Journal Pre-proofs Review Mitochondrial toxicity of nanomaterials Daming Wu, Ying Ma, Yuna Cao, Ting Zhang PII: DOI: Reference:
S0048-9697(19)34986-1 https://doi.org/10.1016/j.scitotenv.2019.134994 STOTEN 134994
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Science of the Total Environment
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2 September 2019 11 October 2019 14 October 2019
Please cite this article as: D. Wu, Y. Ma, Y. Cao, T. Zhang, Mitochondrial toxicity of nanomaterials, Science of the Total Environment (2019), doi: https://doi.org/10.1016/j.scitotenv.2019.134994
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Mitochondrial toxicity of nanomaterials Daming Wu, Ying Ma, Yuna Cao, Ting Zhang*
Key Laboratory of Environmental Medicine Engineering, Ministry of Education, School of Public Health, Southeast University, Nanjing, 210009, China.
*Corresponding
author. Email address:
[email protected]
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Abstract In recent years, nanomaterials have been widely applied in electronics, food, biomedicine and other fields, resulting in increased human exposure and consequent research focus on their biological and toxic effects. Mitochondria, the main target organelle for nanomaterials (NM), play a critical role in their toxic activities. Several studies to date have shown that nanomaterials cause alterations in mitochondrial morphology, mitochondrial membrane potential, opening of the mitochondrial permeability transition pore (MPTP) and mitochondrial respiratory function, and promote cytochrome C release. An earlier mitochondrial toxicity study of NMs additionally reported induction of mitochondrial dynamic changes. Here, we have reviewed the mitochondrial toxicity of NMs and provided a scientific basis for the contribution of mitochondria to the toxicological effects of different NMs along with approaches to reduce mitochondrial and, consequently, overall toxicity of NMs.
Keywords: Nanomaterials; Mitochondria; Mitochondrial toxicity; Mitochondrial dynamic; Mitochondrial homeostasis
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1 Introduction With the rapid development of nanotechnology and its widespread application in multiple fields, such as electronics (Jariwala et al., 2013; Kim et al., 2014), food (Handford et al., 2014), cosmetics (Cao et al., 2016), agriculture (Handford et al., 2014), and biomedicine (Teradal and Jelinek, 2017), the commercial demand for nanomaterials (NM) has increased dramatically (Vance et al., 2015; Lai et al., 2018). Owing to their expanding use, NMs are inevitably released into the environment or directly absorbed by the body (Lead et al., 2018). Every step in the production, processing, transportation, application and disposal of NMs may lead to release into the ambient atmosphere (Caballero-Guzman and Nowack, 2016). In addition, high concentrations of NMs can be released during accidents, such as explosions, fires or transportation collisions (John et al., 2017). The respiratory tract is the main route for NM entry into the human body. NMs also enter aquatic systems and soils through application to agriculture and industrial discharge (Rai et al., 2018), where the majority are aggregated and transformed by colloids, particles and organisms in water and soil (Batley et al., 2013; Lead et al., 2018). The extensive use of NMs in pharmaceuticals, cosmetics, textiles, food and tableware has led to direct contact with human skin and entry into the body through the gastrointestinal tract and intravenous injection (Blaser et al., 2008; Handford et al., 2014; Cao et al., 2016; Rathor et al., 2017). NMs in the body penetrate cells via free diffusion, phagocytosis and pinocytosis (Karlsson et al., 2009), exerting diverse biological effects that cause potential harm to health. Accordingly, determination of the 3
biological effects and safety of NMs, in particular, their interactions with subcellular structures, is essential (Service, 2003). Mitochondria are key organelles involved in numerous biological processes. In addition to their function as an “energy plant”, mitochondria are involved in the initiation of apoptosis (Raimundo et al., 2012), calcium signaling and homeostasis (Marchi et al., 2018), biomacromolecule synthesis (Ahn and Metallo, 2015), ion exchange (Shoshan-Barmatz et al., 2015) and metabolite transport (Ellenrieder et al., 2017). Numerous environmental contaminants exert toxic effects by inducing mitochondrial impairment, including dioxins (Hwang et al., 2016), acrylamide (Zamani et al., 2017), cigarette smoke (He et al., 2017), and heavy metals (Belyaeva et al., 2012). Mitochondrial damage also occurs in human diseases including common aging disorders, such as Parkinson's disease, Alzheimer's disease and cancer (Wallace, 2005), as well as liver disease (Nassir and Ibdah, 2014; Simoes et al., 2018), muscle disease (Russell et al., 2014; Zulian et al., 2016) and heart disease (Santiago et al., 2015). Therefore, mitochondria are suggested to play a key role in diseases caused by environmental pollutants. NMs clearly cause damage to mitochondria (Yu et al., 2013; Maurer and Meyer, 2016; Xue et al., 2017), inducing morphological changes (Nguyen et al., 2015), mitochondrial membrane potential (MMP) decrease (Huerta-Garcia et al., 2014), suppression of mitochondrial respiratory function (Yu et al., 2015) and promotion of cytochrome C release (Jaworski et al., 2019). These toxic effects ultimately lead to decreased ATP production and apoptosis. Changes in mitochondrial dynamics (Yamada et al., 2018) and mitophagy (Wang et al., 2018a) were 4
simultaneously reported from toxicity studies of NMs, which play an important role in the occurrence and development of neurodegenerative diseases, cancer and metabolic disorders (Bertholet et al., 2016; Serasinghe and Chipuk, 2017; Srinivasan et al., 2017; Um and Yun, 2017). This review aids in improving understanding of the biosafety of NMs by highlighting the mitochondrial toxicity of common nanomaterials and provides a reference for subsequent evaluation of mitochondrial contribution to the toxicological effects of different NMs.
