Skip to main content

Dependence of Nanoparticle Toxicity on Their Physical and Chemical Properties


Studies on the methods of nanoparticle (NP) synthesis, analysis of their characteristics, and exploration of new fields of their applications are at the forefront of modern nanotechnology. The possibility of engineering water-soluble NPs has paved the way to their use in various basic and applied biomedical researches. At present, NPs are used in diagnosis for imaging of numerous molecular markers of genetic and autoimmune diseases, malignant tumors, and many other disorders. NPs are also used for targeted delivery of drugs to tissues and organs, with controllable parameters of drug release and accumulation. In addition, there are examples of the use of NPs as active components, e.g., photosensitizers in photodynamic therapy and in hyperthermic tumor destruction through NP incorporation and heating. However, a high toxicity of NPs for living organisms is a strong limiting factor that hinders their use in vivo. Current studies on toxic effects of NPs aimed at identifying the targets and mechanisms of their harmful effects are carried out in cell culture models; studies on the patterns of NP transport, accumulation, degradation, and elimination, in animal models. This review systematizes and summarizes available data on how the mechanisms of NP toxicity for living systems are related to their physical and chemical properties.


The International Organization for Standardization define nanoparticles (NPs) as structures whose sizes in one, two, or three dimensions are within the range from 1 to 100 nm. Apart from size, NPs may be classified in terms of their physical parameters, e.g., electrical charge; chemical characteristics, such as the composition of the NP core or shell; shape (tubes, films, rods, etc.); and origin: natural NPs (NPs contained in volcanic dust, viral particles, etc.) and artificial NPs, which are the focus of this review.

Nanoparticles have become widely used in electronics, agriculture, textile production, medicine, and many other industries and sciences. NP toxicity for living organisms, however, is the main factor limiting their use in treatment and diagnosis of diseases. At present, researchers often face the problem of balance between the positive therapeutic effect of NPs and side effects related to their toxicity. In this respect, the choice of an adequate experimental model for estimating toxicity between in vitro (cell lines) and in vivo (experimental animals) ones is of paramount importance. The NP toxic effects on individual cell components and individual tissues are easier to analyze in in vitro models, whereas in vivo experiments make it possible to estimate the NP toxicity for individual organs or the body as a whole. In addition, the possible toxic effect of NPs depends on their concentration, duration of their interaction with living matter, their stability in biological fluids, and the capacity for accumulation in tissues and organs. Development of safe, biocompatible NPs that can be used for diagnosis and treatment of human diseases can only be based on complete understanding of the interactions between all factors and mechanisms underlying NP toxicity.

Medical Applications of Nanoparticles

In medicine, NPs can be used for diagnostic or therapeutic purposes. In diagnosis, they can serve as fluorescent labels for detection of biomolecules and pathogens and as contrast agents in magnetic resonance and other studies. In addition, NPs can be used for targeted delivery of drugs, including protein and polynucleotide substances; in photodynamic therapy and thermal destruction of tumors, and in prosthetic repair [1,2,3,4,5,6]. Some types of NPs are already successfully used in clinic for drug delivery and tumor cell imaging [7,8,9].

Examples of the use of gold NPs have been accumulating recently. They have proved to be efficient carriers of chemotherapeutics and other drugs. Gold NPs are highly biocompatible; however, although gold as a substance is inert towards biological objects, it cannot be argued that the same is true for gold NPs, since there are no conclusive data yet on the absence of delayed toxic effects [10]. In addition to gold NPs, those based on micelles, liposomes [11], and polymers with attached “capture molecules” [12] are already used as drug carriers. Single- and multiwalled nanotubes are good examples of NPs used for drug delivery. They are suitable for attaching various functional groups and molecules for targeted delivery, and their unique shape allows them to selectively penetrate through biological barriers [13]. The use of NPs as vehicles for drugs enhances the specificity of delivery and decreases the minimum amount of NPs necessary for attaining and maintaining the therapeutic effect, thereby reducing the eventual toxicity. This is especially important in the case of highly toxic and short-lived chemo- and radiotherapeutic agents [14].

Quantum dots (QDs) constitute another group of NPs with a high potential for clinical use. QDs are semiconductor nanocrystals from 2 to 10 nm in size. Their capacity for fluorescence in different spectral regions, including the infrared one [15], makes them suitable for labeling and imaging cells, cell structures, or pathogenic biological agents, as well as various processes in cells, tissues, and body as a whole [16,17,18], which has important diagnostic implications [19, 20]. NPs based on superparamagnetic iron oxide are efficiently used as contrast agents in magnetic resonance tomography (MRT) for imaging liver, bone marrow, and lymph node tissues [21]. There is also an example where radioactively labeled single-walled carbon nanotubes functionalized with phospholipids were used for labeling integrin-containing tumors and their subsequent detection by means of positron emission tomography in experiments on mice [22].

