.3762/bjnano.6.181
RajeshKumar S, Lakshmi T, Naik P (2019) Recent advances and biomedical applications of zinc oxide nanoparticles. In: Green synthesis, characterization and applications of nanoparticles. Elsevier, Amsterdam, pp 445–457
Keller AA, Lazareva A (2015) Predicted releases of engineered nanomaterials: from global to regional to local. Environ Sci Technol Lett 1:65–70. https://doi.org/10.1021/ez400106t
George S, Pokhrel S, Xia T, Gilbert B, Ji ZX, Schowalter M, Rosenauer A, Damoiseaux R, Bradley KA, Madler L, Nel AE (2010) Use of a rapid cytotoxicity screening approach to engineer a safer zinc oxide nanoparticle through iron doping. ACS Nano 4(1):15–29. https://doi.org/10.1021/nn901503q
Naatz H, Lin SJ, Li RB, Jiang W, Ji ZX, Chang CH, Koser J, Thoming J, Xia T, Nel AE, Mädler L, Pokhrel S (2017) Safe-by-Design CuO nanoparticles via Fe-doping, Cu–O bond length variation, and biological assessment in cells and zebrafish embryos. ACS Nano 11(1):501–515. https://doi.org/10.1021/acsnano.6b06495
Xia T, Kovochich M, Liong M, Mädler L, Gilbert B, Shi H, Yeh JI, Zink JI, Nel AE (2008) Comparison of the mechanism of toxicity of zinc oxide and cerium oxide nanoparticles based on dissolution and oxidative stress properties. ACS Nano 2(10):2121–2134. https://doi.org/10.1021/nn800511k
Balati A, Wagle D, Nash KL, Shipley HJ (2018) Heterojunction of TiO2 nanoparticle embedded into ZSM5 to 2D and 3D layered-structures of MoS2 nanosheets fabricated by pulsed laser ablation and microwave technique in deionized water: structurally enhanced photocatalytic performance. Appl Nanosci. https://doi.org/10.1007/s13204-018-0902-x
Balati A, Tek S, Nash K, Shipley H (2019) Nanoarchitecture of TiO2 microspheres with expanded lattice interlayers and its heterojunction to the laser modified black TiO2 using pulsed laser ablation in liquid with improved photocatalytic performance under visible light irradiation. J Colloid Interface Sci 541:234–248. https://doi.org/10.1016/j.jcis.2019.01.082
Balati A, Bazilio A, Shahriar A, Nash K, Shipley HJ (2019) Simultaneous formation of ultra-thin MoSe2 nanosheets, inorganic fullerene-like MoSe2 and MoO3 quantum dots using fast and ecofriendly pulsed laser ablation in liquid followed by microwave treatment. Mater Sci Semicond Process 99:68–77. https://doi.org/10.1016/j.mssp.2019.04.017
Balati A, Matta A, Nash K, Shipley HJ (2020) Heterojunction of vertically aligned MoS2 layers to hydrogenated black TiO2 and rutile based inorganic hollow microspheres for the highly enhanced visible light arsenic photooxidation. Compos B Eng 185:107785. https://doi.org/10.1016/j.compositesb.2020.107785
Hwang R, Mirshafiee V, Zhu YF, Xia T (2018) Current approaches for safer design of engineered nanomaterials. Ecotoxicol Environ Saf 166:294–300. https://doi.org/10.1016/j.ecoenv.2018.09.077
Bundschuh M, Filser J, Lüderwald S, McKee MS, Metreveli G, Schaumann GE, Schulz R, Wagner S (2018) Nanoparticles in the environment: where do we come from, where do we go to? Environ Sci Eur 30(1):6. https://doi.org/10.1186/s12302-018-0132-6
Mortimer M, Holden PA (2019) Fate of engineered nanomaterials in natural environments and impacts on ecosystems. Expo Eng Nanomater Environ. https://doi.org/10.1016/B978-0-12-814835-8.00003-0
Mitrano DM, Nowack B (2017) The need for a life-cycle based aging paradigm for nanomaterials: importance of real-world test systems to identify realistic particle transformation. Nanotechnology 28(7):072001. https://doi.org/10.1088/1361-6528/28/7/072001
Mitrano DM, Motellier S, Clavaguera S, Nowack B (2015) Review of nanomaterial aging and transformations through the life cycle of nano-enhanced products. Environ Int 77:132–147. https://doi.org/10.1016/j.envint.2015.01.013
Zhang J, Guo WL, Li QQ, Wang Z, Liu SJ (2018) The effects and the potential mechanism of environmental transformation of metal nanoparticles on their toxicity in organisms. Environ Sci Nano 5(11):2482–2499. https://doi.org/10.1039/c8en00688a
Odza N, Kistler D, Sigg L (2017) Influence of daylight on the fate of silver and zinc oxide nanoparticles in natural aquatic environments. Environ Pollut 226:1–11. https://doi.org/10.1016/j.envpol.2017.04.006
Du TT, Shi GL, Liu FF, Zhang T, Chen W (2019) Sulfidation of Ag and ZnO nanomaterials significantly affects protein corona composition: implications for human exposure to environmentally aged nanomaterials. Environ Sci Technol 53(24):14296–14307. https://doi.org/10.1021/acs.est.9b04332
David CA, Galceran J, Quattrini F, Puy J, Rey-Castro C (2019) Dissolution and phosphate-induced transformation of ZnO nanoparticles in synthetic saliva probed by AGNES without previous solid-liquid separation. Comparison with UF-ICP-MS. Environ Sci Technol 53(7):3823–3831. https://doi.org/10.1021/acs.est.8b06531