2 Structure and function of mitochondria The structure and functions of mitochondria, important sites for cell energy metabolism, are depicted in Fig.1. The organelle can be divided into four functional regions from the inside to outside: matrix, mitochondrial inner membrane (MIM), intermembrane space and mitochondrial outer membrane (MOM). The mitochondrial permeability transition pore (MPTP) is composed of transmembrane proteins on MIM and MOM (Tsujimoto and Shimizu, 2007). The main physiological role of MPTP is regulation of intracellular calcium homeostasis (Hurst et al., 2017), transport of ATP/ADP and energy metabolism (Mnatsakanyan et al., 2017). Continuous opening of MPTP can lead to collapse of transmembrane potential, oxidative phosphorylation uncoupling and release of cytochrome C (Mashayekhi et al., 2014; Mnatsakanyan et al., 2017). MIM folds inwards to form mitochondrial cristae. Most respiratory complexes responsible for oxidative phosphorylation and ATP production are embedded in cristae (Quintana-Cabrera et al., 2018). The shape of mitochondrial cristae 5
determines mitochondrial respiratory complex assembly and efficiency of energy metabolism (Cogliati et al., 2013; Cogliati et al., 2016). ROS (Sarniak et al., 2016) and MMP (Brand and Nicholls, 2011) are generated during electron transport in the respiratory chain in which complexes I and III are the main sources of mitochondrial ROS (mtROS) (Bleier and Drose, 2013; Vinogradov and Grivennikova, 2016; Basit et al., 2017), which may be involved in organism development (Coffman et al., 2009), immune processes (Pinegin et al., 2018) and signal transduction (Scialo et al., 2017). Excess ROS can be eliminated by antioxidants or antioxidant enzymes in cells (Larosa and Remacle, 2018). Normal MMP is a prerequisite for maintaining oxidative phosphorylation and ATP production (Chen, 1988). When the respiratory chain complex is affected by exogenous factors, excessive production of mtROS, altered MMP and decreased ATP production may be triggered (Zhou and Huang, 2018). Mitochondrial DNA (mtDNA) and ribosomes in the mitochondrial matrix encode ~13 proteins that primarily form enzyme complexes of the oxidative phosphorylation system (Friedman and Nunnari, 2014; Mazunin et al., 2015). MtDNA is transcribed at high rates in some high-energy active tissues, such as heart (Mercer et al., 2011).
3 Role of mitochondria in NM-induced toxicity ROS generation is one of the important mechanisms underlying nanoparticleinduced toxicity (Abdal Dayem et al., 2017; Jayaram et al., 2017). On the one hand, NMs themselves produce ROS, causing damage to mitochondria, in turn, triggering a series of mitochondria-mediated toxic effects (Abdal Dayem et al., 2017). On the other 6
hand, decreased levels or activities of mitochondrial respiratory chain complexes lead to overproduction of ROS (Sun et al., 2016; Passmore et al., 2017; Zhang et al., 2018a). NMs may directly trigger overproduction of mitochondrial ROS by affecting the expression or activity of the respiratory chain complex. A study by Nguyen et al. (2015) on the effects of cadmium telluride quantum dots (CdTe QDs) on mitochondria of human hepatocellular carcinoma cells (HepG2) consistently disclosed that CdTe QDs suppress the activities of electron transport chain complexes II, III and IV. Costa and co-workers (2010) reported the that silver nanoparticles (Ag-NPs; 10, 25 and 50 mg/L) suppress the activities of mitochondrial respiratory chain complexes I, II, III and IV in rat brain, skeletal muscle, heart and liver. The role of the mitochondrial respiratory chain in ROS generation and cytotoxicity in keratinocyte cells induced by nano-TiO2 under UVA irradiation was examined by Xue et al. (2016a). In this study, complexes I and III were determined as the major sites of ROS generation and mitochondrial respiratory chain as the main source of intracellular ROS induced by nano-TiO2. In addition, damage to mtDNA further leading to decreased expression of respiratory chain complexes has been reported in a recent toxicity study of multi-walled carbon nanotubes (MWCNT) (Xu et al., 2016). The collective findings support the theory that NMs trigger increased mtROS levels by affecting respiratory chain complexes and promote oxidative stress (Song et al., 2016; Tee et al., 2016). Upon exposure to environmental stress (such as elevated ROS levels), cells regulate mitochondrial dynamics and mitophagy to control mitochondrial quality and maintain homeostasis (Youle and van der Bliek, 2012; Ni et al., 2015; Vigie and 7
Camougrand, 2017; Palikaras et al., 2018). Changes in mitochondrial dynamics have been detected in nanomaterial-induced toxicity. Mitochondria show a high degree of fusion at low doses and high degree of fragmentation at high doses (Wilson et al., 2015). Mitochondrial fusion may serve as an adaptive response (Meyer et al., 2017). Proper mitochondrial fission protects healthy regions from being eliminated (Burman et al., 2017) and promotes clearance of damaged regions via mitophagy. Wei et al. (2017) showed a protective role of PINK1/parkin-mediated mitophagy against cytotoxicity induced by ZnO-NPs. Mitochondria play critical role in intrinsic apoptosis (Galluzzi et al., 2018). Mitochondria-mediated apoptosis is associated with the toxicological effects of most nanomaterials. Recent experiments on the effects of Ag-NPs on SH-SY5Y cells by Li et al. (2018) demonstrated that Ag-NPs increase the length of endoplasmic reticulummitochondrial contact sites, enhance transfer of Ca2+ from the endoplasmic reticulum to mitochondria, cause Ca2+ overload and disrupt homeostasis in mitochondriatriggered apoptosis. The group of Zhao (2016) demonstrated that ZnO-NPs cause reduction of the Bcl-2/Bax ratio and release of cytochrome C into the cytosol, and ultimately, mitochondria-mediated apoptosis in zebrafish embryos. Induction of mitochondria-mediated apoptosis by single-walled carbon nanotubes (SWCNTs), multi-walled carbon nanotubes (MWCNTs) and Fe2O3 NPs in melanoma cells was further documented by Naserzadeh et al. (2018). In summary, mitochondria act as targets and mediators of the toxic effects of NMs. An overview of mitochondrial toxicity by NMs is shown in Figure 2. 8