Nanoparticles have also been used in designing biosensors, including those based on carbon nanotubes for measuring the glucose level [23], detecting specific DNA fragments and regions [24], and identifying bacterial cells [25].

Silver (or silver-containing) NPs exert antimicrobial and cytostatic effects; for this reason, they are widely used in medicine, e.g., for treating bandages, surgical instruments, prostheses, and contraceptives [13, 22]. Silver NPs have been reported to serve as effective and safe preservation agents in the cosmetic industry [26].

However, NPs may still be highly toxic, even if the safety of using many of their chemical constituents in medicine has been proved. The toxic effect may be caused by their unique physical and chemical properties, which underlie specific mechanisms of interaction with living systems. In general, this determines the importance of studying the causes and mechanisms of the potential toxic effect of NPs.

Mechanisms of Nanoparticle Toxicity

The toxicity of NPs is largely determined by their physical and chemical characteristics, such as their size, shape, specific surface area, surface charge, catalytic activity, and the presence or absence of a shell and active groups on the surface.

The small size of NPs allows them to penetrate through epithelial and endothelial barriers into the lymph and blood to be carried by the bloodstream and lymph stream to different organs and tissues, including the brain, heart, liver, kidneys, spleen, bone marrow, and nervous system [27, 28], and either be transported into cells by transcytosis mechanisms or simply diffuse into them through the cell membrane. Nanomaterials can also increase access to the blood stream through ingestion [29, 30]. Some nanomaterials can penetrate the skin [31, 32] and even greater microparticles can penetrate skin when it is flexed [33]. Nanoparticles, because of their small size, can extravasate through the endothelium in inflammatory sites, epithelium (e.g., intestinal tract and liver), tumors or penetrate microcapillaries [34]. Experiments modeling the toxic effects of NPs on the body have shown that NPs cause thrombosis by enhancing platelet aggregation [35], inflammation of the upper and lower respiratory tracts, neurodegenerative disorders, stroke, myocardial infarction, and other disorders [36,37,38]. Note that NPs may enter not only organs, tissues, and cells, but also cell organelles, e.g., mitochondria and nuclei; this may drastically alter cell metabolism and cause DNA lesions, mutations, and cell death [39].

The toxicity of QDs has been shown to be directly related to the leakage of free ions of metals contained in their cores, such as cadmium, lead, and arsenic, upon oxidation by environmental agents. QDs may be absorbed by mitochondria and cause morphological changes and dysfunction of the organelles [40]. Entry of cadmium-based QDs into cells and formation of free Cd2+ ions causes oxidative stress [41, 42].

Recent studies have shown that contact of lung tissue with NPs about 50 nm in size leads to perforation of the membranes of type I alveolar cells and the resultant entry of the NPs into the cells. This, in turn, causes cell necrosis, as evidenced by the release of lactate dehydrogenase [43]. There is evidence that QD penetration increases the cell membrane fluidity [44]. On the other hand, the formation of reactive oxygen species (ROS) induced by peroxidation of membrane lipids may lead to the loss of membrane flexibility, which, as well as an abnormally high fluidity, inevitably results in cell death.

Interaction of NPs with the cytoskeleton may also damage it. For example, TiO2 NPs induce conformational changes in tubulin and inhibit its polymerization [45], which disturbs intracellular transport, cell division, and cell migration. In human umbilical vein endothelial cells (HUVECs), damage of the cytoskeleton hinders the maturation of coordination adhesive complexes which link the cytoskeleton to the extracellular matrix, thereby disturbing the formation of the vascular network [46].

In addition, the NP cytotoxicity may interfere with cell differentiation and protein synthesis, as well as activate proinflammatory genes and synthesis of inflammatory mediators. It should be specially noted that normal protective mechanisms do not affect NPs; macrophage uptake of large PEGylated nanoparticles is more efficient than uptake of small ones, which leads to accumulation of NPs in the body [47]. Superparamagnetic iron oxide NPs have been demonstrated to disturb or entirely suppress osteogenic differentiation of stem cells and activate the synthesis of signal molecules, tumor antigens, etc. [48, 49]. In addition, interaction of NPs with the cell enhances the expression of the genes responsible for the formation of lysosomes [50], disturbs their functioning [51], and inhibits protein synthesis [52, 53]. A study on the toxic effects of NPs of different compositions on lung epithelial cells and human tumor cell lines has shown that NPs stimulate the synthesis of inflammation mediators, e.g., interleukin 8 [54]. According to Park, who studied the expression of proinflammatory cytokines in vitro and in vivo, the expressions of interleukin 1 beta (IL-1β) and tumor necrosis factor alpha (TNFα) are enhanced in response to silicon NPs [55].

Oxidation, as well as action of various enzymes on the shell and surface of NPs, results in their degradation and release of free radicals. In addition to the toxic effect of free radicals expressed as oxidation and inactivation of enzymes, mutagenesis, and disturbance of chemical reactions leading to cell death, degradation of NPs leads to alteration or loss of their own functionality (e.g., the loss of the magnetic moment and the changes in the fluorescence spectrum and transport or other functions) [56, 57].