Ivask A, Scheckel KG, Kapruwan P, Stone V, Yin H, Voelcker NH, Lombi E (2017) Complete transformation of ZnO and CuO nanoparticles in culture medium and lymphocyte cells during toxicity testing. Nanotoxicology 11(2):150–156. https://doi.org/10.1080/17435390.2017.1282049
Nowack B, Ranville JF, Diamond S, Gallego-Urrea JA, Metcalfe C, Rose J, Horne N, Koelmans AA, Klaine SJ (2012) Potential scenarios for nanomaterial release and subsequent alteration in the environment. Environ Toxicol Chem 31(1):50–59. https://doi.org/10.1002/etc.726
Wang MM, Wang YC, Wang XN, Liu Y, Zhang H, Zhang JW, Huang Q, Chen SP, Hei TK, Wu LJ, Xu A (2015) Mutagenicity of ZnO nanoparticles in mammalian cells: role of physicochemical transformations under the aging process. Nanotoxicology 9:972. https://doi.org/10.3109/17435390.2014.992816
Wang J, Wang JJ, Liu Y, Nie YG, Si B, Wang T, Zhao GP, Wang MM, Xu A (2019) Aging-independent and size-dependent genotoxic response induced by titanium dioxide nanoparticles in mammalian cells. J Environ Sci 85:94–106. https://doi.org/10.1016/j.jes.2019.04.024
Liu L, Sun QQ, Xu H, Yu XJ, Chen WT, Wei HQ, Jiang J, Xu YZ, Lu WJ (2020) Hyperuricemia induces lipid disturbances mediated by LPCAT3 upregulation in the liver. FASEB J 34(10):13474–13493. https://doi.org/10.1096/fj.202000950R
Song YJ, Guan RF, Lyu F, Kang TS, Wu YH, Chen XQ (2014) In vitro cytotoxicity of silver nanoparticles and zinc oxide nanoparticles to human epithelial colorectal adenocarcinoma (Caco-2) cells. Mutat Res Fund Mol Mech Mutagen 769:113–118. https://doi.org/10.1016/j.mrfmmm.2014.08.001
Budihardjo I, Oliver H, Lutter M, Luo X, Wang XD (1999) Biochemical pathways of caspase activation during apoptosis. Annu Rev Cell Dev Biol 15:269–290. https://doi.org/10.1146/annurev.cellbio.15.1.269
Zhang H, Huang Q, Xu A, Wu LJ (2016) Spectroscopic probe to contribution of physicochemical transformations in the toxicity of aged ZnO NPs to Chlorella vulgaris: new insight into the variation of toxicity of ZnO NPs under aging process. Nanotoxicology 10(8):1177–1187. https://doi.org/10.1080/17435390.2016.1196252
Brunner TJ, Wick P, Manser P, Spohn P, Grass RN, Limbach LK, Bruinink A, Stark WJ (2006) In vitro cytotoxicity of oxide nanoparticles: comparison toasbestos, silica, and the effect of particle solubility. Environ Sci Technol 40:4374–4381. https://doi.org/10.1021/es052069i
Raghupati KR, Koodaali RT, Manna AC (2011) Size dependent bacterial growth inhibition and mechanism of antibacterial activity of zinc oxide nanoparticles. Langmuir 27:4020–4028. https://doi.org/10.1021/la104825u
England H, Summersgill H, Edye M, Rothwell N, Brough D (2014) Release of interleukin-1α or interleukin-1β depends on mechanism of cell death. J Biol Chem 289:15942–15950. https://doi.org/10.1074/jbc.M114.557561
Meier P, Dayer E, Blanc E, Wauters JP (2002) Early T cell activation correlates with expression of apoptosis markers in patients with end-stage renal disease. J Am Soc Nephrol 13(1):204–212. https://doi.org/10.1053/jren.2002.31185
Bossy-Wetzel E, Bakiri L, Yaniv M (1997) Induction of apoptosis by the transcription factor c-Jun. EMBO J 16(7):1695–1709. https://doi.org/10.1093/emboj/16.7.1695
Elmore S (2007) Apoptosis: a review of programmed cell death. Toxicol Pathol 35(4):495–516. https://doi.org/10.1080/01926230701320337
Shalini S, Dorstyn L, Dawar S, Kumar S (2015) Old, new and emerging functions of caspases. Cell Death Differ 22(4):526–539. https://doi.org/10.1038/cdd.2014.216
Choudhary GS, Al-Harbi S, Almasan A (2015) Caspase-3 activation is a critical determinant of genotoxic stress-induced apoptosis. Methods Mol Biol 1219:1–9. https://doi.org/10.1007/978-1-4939-1661-0_1
Acknowledgements
The authors thank attending physician Guangtao Luo for his support in this work.
Funding
This work was supported in part by grants from National Natural Science Foundation of China (22006149, 21507002, 21677147), Anhui Provincial Natural Science Foundation (2008085MB49), “Hundred Talents Program” of the Chinese Academy of Sciences (E09BR22), Open Project Fund of the Key Laboratory of the Ministry of Education for the Birth Population (JKZD20202) and National undergraduate innovation and entrepreneurship training program (202010366043).
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JW, LW, NY, XYW and MMW performed the experiments. MMW, HD, JW, LW, ML, CH, MQ, SW, TZH and NY drafted the manuscript. MMW and HD reviewed the manuscript. All authors read and approved the final manuscript.
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Wang, J., Wang, L., Zhao, W. et al. The Role of Apoptosis Pathway in the Cytotoxicity Induced by Fresh and Aged Zinc Oxide Nanoparticles. Nanoscale Res Lett 16, 129 (2021). https://doi.org/10.1186/s11671-021-03587-y
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DOI: https://doi.org/10.1186/s11671-021-03587-y