4 Different types of nanomaterials inducing mitochondrial toxicity According to composition and application, we have divided nanomaterial subtypes into metal and metal oxides (MNM), metal-free carbon (CNM) and quantum dots (QD). This article mainly focuses on the mitochondrial toxicity of these three NM types (presented in Tables 1, 2 and 3). 4.1 Metal and metal oxide nanomaterials The latest Nanotechnology Consumer Products Inventory highlights that MNMs are the most highly used NM types, accounting for 37% nanoproducts worldwide (Vance et al., 2015). Among these, titanium dioxide nanoparticles (TiO2-NP) and zinc oxide nanoparticles (ZnO-NP) have the largest yield and are the most widely used in various applications including paints, coatings, catalysts, pharmaceuticals, food, cosmetics and toothpaste (Shi et al., 2013; Madhumitha et al., 2016). Although the annual production of Ag-NPs accounts for only 2% TiO2-NPs, more than 400 products contain this subtype (Vance et al., 2015). Moreover, Ag-NPs are widely used in medical fields, such as antibacterial, biological imaging, drug delivery and tumor hyperthermia (Abbasi et al., 2016; Mathur et al., 2018). TiO2-NPs, Ag-NPs and ZnO-NPs cause morphological changes in mitochondria (Hou et al., 2014; Jain et al., 2017; Jia et al., 2017; Ostaszewska et al., 2018; Pereira et al., 2018), MMP collapse and cytochrome C release leading to mitochondria-mediated apoptosis in various cell types (Huerta-Garcia et al., 2014; Sheng et al., 2015; Hong et al., 2016; Kovacs et al., 2016; Liang et al., 2016; Tan et al., 2016; Xin et al., 2016; Xue et al., 2016b; Zhao et al., 2016; Choudhury et al., 2017; Han et al., 2017; Reshma and Mohanan, 2017; Sruthi et al., 2017; George et al., 2018; Wang et al., 2018a; Wang et 9
al., 2018b; Tang et al., 2019). In addition, MNMs are reported to affect mitochondrial respiratory function. Yu et al. (2017) studied the effects of TiO2-NPs (anatase, rutile) on mouse macrophages. Data from the reverse electron transfer (RET) assay showed significant inhibition of mitochondrial respiration by TiO2-NPs. Moreover, the inhibitory effect of anatase was stronger, indicating a greater impact on mitochondria. Chen et al. (2018) performed GC-MS-based metabolic flux analysis of macrophages exposed to TiO2-NP, which showed a dose-dependent decrease in flux of metabolites in the Krebs cycle. Additionally, TiO2-NPs suppressed expression of mitochondrial respiratory chain complexes I, II and IV (Yu et al., 2015) and inhibited complex II activity (Ghanbary et al., 2018). Ag-NPs inhibit activity of liver mitochondrial complexes II, IV and ATP synthase in Sprague-Dawley male rats (Teodoro et al., 2016). The effects of these MNMs on mitochondrial respiration ultimately result in decreased ATP production and mitochondrial dysfunction (Park et al., 2014a; Tan et al., 2016; Sharma et al., 2017). MNMs have been shown to affect mitochondrial dynamics. Natarajan et al. (2015) examined the toxic effects of three different TiO2-NPs (rutile, anatase and P25) on primary rat hepatocytes. Their results showed that gene expression levels of OPA1 and MFN1 associated with mitochondrial fusion events were significantly downregulated upon exposure to 50 ppm P25 and anatase, with P25 exerting the highest effect. High levels of mitochondrial fragmentation were observed using the fluorescent stain MitoTracker FM for imaging mitochondria while downregulation of the fusion-related gene in the rutile treatment group was not significant. Wilson and co-workers (2015) 10
investigated the effects of rutile, anatase and P25 TiO2-NPs on mitochondrial dynamics of primary rat cortical astrocytes by determining the relative expression levels of Mfn1, Mfn2, and Drp1. At a concentration of 25 ppm, P25 induced marked upregulation of Mfn1 and Mfn2 transcript levels while astrocytes treated with anatase showed a significant increase in Mfn1, but not Mfn2, and those treated with rutile showed a significant increase in Mfn2, but not Mfn1. The three TiO2-NPs exerted no significant effects on Drp1 transcript levels. At a concentration of 100 ppm, all three TiO2-NPs enhanced the levels of Mfn1, Mfn2 and Drp1. Confocal imaging of mitochondrial morphology revealed that mitochondria of astrocytes treated with 25 ppm P25 showed the greatest degree of fusion while those treated with 100 ppm P25 and anatase displayed highest fragmentation. In a study by Yamada et al. (2018) on the effects of Ag-NPs on human embryonic stem cell-derived neural progenitor cells (NPCs), AgNPs induced mitochondrial fragmentation and reduced the level of mitochondrial fusion related protein Mfn-1. Mitochondrial division and fusion are closely related to mitophagy. Recent studies have demonstrated that MNMs also activate mitophagy (Wei et al., 2017; Wang et al., 2018a; Zhang et al., 2018b). Wei and co-workers (2017) showed that PINK1/parkin-mediated mitophagy exerts protective effects against toxicity to mouse microglial cell line BV-2 induced by ZnO-NPs. 4.2 Carbon nanomaterials CNMs are considered the most promising products of nanotechnology (Hirsch, 2010) and widely used in biomedicine (Saeed et al., 2014; Kim et al., 2017; Teradal 11
and Jelinek, 2017), electronic components (Wang and Dai, 2015) and architecture (Hincapie et al., 2015). Common CNMs include zero-dimensional fullerenes (C60), onedimensional carbon nanotubes (CNTs) and the two-dimensional carbon allotrope graphene (Teradal and Jelinek, 2017). We have mainly focused on the mitochondrial toxicities of these three CNMs and their derivatives. In experiments on mitochondrial toxicity induced by C60 and its derivatives, Yang et al. (2016) extracted rat liver mitochondria followed by direct exposure to polyhydroxylated fullerenes (C60(OH)44), which resulted in mitochondrial swelling, mitochondrial membrane fluidity changes, MMP collapse and mitochondrial permeability transition (MPT) in addition to causing a decrease in mitochondrial respiratory control ratio (RCR; ratio of state 3 to state 4 respiration rates, which is an important parameter reflecting the coupling of mitochondrial oxidative phosphorylation) by promoting status 4 respiration and inhibiting state 3 respiration. The low respiration rate of state 4 (when ADP is exhausted) indicates intact mitochondrial inner membrane, which is necessary to maintain a sufficiently high potential to limit electron transport. The high respiratory rate of state 3 in the presence of ADP indicates the integrity of the respiratory chain (Adlam et al., 2005). The findings suggest impairment of the integrity of the mitochondrial inner membrane and respiratory chain by C60(OH)44. Santos et al. (2014) reported that C60 has higher affinity for the mitochondrial membrane than C60(OH)18–22 with a greater inhibitory effect on mitochondrial function, indicating that the surface chemistry of fullerene nanoparticles influences their toxic effects on mitochondria. In addition, C60 is reported to stimulate translocation of the pro-apoptotic 12