In summary, the most common mechanisms of NP cytotoxicity are the following:

  1. 1.

    NPs may cause oxidation via formation of ROS and other free radicals;

  2. 2.

    NPs may damage cell membranes by perforating them;

  3. 3.

    NPs damage components of the cytoskeleton, disturbing intracellular transport and cell division;

  4. 4.

    NPs disturb transcription and damage DNA, thus accelerating mutagenesis;

  5. 5.

    NPs damage mitochondria and disturb their metabolism, which leads to cell energy imbalance;

  6. 6.

    NPs interfere with the formation of lysosomes, thereby hampering autophagy and degradation of macromolecules and triggering the apoptosis;

  7. 7.

    NPs cause structural changes in membrane proteins and disturb the transport of substances into and out of cells, including intercellular transport;

  8. 8.

    NPs activate the synthesis of inflammatory mediators by disturbing the normal mechanisms of cell metabolism, as well as tissue and organ metabolism (Fig. 1).

Fig. 1
figure 1

Mechanisms of cell damage by nanoparticles. (1) Physical damage of membranes [43, 67, 75]. (2) Structural changes in cytoskeleton components [45, 46]. (3) Disturbance of transcription and oxidative damage of DNA [61, 62]. (4) Damage of mitochondria [39, 40]. (5) Disturbance of lysosome functioning [51]. (6) Generation of reactive oxygen species [61]. (7) Disturbance of membrane protein functions [172]. (8) Synthesis of inflammatory factors and mediators [54, 55]

Although there are numerous mechanisms of NP toxicity, it is necessary to determine and classify the type and mechanism of each particular toxic effect of NPs as dependent on their physical and chemical properties.

Relationships of Nanoparticle Toxicity with Their Physical and Chemical Properties

The toxicity of NPs is considered to depend on their physical and chemical characteristics, including the size, shape, surface charge, chemical compositions of the core and shell, and stability. In particular, Oh et al., using the data meta-analysis of 307 papers describing 1741 cell viability-related data samples, recently analyzed the CdSe quantum dot toxicity. It has been shown that the QD nanotoxicity is closely correlated with their surface properties (including shell, ligand, and surface modifications), diameter, toxicity assay type used, and the exposure time [58]. Which of these factors is the most important is determined by the specific experimental task and model; therefore, we will now consider each factor separately.

Nanoparticle Size and Toxicity

The NP size and surface area play an important role, largely determining the unique mechanism of NP interaction with living systems. NPs are characterized by a very large specific surface area, which determines their high reaction capacity and catalytic activity. The sizes of NPs (from 1 to 100 nm) are comparable with the size of protein globules (2–10 nm), diameter of DNA helix (2 nm), and thickness of cell membranes (10 nm), which allows them to easily enter cells and cell organelles. For example, Huo et al. have demonstrated that gold NPs no larger than 6 nm effectively enter the cell nucleus, whereas large NPs (10 or 16 nm) only penetrate through the cell membrane and are found only in the cytoplasm. This means that NPs several nanometers in size are more toxic than 10 nm or larger NPs, which cannot enter the nucleus [59]. Pan et al. have traced the dependence of the toxicity of gold NPs on their size in the range from 0.8 to 15 nm. The NPs 15 nm in size have been found to be 60 times less toxic than 1.4-nm NPs for fibroblasts, epithelial cells, macrophages, and melanoma cells. It is also noteworthy that 1.4-nm NPs cause cell necrosis (within 12 h after their addition to the cell culture medium), whereas 1.2-nm NPs predominantly cause apoptosis [60]. These data suggest not only that NPs can enter the nucleus, but also that the correspondence of the geometric size of NPs (1.4 nm) to that of the major groove of DNA allows them to effectively interact with the negatively charged sugar–phosphate DNA backbone and block the transcription [61, 62].

In addition, the NP size largely determines how the NPs interact with the transport and defense systems of cells and the body. This interaction, in turn, affects the kinetics of their distribution and accumulation in the body. The review paper by [63] presents both theoretical considerations and numerous experimental data demonstrating that NPs smaller than 5 nm usually overcome cell barriers nonspecifically, e.g., via translocation, whereas larger particles enter the cells by phagocytosis, macropinocytosis, and specific and nonspecific transport mechanisms. An NP size of about 25 nm is believed to be optimal for pinocytosis, although this also strongly depends on the cell size and type [63, 64]. In vivo experiments have shown that NPs smaller than 10 nm are rapidly distributed among all organs and tissues upon intravenous administration, whereas most larger NPs (50–250 nm) are found in the liver, spleen, and blood [65]. This suggests that large NPs are recognized by specific defense systems of the body and absorbed by the system of mononuclear phagocytes, which prevents them from entering other tissues. In addition, Talamini et al. claimed that the NP size and shape influence the kinetics of accumulation and excretion of gold NPs in filter organs, and only star-like gold NPs are able to accumulate in the lung. They have also shown that the changes in the NP geometry do not improve the NP passage of the blood–brain barrier [66].