protein, Bax, to mitochondria, leading to mitochondria-mediated apoptosis (Song et al., 2012). Other fullerene derivatives, such as C60OH and C60(OH)24, are reported to cause a decrease in ATP generation and MMP (Johnson-Lyles et al., 2010; Nakagawa et al., 2015). Numerous studies have explored the toxicity of accumulating CNTs to mitochondria (Zhou et al., 2011; Xu et al., 2016). Furthermore, some researchers have utilized this property and combined drugs with CNTs to activate apoptosis (Yoong et al., 2015; Kim et al., 2017). Carbon nanotubes and their derivatives cause a variety of mitochondrial toxicities as specified earlier (mitochondrial morphological changes, decreased MMP, MPTP opening and cyto C release (Ma et al., 2012; Park et al., 2014b; Zhu et al., 2016; Visalli et al., 2017; Naserzadeh et al., 2018; Zhu et al., 2018; Visalli et al., 2019)), along with mtDNA damage (Xu et al., 2016). CNTs and their derivatives have multiple effects on mitochondrial respiratory function, including significant decrease in mitochondrial oxygen consumption (Ma et al., 2012; Xu et al., 2016), expression of MT-ND2 (mitochondria-NADH dehydrogenase subunit 2) and MT-ND3 (mitochondria-NADH dehydrogenase subunit 3) (Xu et al., 2016), decreased activity of mitochondrial respiratory chain complex II and ATP synthase (Ghanbari et al., 2017; Chen et al., 2012), attenuated electron transfer and conformational changes of cytochrome C (Ma et al., 2012). Different CNTs and their derivatives exert distinct mitochondrial toxicity effects. Ghanbari et al. (2017) compared the effects of equivalent doses of SWCNTs and MWCNTs on rat skin cells and found that mitochondrial toxicity caused by SWCNTs was higher than that of MWCNTs in terms of complex II activity, 13
cytochrome c release, reduction of MMP and ATP production. Moreover, levels of MMP decline and cytochrome C release induced by modified MWCNTs, such as MWCNT-COOH (hydroxylation) (Liu et al., 2014a), MWCNT -OH(hydroxylation) (Liu et al., 2014b) and tau-MWCNT (taurine functionalization) (Chen et al., 2012; Wang et al., 2012) were lower than those by raw MWCNTs. Similar to CNTs, mitochondria may be the main site of distribution of graphene and its derivatives in cells (Li et al., 2014; Zhou et al., 2014a). These compounds have a substantial impact on the respiratory function of mitochondria. Zhou et al. (2014a) reported that graphene and graphene oxide affect activity of mitochondrial respiratory chain complexes I, II, III and IV through effects on electron transfer between iron-sulfur centers but not the activity of complex V, potentially due to the absence of an ironsulfur center in this complex. The group additionally evaluated the effect of PEGmodified graphene oxide (PEG-GO) on mitochondrial oxidative phosphorylation system (OXPHOS) activity in breast cancer cell lines MDA-MB-231, MDA-MB-436 and SK-BR-3 using the Seahorse XF24-3 Extracellular Flux Analyzer to monitor mitochondrial oxygen consumption rate (OCR). PEG-GO reduced basal and maximal OCR to a significant extent, suggesting inhibition of mitochondrial OXPHOS activity, and downregulated mitochondrial respiratory chain complexes II and III in breast cancer cells, resulting in suppression of ATP production (Zhou et al., 2014b). In terms of the influence of graphene and its derivatives, the majority of studies to date have reported a decrease in MMP (Lammel et al., 2013; Hu et al., 2015; Zou et al., 2018; Jaworski et al., 2019), but with the use of higher concentrations of graphene and its 14
derivatives. Moreover, the results were obtained at a single time-point. Mari et al. (2016) studied the effects of low-dose (2 μg/mL) graphene oxide on mitochondria of neuroblastoma cell lines, SK-N-BE (2) and SH-SY5Y, at different time-points. MMP decreased in the first 4 h, followed by a gradual increase, and structurally disordered mitochondria were observed in the autophagosome after 48 h of GO exposure, indicating the occurrence of mitophagy. Moreover, extremely low doses (0.01–1 μg/L) of graphene oxide have been shown to cause changes in mitochondrial morphology and structures of adult zebrafish (Ren et al., 2016), indicating that graphene and its derivatives are more toxic to mitochondria. Additionally, graphene and derivatives are capable of inducing cytochrome C release, resulting in mitochondria-mediated apoptosis (Park et al., 2015; Jaworski et al., 2019). 4.3 Quantum dots Quantum dots (QD), also known as semiconductor nanocrystals, consist of II-IV or III-V elements with physical dimensions smaller than the exciton Bohr radius (Alivisatos, 1996). Their optical properties can be altered by adjusting the physical QD size (Esteve-Turrillas and Abad-Fuentes, 2013). Compared with traditional organic dyes, QDs have a longer fluorescence lifetime (Volkov, 2015) and are therefore more widely used in bioimaging (Mukherjee et al., 2016; Liu et al., 2017; Ma et al., 2017; Matea et al., 2017). Several in vitro experiments have identified mitochondria as one of the distribution sites of QDs (Clift et al., 2011; Wang et al., 2016; Han et al., 2019). In experiments by Li et al. (2011) involving direct exposure of rat liver mitochondria to 15
NAC-coated CdTe QDs, state 3 respiration was significantly decreased while state 4 respiration initially increased and then decreased with increasing QD doses, along with mitochondrial swelling and membrane lipid peroxidation. In the majority of in vitro studies, different cell types were exposed to QDs, which caused a range of mitochondrial toxicities including mitochondrial swelling and cristae disappearance, reduction of MMP and oxygen consumption, decreased levels of mitochondrial respiratory chain complexes II-IV and concomitantly increased complex V, MPTP opening, and cytochrome C release, with consequent mitochondria-mediated apoptosis (Chan et al., 2006; Nguyen et al., 2013; Wu et al., 2013; Lai et al., 2015; Nguyen et al., 2015), but no mtDNA damage (Paesano et al., 2016; Pasquali et al., 2017). In an in vivo study, Lin et al. (2012) treated mice with a single dose of QD (intravenous; 40 pmol) and examined mitochondrial toxicity in kidney at 4, 12, 16 and 24 weeks. Disorientation and decreased numbers of mitochondria were detected early, followed by mitochondrial swelling and compensatory hypertrophy, and finally an increase in number. Other studies have shown that toxic effects of QDs on mitochondria are affected by surface modification and particle size. Xiang et al. (2018) investigated the mitochondrial toxicity of CdTe QDs coated with thioglycolic acid (TGA), mercaptoethylamine (MEA) and 1-cysteine (1-Cys) in liver of female Wistar rats. All three types of QDs reduced mitochondrial respiration rates of state 3, state 4 and unconjugated states in a dosedependent manner. TGA-CdTe QDs exerted greater effects on mitochondria morphology, MMP and MPTP proteins than the other two QD types. MEA-CdTe QDs induced a dose-dependent decrease in mitochondrial membrane fluidity and l-Cys16
CdTe QDs had no significant effect while TGA-CdTe QDs increased mitochondrial membrane fluidity in a dose-dependent manner. The group of Lai (2016) reported greater effects of larger particle sizes of CdTe QDs on mitochondrial morphology, MMP and permeability. Therefore, toxic effects on mitochondria may be reduced by adjusting the modifications and particle sizes of QDs.