The large specific surface area ensures effective adsorption of NPs on the cell surface. This was shown in a study on the hemolytic activity of 100- to 600-nm mesoporous silicon particles towards human erythrocytes [67]. The particles 100 nm in size were effectively adsorbed on the erythrocyte surface without causing cell destruction or any morphological changes in the cells, whereas 600-nm particles deformed the membrane and entered the cells, resulting in erythrocyte destruction (hemolysis) [67].

Nanoparticle Shape and Toxicity

The characteristic shapes of NPs are spheres, ellipsoids, cylinders, sheets, cubes, and rods. NP toxicity strongly depends on their shape. This has been shown for numerous NPs of different shapes and chemical compositions [68,69,70,71]. For example, spherical NPs are more prone to endocytosis than nanotubes and nanofibers [72]. Single-walled carbon nanotubes have been found to more effectively block calcium channels compared to spherical fullerenes [73].

Comparison of the effects of hydroxyapatite NPs with different shapes (needle-like, plate-like, rod-like, and spherical) on cultured BEAS-2B cells have shown that plate-like and needle-like NPs cause death of a larger proportion of cells than spherical and rod-like NPs [74]. This is partly accounted for by the capacity of plate-like and needle-like NPs for damaging cells and tissue upon direct contact. Hu et al. [75] obtained interesting data when studying the damage of mammalian cells by graphene oxide nanosheets. The toxicity of these NPs was determined by their shape allowing them to physically damage the cell membrane. However, their toxicity was found to decrease with an increase in the fetal calf serum concentration in the culture medium. This was explained by a high capacity of graphene oxide NPs for adsorbing protein molecules, which cover the NP surface, thereby changing the shape of the NPs and partly preventing the damage of cell membranes [75].

Nanoparticle Chemical Composition and Toxicity

Although the toxicity of NPs strongly depends on their size and shape, the influence of other factors, such as the NP chemical composition and crystal structure, should not be disregarded. Comparison of the effects of 20-nm silicon dioxide (SiO2) and zinc oxide (ZnO) NPs on mouse fibroblasts has shown that they differ in the mechanisms of toxicity. ZnO NPs cause oxidative stress, whereas SiO2 NPs alter the DNA structure [76].

The toxicity of NPs is indeed largely determined by their chemical composition. It has been shown that degradation of NPs can occur, and its extent depends on the environment conditions, e.g., pH or ionic strength. The most common cause of the toxic effect of NPs interacting with cells is leakage of metal ions from the NP core. The toxicity also depends on the composition of the core of NPs. Some metal ions, such as Ag and Cd, are in fact toxic and, therefore, cause damage of the cells. Other metal ions, such as Fe and Zn, are biologically useful, but, at high concentrations, they could damage cellular pathways and, hence, cause high toxicity. However, this effect can be decreased, e.g., by coating NP cores with thick polymer shells, silica layers, or gold shells instead of short ligands or by using nontoxic compounds for NP synthesis. On the other hand, the composition of the core could be altered by addition of other metals. This can result in enhanced chemical stability against NP degradation and metal ion leakage into the body [77].

The toxicity of NPs also depends on their crystal structure. The relationship between crystal structure and toxicity has been studied using a human bronchial epithelium cell line and titanium oxide NPs with different types of crystal lattice. It has been demonstrated that NPs with a rutile-like crystal structure (prism-shaped TiO2 crystals) cause oxidative damage of DNA, lipid peroxidation, and formation of micronuclei, which indicates abnormal chromosome segregation during mitosis, whereas NPs with anatase-like crystal structure (octahedral TiO2 crystals) of the same size are nontoxic [78]. It should be noted that the NP crystal structure may vary depending on the environment, e.g., upon interaction with water, biological fluids, or other dispersion media. There is evidence that the crystal lattice of ZnS NPs is rearranged into a more ordered structure upon contact with water [79].

Nanoparticle Surface Charge and Toxicity

The surface charge of NPs plays an important role in their toxicity, because it largely determines the interactions of NPs with biological systems [80, 81].

NP surfaces and their charges could be modified by grafting differently charged polymers. PEG (polyethylene glycol) or folic acid is often used to improve the NP intracellular uptake and ability to target specific cells [82]. The synthesis of biocompatible TiO2 nanoparticles containing functional NH2 or SH groups has also been reported [83]. Other substances, such as methotrexate, polyethyleneimine, and dextran, had also been used to modify NP surfaces and their charge [84].

A high toxicity of positively charged NPs is explained by their ability to easily enter cells, in contrast to negatively charged and neutral NPs. This is accounted for by electrostatic attraction between the negatively charged cell membrane glycoproteins and positively charged NPs. Comparison of the cytotoxic effects of negatively and positively charged polystyrene NPs on HeLa and NIH/3T3 cells has shown that the latter NPs are more toxic. This is not only because positively charged NPs more effectively penetrate through the membrane, but also because they are more strongly bound to the negatively charged DNA, causing its damage and, as a result, prolongation of the G0/G1 phase of the cell cycle. Negatively charged NPs have no effect on the cell cycle [85]. Similar results have been obtained for positively and negatively charged gold NPs, positive NPs being absorbed by cells in larger amounts and more rapidly than negative ones and being more toxic [86].

Positively charged NPs have an enhanced capacity for opsonization, i.e., adsorption of proteins facilitating phagocytosis, including antibodies and complement components, from blood and biological fluids [87]. The adsorbed proteins, referred to as the protein crown, may affect the surface properties of NPs. For example, they may alter the surface charge, aggregation characteristics, and/or hydrodynamic diameter of NPs. In addition, adsorption of proteins on the NP surface leads to their conformational changes, which may decrease or completely inhibit the functional activities of the adsorbed proteins. The protein crown mainly consists of major serum proteins, such as albumin, fibrinogen, and immunoglobulin G, as well as other effector, signal, and functional molecules [88, 89]. Binding to NPs alters the protein structure, which leads to the loss of their enzymatic activity, disturbance of biological processes, and precipitation of ordered polymeric structures, e.g., amyloid fibrils [90]. This may lead to various diseases, such as amyloidosis. In vitro experiments have demonstrated that QDs coated with a hydrophilic polymer accelerate the formation of fibrils of human β2 microglobulin, which are then arranged into multilayered structures on the particle surface; this results in a local increase in the protein concentration on the NP surface, precipitation, and formation of oligomers [91].

Xu et al. developed a method for changing the NP charge from negative to positive via various modifications of the surface. For example, polymer NPs were modified with a pH-sensitive polymer so that, being negatively charged in a neutral medium, they acquired a positive charge in an acid medium, at pH 5–6 [92]. This technique makes it possible to substantially increase the rate of NP uptake by cells, which could be used for drug delivery to tumor cells. Estimation of the cytotoxicity of surface-modified cerium oxide NPs for H9C2, HEK293, A549, and MCF-7 cells has shown that basically different biological and toxic effects can be obtained by using different polymers to make the NPs positively or negatively charged or neutral. Specifically, positively charged and neutral NPs are absorbed by all cell types at the same rate, whereas negatively charged ones predominantly accumulate in tumor cells [93]. Thus, modification of the NP charge allows their localization and toxicity to be controlled, which could be used for developing effective systems for delivery of chemotherapeutic drugs to tumors.

Nanoparticle Shell and Toxicity

Application of a shell onto the surface of NPs is necessary for changing their optical, magnetic, and electrical properties; it is used for improving NP biocompatibility and solubility in water and biological fluids by decreasing their aggregation capacity, increasing their stability, etc. Thus, the shell decreases the toxicity of NPs and provides them with the capacity for selective interaction with different types of cells and biological molecules. In addition, the shell considerably influences the NP pharmacokinetics, changing the patterns of NP distribution and accumulation in the body [94].

As noted above, NP toxicity is largely related to the formation of free radicals [40, 57, 95, 96]. However, the shell can considerably mitigate or eliminate this negative effect, as well as stabilize NPs, increase their resistance to environmental factors, decrease the release of toxic substances from them, or make them tissue-specific [97]. For example, Cho et al. modified polymer NPs by coating them with lectins. The modified NPs selectively bound with tumor cells presenting sialic acid molecules on the surface, which made the NPs suitable for specifically labeling cancer cells [98].

The NP surface can be modified with both organic and inorganic compounds, e.g., polyethylene glycol, polyglycolic acid, polylactic acid, lipids, proteins, low molecular weight compounds, and silicon. This variety of modifiers makes it possible to form complex systems on the NP surface for changing the NP properties and for their specific transport and accumulation.

Nanoparticles coated with shells of synthetic polymers are used for delivery of antigens, thus serving as adjuvants boosting the immune response. This allows obtaining vaccines against the antigens that are targets of strong natural nonspecific cellular immunity [99].

The shell is often used for improving solubilization and decreasing the toxicity of QDs, because their metal cores are hydrophobic and mainly consist of toxic heavy metals, such as cadmium, tellurium, and mercury. The shell increases the stability of the QD core and prevents its desalination and oxidative or photolytic degradation. This, in turn, decreases the leakage of metal ions outside of the QD core and, hence, the toxicity of QDs [100,101,102].

Study of Nanoparticle Toxicity

During the past two decades, the use of NPs has tremendously extended and led to the foundation of nanotoxicology, a new science studying the potential toxic effects of NPs on biological and ecological systems. The general goal of nanotoxicology is to develop the rules of synthesis of safe NPs [103]. This calls for a comprehensive, systemic approach to analysis of the toxic properties of NPs and their effects on cells, tissues, organs, and the body as a whole.