5. Conclusions and Future Perspectives In this review, we have provided an overview of the multiple subcellular, cellular and in vivo toxic effects of NMs on mitochondria, including morphological and dynamic changes, decreased MMP, opening of MPTP, impaired mitochondrial respiratory function, and apoptosis caused by increased cytochrome C release. The differences in mitochondrial toxicity between NMs with various modifications and particle sizes are additionally explored. Although the included studies have provided valuable insights into the mitochondrial toxicity of NMs, a number of aspects require further research. Firstly, the majority of studies to date have investigated the toxic effects of NMs on mitochondria in vitro, and further in vivo evaluation is required. Secondly, changes in mitochondrial dynamics were detected in mitochondrial toxicity studies on MNMs, but not those on CNMs and QDs. The reasons for this discrepancy require further clarification. Thirdly, CNTs cause damage to mitochondrial DNA, but not QDs. Therefore, in further research on the mitochondrial toxicity of different NMs, the integrity of mitochondrial DNA should be routinely analyzed. Fourthly, in most studies, the exposure concentration was high and mitochondrial toxicity of NMs was 17
observed at a single time-point. Future analyses should be conducted using low concentrations and the toxic effects of NMs on mitochondria examined at different time-points. Harnessing the mitochondrial toxicity of NMs is emerging as a promising research strategy. Given the diverse functions of mitochondria in both physiological and pathological contexts, damaged mitochondria serve to balance survival and death and ultimately dictate cellular fate. A key objective of upcoming studies in this field will be to clarify the mechanisms associated with mitochondrial toxicity and enhance its applicability to nanotoxicity studies and risk assessment of exposure in the near future.
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Acknowledgments This work was Supported by the National Natural Science Funds of China (No. 81673218) and the Fundamental Research Funds for the Central Universities (No. 2242019K40223).
Disclosure The author reports no conflicts of interest in this work.
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Figure legends Figure 1. Mitochondrial structure and function. The main function of mitochondria is to produce ATP, which is achieved via electron transport of respiratory chain complexes embedded in the cristae. ROS are generated during electron transport, and complexes I and III are the main source of mtROS. mtDNA in the mitochondrial matrix encodes the majority of oxidative phosphorylation enzyme complexes. MPTPs are composed of transmembrane proteins on the inner and outer membranes of mitochondria and involved in the regulation of intracellular calcium homeostasis and ATP/ADP transport. Figure 2. Role of mitochondria in nanomaterial-induced toxicity. When cells are exposed to environmental stress (such as elevated ROS) induced by nanomaterials, mitochondrial dynamics are regulated to control mitochondrial quality and maintain cell homeostasis. Under slight environmental stress, mitochondria promote production of ATP and reduce the influence of stress through fusion. Under high environmental stress, cells are protected through proper fission of mitochondria and mitophagy. Nanomaterials also cause production of excess ROS by affecting the activity or expression of respiratory chain complexes, thereby further affecting mitochondrial dynamics and structure and leading to decreased MMP and ATP production. In addition, some nanomaterials induce structural damage upon entry into mitochondria, causing a decrease in the bcl-2/bax ratio and opening of MPTP. Eventually, cytochrome C is released into the cytoplasm, triggering mitochondria-mediated apoptosis.
43
Table legends Table 1. Physicochemical properties of metal and metal oxide nanomaterials and corresponding tissue-specific and cell-specific mitochondrial toxicity Table 2. Physicochemical properties of carbon nanomaterials and corresponding tissuespecific and cell-specific mitochondrial toxicity Table 3. Physicochemical properties of quantum dots and corresponding tissue-specific and cell-specific mitochondrial toxicity
44
45
46
Table 1. Physicochemical properties of metal and metal oxide nanomaterials and corresponding tissue-specific and cell-specific mitochondrial toxicity S.
NMs type
Size(nm)
No.
Target organ or cell
Concentration or exposure
type used
route,
time
Mitochondrial effects
Reference
and
concentration 1
TiO2-NPs
<50nm
Rat and human glial
20µg/cm2
Mitochondrial depolarization
Huerta-
cells(C6 and U373)
Garcia et al. (2014)
2
TiO2-NPs
117±19nm
Endothelial cells
0.1, 0.15, 0.2 mg/mL
Decreased number of mitochondria, mitochondrial swelling
3
TiO2-NPs
5-6nm
Primary hippocampal
5, 15, 30µg/mL
Hou et al. (2014)
Decreased MMP, increased release of Cyto-c
neurons in Sprague-
Sheng et al. (2015)
Dawley rats 4
TiO2-NPs
5-6nm.
Primary Sertoli cells
5, 15, 30µg/mL
Decreased MMP and increased
release of Cyto-c
isolated from mice 5
TiO2-
21-50nm
NPs(rutile, anatase
Primary
Hong et al. (2016)
rat
20, 50,100ppm
hepatocytes and
MMP reduction, OPA-1 and Mfn-1 expression
Natarajan
levels were significantly down-regulated when
et al. (2015)
exposed to 50ppm P25 and anatase
P25) 6
TiO2-NPs
20nm
Human monocyte
10, 20, 50, 100µg/mL
Mitochondrial swelling, decreased MMP and ATP
Ghanbary
production, increased Cyto-c release, decreased
et al. (2018)
activity of mitochondrial respiratory chain complex II 7
TiO2-NPs
250nm
Human
bronchial
epithelial
50, 100µg/mL
cells
Mitochondrial swelling, reduction in mitochondrial number, decreased VDAC1 expression, decreased
(16HBE14o-)
Yu et al. (2015)
expression of respiratory chain complexes I, II and IV, reduced ATP production
8
TiO2-NPs
73.29 ± 5.75nm
Human
trophoblast
1, 10, 100µg/mL
Activation of mitophagy
Zhang et al.