There are two routine approaches to the study of the effects of various substances on living systems, which are also applicable to NP toxic effects: in vitro experiments on model cell lines and in vivo experiments on laboratory animals. We do not consider here the third possible approach to estimating NP toxicity, computer simulation, because the pathways and mechanisms of the toxic effects of NPs are not known well enough for a computer model to predict the consequences of interactions between NPs and living matter for a wide range of NPs with sufficient reliability.

Both cell culture and animal experimental models for studying NP toxicity have their specific advantages and disadvantages. The former allow deeper insight into the molecular mechanisms of toxicity and identification of the primary targets of NPs; however, the patterns of the distribution of NPs in the body and their transport to different tissues and cells are not taken into consideration. The study of NP toxicity in animal experiments allows the delayed effects of NP action in vivo to be estimated. However, the general pattern of toxicity manifestations becomes so complicated that it is impossible to determine which of them is the primary cause of the observed effect and which are its consequences.

Study of Toxicity in Cell Cultures

Many studies of NP toxicity are carried out in primary cell cultures serving as models of various types of human and animal tissues. In some cases, tumor cell lines are used, e.g., for estimating the toxic effects of NPs used in cancer chemotherapy. The type of cells is selected according to the potential route by which NPs enter the body. This may be oral uptake (mainly by ingestion), transdermal uptake (through the skin surface), inhalation uptake of NPs contained in the breathing air, or intentional NP injection in clinic. Intestinal epithelium cells (Caco-2, HT29, and SW480) are often used in experimental models for studying the toxicity of ingested NPs (Table 1). In these models, the kinetics of NP uptake by cells and the viability of cells upon the NP uptake are studied.

Table 1 Results of estimation of nanoparticle toxicity in experimental models of their oral uptake

The NPs that serve as carriers of drugs or contrast agents, or those used for imaging, are administered by injection. The toxicity of these NPs is studied in primary blood cell cultures. Most commonly, hemolysis, platelet activation, and platelet aggregation are estimated. In addition to primary blood cell cultures, cultured HUVECs, mesenchymal stem cells, mononuclear blood cells, and various tumor cell lines (HeLa, MCF-7, PC3, C4-2, and SKBR-3) are used (Table 2).

Table 2 Results of estimation of nanoparticle toxicity in experimental models of their intravenous administration and the consequences of interaction of nanoparticles with cells of various organs

The toxicity of inhaled NPs is studied using the cell lines modeling different tissues of the respiratory system, e.g., A549 and C10 cells of pulmonary origin, alveolar macrophages (RAW 264.7), various epithelial cells and fibroblasts (BEAS-2B, NHBE, 16-HBE, SAEC), as well as human monocytes (THP-1) (Table 3).

Table 3 Results of estimation of nanoparticle toxicity in experimental models of their inhalation uptake

The toxicity of NPs that enter the body transdermally is usually studied in keratinocytes, fibroblasts, and, more rarely, sebocytes (cells of sebaceous glands) (Table 4).

Table 4 Results of estimation of nanoparticle toxicity in experimental models of their transdermal uptake

Co-cultured Cell Lines and 3D Cell Cultures

Although the majority of in vitro nanotoxicity studies are carried out on cell monocultures, studies using two other approaches are increasingly often reported in the literature. One of them is co-culturing of several types of cells; the other is the use of 3D cultures. The rationale for these approaches is the need for more realistic models of mammalian tissues and organs. For example, co-cultured Caco-2 epithelial colorectal adenocarcinoma cells and Raji cells (a lymphoblast cell line) have served as a model of the human intestinal epithelium in experiments on the toxicity of silver NPs [104]. A co-culture of three cell lines derived from lung epithelial cells, human blood macrophages, and dendritic cells has been used as an experimental model in a study on the toxic effects of inhaled NPs [105]. A model of skin consisting of co-cultured fibroblasts and keratinocytes has been suggested [106].

It is known that the cell phenotype, as well as cell functions and metabolic processes, is largely determined by the complex system of cell interactions with other cells and the surrounding extracellular matrix [107]. Therefore, many important characteristics of cells with an adhesive type of growth in a monolayer culture substantially differ from those of the same cells in the living tissue; hence, conclusions from many experiments on the NP toxic effects on cells growing in a monolayer are somewhat incorrect [108]. Experimental 3D models of tissues and organs have been used for analysis of NP toxicity and penetration into cells in several published studies. For example, there are 3D models based on polymer hydrogels [109] and models constructed in special perfusion chambers containing a semipermeable membrane to which the cells are attached. Li et al. and Lee et al. [110, 111] used multicellular spheroids about 100 μm in size to obtain a 3D model of the liver and compare the toxicities of CdTe and Au NPs in experiments on this model and a monolayer culture of liver cells [111]. The results obtained using the 3D model were more closely correlated with the data obtained in experiments on animals, which indicates a considerable potential of this approach for adequate and informative testing of NP toxicity.

In vivo Study of Nanoparticle Toxicity

In addition to the study of multilayered and 3D cell cultures, the behavior of NPs in the living body is being extensively studied. Since these studies are focused on the biomedical applications of NPs, the NP toxicity for living organisms remains an important issue. Although NPs are highly promising for various clinical applications, they are potentially hazardous. This hazard cannot be estimated correctly in vitro, following from the comparison of the in vivo and in vitro effects of NPs.

Titanium dioxide (TiO2) particles are among the most widely used NPs, in particular, in environment protection measures. Therefore, it was exceptionally important to estimate their toxicity in the case of a 100% bioavailability, namely, in experiments with their intravenous injection to experimental animals. This study has been performed by Fabian et al. [112]. Experimental animals (rats) were injected with a suspension of TiO2 NPs at a dose of 5 mg/kg, and their biodistribution, as well as the general condition of the animals, was monitored. The results have shown that the animals exhibit no signs of ailment or disorder, nor is inflammation or another manifestation of a toxic effect observed, within 28 days. This suggests that TiO2 NPs are relatively harmless.

Silver NPs are another example of NPs potentially useful in medicine, owing to their antimicrobial activity. Their toxicity and biodistribution were analyzed in an experiment where CD-1 mice were intravenously injected with 10 mg/kg of silver NPs of different sizes (10, 40, and 100 nm) coated with different shells. Although each type of NPs was found to cause toxic damage of tissues, larger particles were less toxic, probably, due to their lower penetration capacity [113]. Asare et al. [114] estimated the genotoxicity of silver and titanium NPs administered at a dose of 5 mg/kg. They have found that silver NPs cause DNA strand breaks and oxidation of purine bases in the tissues examined. Gold nanoparticles have a similar effect [115]. They have been shown to be toxic for mice, causing weight loss, decrease in the hematocrit, and reduction of the red blood cell count.

Targeted drug delivery is one of the most important applications of NPs. In this case, it is also paramount to know their toxic properties, because the positive effect of their use should prevail over the negative one. Kwon et al. [116] have developed antioxidant NPs from the polymeric prodrug of vanillin. Their study has shown that the NPs have no toxic effect on the body, specifically the liver, at doses lower than 2.5 mg/kg. Similar results have been obtained for gelatin NPs modified with polyethylene glycol, which are planned to be used for targeted delivery of ibuprofen sodium salt [117]. The NPs have proved to be nontoxic at the dose that is necessary for effective drug delivery (1 mg/kg), which has been confirmed by measuring the inflammatory cytokine levels in the animals studied, as well as histological analysis of their organs.

Quantum dots are among the NPs that are most promising for medical applications (Fig. 2). However, they are potentially hazardous for human health, because they exhibit various toxic effects in both in vitro and in vivo experiments [118,119,120,121,122].

Fig. 2
figure 2

The possible reasons why quantum dots may be nontoxic in animal models. (1) The shell prevents the leakage of heavy metals into the body [129, 135]. (2) Quantum dots are localized in the liver and subsequently eliminated from the body [135, 173]. (3) The protein crown around quantum dots protects the body from heavy metals [132, 174]

Toxic effects of QDs in vivo are usually studied in experiments on mice and rats [123]. A study on the toxicity of cadmium-based QDs for mice showed that QDs were distributed throughout the body as soon as 15 min after injection to the caudal vein, after which they accumulated in the liver, kidneys, spleen, red bone marrow, and lymph nodes. Two years after the injection, fluorescence was mainly retained in lymph nodes; in other organs, no QDs were detected [124]. It should be also noted that the fluorescence spectrum was shifted to the blue spectral region because of the destruction of the QD shell and changes in the shape, size, and surface charge of the QDs. This, however, occurred rather slowly, because the QDs were found to be nontoxic after their injection at the doses at which pure cadmium ions would have had a lethal effect. Similar results were obtained by Yang et al. [125]. Zhang et al. [95] showed that CdTe QDs predominantly accumulated in the liver, decreasing the amount of antioxidants in it and inducing oxidative stress in liver cells.

Cadmium and tellurium ions tend to accumulate in various organs and tissues upon degradation and decay of the cores of CdTe/ZnS QDs. Experiments on mice have shown that cadmium predominantly accumulates in the liver, kidneys, and spleen, whereas tellurium accumulates almost exclusively in the kidneys [126]. Ballou et al. [127] found that cadmium-containing QDs coated with polymer shells of polyacrylic acid or different derivatives of polyethylene glycol had no lethal effect on experimental mice and remained fluorescent for 4 months. СdSe/ZnS NPs also had no detectable pathological effect on mice [128]; however, the absence of distinct signs of pathology still does not mean that the QDs are absolutely nontoxic.