HTR-8/SVneo cells 9
TiO2-NPs
20-100nm
(rutile, anatase
Primary rat cortical
(2018b) 25, 50, 100ppm
astrocytes
Decreased MMP, when the exposure concentration was
and P25)
25ppm,
P25
significantly
up-regulated
Wilson
et
al. (2015)
transcript levels of Mfn1 and Mfn2, while anatase significantly
up-regulated
Mfn1
transcription
levels and rutile significantly up-regulated Mfn2 transcription
levels,
when
the
exposure
concentration was 100ppm, all three TiO2-NPs significantly increased the transcript levels of Mfn1, Mfn2 and Drp1 10
TiO2-NPs
100-300 nm
Macrophages
10, 100µg/ml
Increased mitochondrial reactive oxygen species (ROS) levels ,decreased ATP content, and
47
Chen et al. (2018)
decreased metabolic flux in tricarboxylic acid (TCA) cycle 11
TiO2-
12-25nm
NPs(anatase) 12
TiO2-
Chinese hamster lung
1, 10, 25, 50, 100µg/ml
Mitochondrial swelling
fibroblast cells (V-79) 20-40nm
NPs(anatase,
Mouse
macrophage
(2017) 12.5, 25, 50, 200µg/ml
Decreased mitochondrial membrane potential,
line RAW264.7 7
inhibition of mitochondrial reverse electron
rutile) 13
TiO2-NPs
Jain et al.
Yu et al. (2017)
transport(RET) activity 223.6±21.5nm
Mouse
alveolar
2.5, 5, 10, 20µg/mL
ATP generation reduction
Park et al.
macrophage cell line
(Sheet-type)
(2014a)
(MH-S) 14
TiO2-NPs
10-90nm
ICR mice liver, brain
Intraperitoneal injection 5,
Mitochondrial
and embryo
10,
vacuoles
50,
200mg/kg,
100,
150,
observed
swelling
and
mitochondrial
Jia et al. (2017)
2
weeks 15
Ag-NPs
13.5 -43.8nm
A549, HepG2
12.5,
25,
50,
100,
Decreased MMP
Xin et al.
200µg/mL 16
Citrate-coated
2-15n, 10-70nm
Ag-NPs 17
Ag-NPs
235.5±25.1nm
(2016)
Saos-2 osteosarcoma
50, 10, 15, 20, 25μM;
Decrease in MMP, increased mitochondrial Cyto-c
cell
20, 40, 60, 80, 100μM
release
1.5mg/L
Mitochondrial swelling
Rainbow
trout
Kovacs et al. (2016)
hepatocytes
Ostaszewsk a
et
al.
(2018) 18
Ag-NPs
2-100nm
F9 mouse embryonic
12.5μg/mL
Decreased MMP
Han et al.
carcinoma cells 19
Ag-NPs
20-26nm
SH-SY5Y
(2017) 50μg/mL
Decreased MMP and production of ATP
Tan et al.
neuroblastoma cells 20
Ag-NPs
10-30nm
HepG2
(2016) 40, 80, 160μg/mL
Decreased MMP
Xue et al. (2016b)
21
Ag-NPs
10nm
Human stem
22
Ag-NPs
10nm, 100nm
embryonic
0.1, 0.2, 0.3μg/mL
cell-derived
mitochondrial fragmentation and decreased the
neural progenitor cells
level of the mitochondrial fusion protein mitofusin
(NPCs)
1 (Mfn1)
Rat tracheal epithelial
100,10000μg/L
Increased Cyto-c release and caused mitochondria-
cells (RTE) 23
Rubus-
30-150nm
conjugated Ag
Decreased ATP production and MMP, induced
Human breast cancer
mediated apoptosis 2.5, 5, 10μg/ml
al. (2018)
Tang et al. (2019)
Decreased MMP, increased release of Cyto-c
cell MCF-7
Yamada et
caused mitochondria-mediated apoptosis
George et al. (2018)
NPs 24
sodium citrate-
10,75nm
coated Ag-NPs
Sprague-Dawley male
Intraperitoneal
injection
Mitochondrial
swelling,
decreased
MMP,
rat liver
250 µM/kg weekly, for 4
mitochondrial permeability transition (MPT),
weeks.
decreased activity of mitochondrial respiratory
Teodoro et al. (2016)
chain complex II, IV and ATP synthase activity 25
Ag-NPs, TiO2NPs
<100nm
Male Wistar rat live
Gavage
treatment,
100µg/kg/day for 21 days
Mitochondrial swelling, uncoupling effect in
Pereira
oxidative phosphorylation system, GSH/GSSG
al. (2018)
ratio reduction
48
et
26
ZnO-NPs
50-100nm
C6 cells
5, 10, 20, 40, 80µg/mL
Decreased MMP
Sruthi et al. (2017)
27
ZnO-NPs
25-40nm
Human kidney
embryonic (HEK
293)
5,
15,
25,
50,
75,
Decreased MMP
Reshma and
100μg/mL
Mohanan
cells 28
ZnO-NPs
85-130nm
(2017)
HEK-293 cells
25, 50µg/mL
Increased mitochondrial Cyto-c release, decreased MMP
29
ZnO-NPs
40-170nm
Zebrafish embryo
10, 30, 60, 90, 120mg/L
et al. (2017)
Decreased MMP, increased release of Cyto-c caused mitochondria-mediated apoptosis
30
ZnO-NPs
~50nm
CAL 27 oral cancer
25µg/mL
Mitochondrial
cell lines 31
ZnO-NPs
38.52 ± 2.82nm
swelling,
decreased
activation of PINK1/Parkin-mediated
Mouse microglial cell
6.6μg/ml
Zhao et al. (2016)
MMP,
mitophagy
Decreased ATP production and MMP, increased
line, N9
Choudhury
release of Cyto-c caused mitochondria-mediated
Wang et al. (2018a) Sharma et al. (2017)
apoptosis 32
ZnO-NPs
50nm
Murine microglia cell
10μg/mL
Mitochondrial
line, BV-2
swelling,
decreased
activation of PINK1/Parkin-mediated
MMP,
mitophagy
Wei et al. (2017)
and PINK1/parkin-mediated mitophagy plays a protective role in ZnO-NPs-induced cytotoxicity. 33
ZnO-NPs
70nm
Human
aortic
8, 15, 25, 50μg/mL
endothelial cells 34
ZnO-NPs
10-35nm
Murine photoreceptor
Decreased MMP, increased release of Cyto-c caused mitochondria-mediated apoptosis
31.25, 62.5, 125μmol/L
cells
Reduction of ATP levels, collapse of MMP, Cytoc caused mitochondria-mediated apoptosis
49
Liang et al. (2016) Wang et al. (2018b)
Table 2. Physicochemical properties of carbon nanomaterials and corresponding tissue-specific and cell-specific mitochondrial toxicity S.
NMs type
No.
Diameter(D)
Target organ or cell
Concentration
Length(L)
type used
exposure route, time and
Thickness(T) 1
C60
D:179.3±3.4nm,
or
Mitochondrial effects
Reference
concentration Human
lung
123.4±4.9nm,
adenocarcinoma
108.6±3.5nm,
line A549
60mg/L
Bax
cell
translocated
to
mitochondria,
causing
mitochondria-mediated apoptosis
Song et al. (2012)
228.2±7.5nm 2
C60(OH)44
D:26.96 nm
Rat liver mitochondria
0, 5, 25, 50, 100, 150,
Mitochondrial
permeability
transition,
200μg/mL
mitochondrial
swelling,
decreased
mitochondrial
membrane
fluidity
MMP,
Yang et al. (2016)
changed,
decreased respiration rate of state 3 and increased respiration rate of state 4 3
C60(OH)24
Rat hepatocytes
—
50μM
Decreased ATP production and MMP
Nakagawa et al. (2015)
4
Fullerenol
D:15.7nm
The
porcine
proximal
(C₆₀OHx)
cell
renal
0.2-60mM
Decreased ATP production and MMP
Johnson-
line
Lyles et al.
(LLC-PK1 cells) 5
MWCNTs
L:180nm
Mice
spermatocyte
cell line (GC-2spd)
(2010) 0.05,
0.25,
0.5,
1,
5μg/mL
mtDNA
damaged,
oxygen
consumption
decreased
decreased and
expression
mitochondrial
ATP
levels
production,
of
Xu et al. (2016)
MT-ND2
(mitochondria-NADH dehydrogenase subunit 2) and
MT-ND3
(mitochondria-NADH
dehydrogenase subunit 3) 6
SWCNTs, MWCNTs
D:1.3-2.3nm,
Male mouse skin
0.1, 0.2, 0.4μg/mL
Decreased activity of mitochondrial respiratory
5nm
chain complex II,
L:1.5um,
mitochondrial swelling,
Ghanbari et al. (2017)
decreased mitochondrial GSH, ATP and MMP,
5um
increased
release
of
Cyto-c
(SWCNTs>
MWCNTs) 7
MWCNTs,
D:10-20nm,
MWCNT-
L:10-30μm
L02 cells
12.5,
25,
200μg/mL
COOH 8
SWCNTs,
50,
100,
Decreased MMP and increased Cyto-c release caused
mitochondria-mediated
apoptosis
Liu et al. (2014a)
(MWCNTs-COOH
Melanoma cells
0-0.4μg/mL
MWCNTs
Mitochondrial swelling, increased
mtROS,
decreased MMP,
Cyto-c
release
caused
Naserzadeh et al. (2018)
mitochondria-mediated apoptosis 9
Oxidized
L:60-500nm
MWCNTs 10
MWCNTs,
Saccharomyces
0-600mg/L
cerevisiae L:10-20μm
Decreased MMP, release of Cyto-c in dosedependent manners
SH-SY5Y cells
25μg/mL
Zhu et al. (2016)
Decreased MMP
Visalli
MWCNT-
et
al. (2017)
COOH 11
SWCNTs
Not specified
Human
epithelial
0-60μg/ml
50
Mitochondria
swelling
and
round,
cristae
Ma et al.
carcinoma cells
disappeared, decreased
mitochondrial oxygen
(2012)
consumption and MMP, decreased Cyto-c in mitochondria, disrupting
electron transfer of
Cyto-c 12
MWCNTs,
D:10-20nm
MWCNTs-OH
L:10-30μm
L02 cells
12.5,
25,
50,
100,
200μg/ml
Decreased MMP and increased Cyto-c release caused
mitochondria-mediated
apoptosis
Liu et al. (2014b)
( MWCNTs-OH< MWCNTs) 13
SWCNTs
D:4±2nm
Human
L:335±154nm
epithelial
bronchial
0.8, 1.7, 3.3 6.6μg/ml
Reduced ATP production, mitochondrial damaged
cells
Park et al. (2014b)
(BEAS-2B) 14
15
SWCNTs,
L:3.16μm
O-SWCNTs
263nm
MWCNTs,
Not specified
Saccharomyces
23.5, 47.1, 94.1, 188.2,
cerevisiae
376.4mg/L
Mouse
peritoneal
5, 20, 40, 80μg/ml
Decreased MMP and ATP production
Zhu et al. (2018)
Decreased MMP, release of cytochrome C,
tau-MWCNTs
macrophage cell line
decreased activity of ATP synthase and succinate
(Taurine-
(RAW 264.7)
dehydrogenase
Functionalized
Chen et al. (2012)
(tau-MWCNTs< MWCNTs)
) 16
Aci-MWCNT
D:10–20nm
Mouse
peritoneal
5, 20, 40, 80μg/ml
Mitochondrial swelling, decreased MMP, and
( acid-treated), L:0.3–0.6μm
macrophage cell line
release of Cyto-c caused mitochondria-mediated
tau-MWCNTs
(RAW 264.7)
apoptosis
(
Wang et al. (2012)
taurine-
functionalized) 17
Not specified
MWCNTs, MWCNTs
Human alveolar cell
2,20μg/ml
line A549
-
Dose dependent higher levels of dehydrogenase kinase 1
COOH
pyruvate
in the short time, and
then decreased, MMP declined,
Visalli
et
al. (2019)
increased
release of Cyto-c, MPTP opening 18
Graphene
D:42.0±11.3nm
oxide,
382.9±22.0nm
carboxyl
4672.5±414.9nm
graphene
HepG2 cells
1, 2, 4, 8, 16μg/ml,
Decreased MMP
Lammel et al. (2013)
2, 4, 8, 16, 32μg/ml
D:349.5±42.6nm 1805.6±616.8nm 4827.3±497.5nm
19
Graphene,
D:100-200nm
MDA-MB-231 human
graphene oxide
T:3-4nm
breast cancer cells,
20, 40, 60, 80, 100μg/ml
Decreased MMP and ATP production, inhibited activity
succinate of dehydrogenase by affecting
Zhou et al. (2014a)
the function of iron-sulfur center in succinate dehydrogenase, decreased
activity of complexes
I, II, III and IV in a dose-dependent manner
20
Graphene
D:0.5-5μm
oxide
T:0.8-1.2nm
C. vulgaris
0.01, 0.1, 1, 10mg/L
Decreased MMP
Hu et al., (2015)
51
21
22
Polyethylene
D:100-200nm
MDA-MB-231
glycol-
T:2-3nm
MDA-MB-436,
of complex II and complex III was significantly
modified
SK-BR-3(breast
down-regulated
graphene oxide
cancer cells)
,
Graphene
D:<2μm
Human
bronchial
nanoplatelets
T:3-4nm
epithelial cell (BEAS-
40μg/ml
2.5, 5, 10, 20μg/mL
Decreased ATP production, the expression levels
Decreased ATP production,
release of Cyto-c
caused mitochondria-mediated apoptosis
Zhou et al. (2014b)
Park et al. (2015)
2B)
23
Graphene
D:22-26nm
oxide
Neuroblastoma Lines
Cell
2μg/mL
(SK-N-BE(2),
MMP decreased in the first 4 hours, then gradually increased, and returned to normal in 72 hours. At
SH-SY5Y)
Mari et al. (2016)
48 hours, mitochondria swelling and disintegrating were observed. At 72 hours, mitochondrial conformational condensation and mitochondria with structural dysfunction in autophagosomes were observed.
24
Graphene
D:0.5μm
oxide
T:1.02±0.15nm
Adult zebrafish
0.01, 0.1, 1μg/L
The structures of the mitochondria were obscured, with the intact crista structure being fractured and
Ren et al. (2016)
reduced in size
25
Graphene
D:420nm-1.6μm
Human
glioblastoma
20, 50, 100, 200μg/mL
Mitochondrial swelling, decreased MMP and ATP
U87 cell line and non-
production,
cancer
mitochondria-mediated apoptosis
cells
HS-5
release
of
Cyto-c
caused
Jaworski et al. (2019)
(bone marrow/stroma)
26
Graphene
D:0.3-2.6µm
oxide
T:1.01±0.05nm
Zebrafish larva
1, 10, 100μg/L
Decreased MMP AND Na+/K+-ATPase activity, and
up-regulated
proteins
associated
with
mitochondrial respiratory chain and intramolecular oxidoreductase activity, including ndufa8, ndufa2, ndufc2, ndufa10, mthfd1b, cox6a1, ndufs4, aifm4, acadsb and qsox1
52
Zou et al. (2018)
Table 3. Physicochemical properties of quantum dots and corresponding tissuespecific and cell-specific mitochondrial toxicity S.
NMs type
Size
No.
Diameter(D)
or and
Target organ or cell
Concentration
type used
exposure route, time and
Thickness(T) 1
ZnS-CdSe
3.5nm
QDs
or
Mitochondrial effects
Reference
concentration Human
150, 300nM
Increased
neuroblastoma IMR-
Cyto-c
release
and
caused
mitochondria-mediated apoptosis
Chan et al. (2006)
32 cells 2
NAC-capped
~5.5nm
CdTe QDs
Mitochondria isolated
200,
400,
from rat livers
800,1000nmol/mg
600,
Low concentration of QDs
Li
stimulated respiration rate of state 4 while high
et
al.
(2011)
concentration of QDs inhibited respiration rate of state 4, the respiration rate of state 3 decreased with the addition of QDs. mitochondrial swelling,
mitochondrial
membrane
lipid
peroxidation 3
Cd/Se/Te-
20nm
Mice kidneys
based QDs
Intravenous,40pmol, 4,
Mitochondrial
12, 16, and 24 weeks
mitochondrial
dysplasia, number and
decreased mitochondrial
Lin et al. (2012)
swelling (early changes), later compensatory mitochondrial hypertrophy and mitochondrial hyperplasia 4
5
CdTe QDs
CdTe QDs
14±2.8nm
13.98 ± 2.79 nm
HepG2 cells
HepG2 cells
0.001, 0.01, 0.1, 1, 10,
Increased
100μg/ml
mitochondria-mediated apoptosis
1, 10μg/ml
Mitochondrial swelling and cristae disappeared, MMP
Cyto-c
decreased,
release
and
caused
Nguyen et al. (2013)
mitochondrial
oxygen
Nguyen et al. (2015)
consumption and ATP production decreased, mitochondrial respiratory chain complex II-IV content and activity decreased significantly, and complex V content increased significantly. Stimulating mitochondrial biogenesis 6
7
GSH-CdTe
5.22±0.17nm,
Human
embryonic
QDs
7.21±0.19nm,
kidney
9.34±0.37nm
293)
MEA-CdTe
2.20 ± 0.60nm,
Female Wistar rats
QDs,
l-Cys-
2.35 ± 0.55nm,
liver mitochondria
CdTe
QDs,
2.35 ± 0.40nm
cells
1, 2, 4μM
(HEK
Decreased MMP, mitochondrial swelling and increased
mitochondrial
inner
membrane
Lai et al. (2016)
permeability 100, 200, 300, 400nM
Three types of CdTe QD reduced mitochondrial respiration rates of state 3, state 4 and unconjugated state in a dose-dependent manner.
TGA-CdTe
Mitochondrial swelling and decreased MMP
QDs
caused by TGA-CdTe QDs were stronger than the
other
two.
MEA-CdTe
QDs
reduce
mitochondrial membrane fluidity in a dosedependent manner. LCA-CdTe QDs increase
53
Xiang et al. (2018)
mitochondrial membrane fluidity in a dosedependent manner. TGA-CdTe QD has greater effects on MPTP proteins than the other two 8
Graphene QDs
D: ~20nm
Human gastric cancer
T:1nm
MGC‐803 and breast
20, 100, 200, 400μg/mL
Decreased MMP
Wu et al. (2013)
cancer MCF‐7 cells 9
MPA-CdTe
~4nm
HEK293 cells
25, 50, 100, 200nm
QDs 10
CdS QDs
Mitochondrial
swelling,
Decreased
MMP,
MPTP opening 6nm
Bakers' yeast strain
75, 100, 150mg/L
BY4742
(2015)
Decreased MMP and oxygen consumption, mitochondrial
Lai et al.
morphology
changes,
Pasquali et al. (2017)
morphological changes in mitochondria, but mtDNA was not damaged 11
CdS QDs
∼5nm
HepG2 cells
3, 7, 14μg/ml
Decreased MMP, no damage to
mtDNA
Paesano et al. (2016)
54
Highlights: 1. We provided an overview of the role of mitochondria in toxicity caused by nanomaterials. 2. We reviewed current knowledge of mitochondrial toxicity induced by nanomaterials. 3. We highlighted the challenges and opportunities regarding mitochondrial toxicity studies of nanomaterials.
55
Graphical abstract
56