Hu et al. [129] found that lead-containing QDs had no toxic effect on mice for 4 weeks; however, this was most probably because the QDs studied were coated with a polyethylene glycol shell.

Since heavy metals contained in QDs are a factor of their toxicity, several research groups suggested that heavy-metal-free NPs be synthesized. For example, Pons et al. [130] synthesized CuInS2/ZnS QDs fluorescing in the near-infrared spectral region (at a wavelength of about 800 nm) and supposed that this composition would make the QDs nontoxic for experimental animals. Comparison of the effects of CuInS2/ZnS and CdTeSe/CdZnS QDs on regional lymph nodes in mice showed that the lymph nodes were only slightly, if at all, enlarged upon injection of the QDs not containing heavy metals, whereas injection of the CdTeSe/CdZnS QDs induced a distinct immune response in them [130]. QDs in which silicon was substituted for heavy metals also had no toxic effect on mice [131].

Even QDs containing heavy metals are often found to be nontoxic. One of the possible explanations is that QDs are coated with the protein crown upon entering the living body; this crown shields their surface and protects cells against damage [132]. Usually, the proteins that are included in the NP molecular corona are major serum proteins, such as albumin, immunoglobulin G (IgG), fibrinogen, and apolipoproteins [133]. Molecular corona also can influence on the interaction of NPs with cells. Zyuzin et al. have demonstrated that, in human endothelial cells, the NP protein corona decreases the NP nonspecific binding to the cell membrane, increases the residence time of NP in early endosomes, and reduces the amount of internalized NPs [134].

However, even in the absence of direct signs of intoxication in experimental animals, it remains unclear whether the use of QDs in medicine is safe for humans. In some cases, the QD toxicity was not detected in mice because the NPs were neutralized by the liver and accumulated in it [135]; in other cases, QDs coated with phospholipid micelles exhibited reduced toxicity owing to the shell [129]. Despite the extensive in vivo studies on QD toxicity, their use in biomedicine remains an open question. One of the main reasons is that all the delayed effects of QDs cannot be monitored in experimental animals, because their lifespan is as short as a few years, which is insufficient for complete elimination or degradation of NPs.


The potential toxicity of NPs is the main problem of their use in medicine. Therefore, not only positive results of the use of NPs, but also the possible unpredictable negative consequences of their action on the human body, should be scrutinized. The toxicity of NPs is related to their distribution in the bloodstream and lymph stream and their capacities for penetrating into almost all cells, tissues, and organs and interacting with various macromolecules and altering their structure, thereby interfering with intracellular processes and the functioning of whole organs. The NP toxicity strongly depends on their physical and chemical properties, such as the shape, size, electric charge, and chemical compositions of the core and shell. Many types of NPs are not recognized by the protective systems of cells and the body, which decreases the rate of their degradation and may lead to considerable accumulation of NPs in organs and tissues, even to highly toxic and lethal concentrations. However, a number of approaches to designing NPs with a decreased toxicity compared to the traditional NPs are already available. Advanced methods for studying the NP toxicity make it possible to analyze different pathways and mechanisms of toxicity at the molecular level, as well as reliably predict the possible negative effect at the body level.

Thus, it is obvious that designing NPs that have small or no negative effects is impossible unless all qualitative and quantitative physical and chemical properties of NPs are systematically taken into consideration and a relevant experimental model for estimating their influence on biological systems is available.



Food and Drug Administration




Magnetic resonance tomography




Quantum dot


Reactive oxygen species


Scanning electron microscopy


Transmission electron microscopy


Tumor necrosis factor alpha


  1. 1.

    Iqbal MA, Md S, Sahni JK, Baboota S, Dang S, Ali J (2012) Nanostructured lipid carriers system: recent advances in drug delivery. J Drug Target 20(10):813–830

    Article  Google Scholar 

  2. 2.

    Liechty WB, Kryscio DR, Slaughter BV, Peppas NA (2010) Polymers for drug delivery systems. Annu Rev Chem Biomol Eng 1(1):149–173

    Article  Google Scholar 

  3. 3.

    Peckys DB, de Jonge N (2011) Visualizing gold nanoparticle uptake in live cells with liquid scanning transmission electron microscopy. Nano Lett 11(4):1733–1738

    Article  Google Scholar 

  4. 4.

    Phillips E, Penate-Medina O, Zanzonico PB, Carvajal RD, Mohan P, Ye Y et al (2014) Clinical translation of an ultrasmall inorganic optical-PET imaging nanoparticle probe. Sci Transl Med 6(260):260ra149

    Article  Google Scholar 

  5. 5.

    Lucky SS, Soo KC, Zhang Y (2015) Nanoparticles in photodynamic therapy. Chem Rev 115(4):1990–2042

    Article  Google Scholar 

  6. 6.

    Ma L, Zou X, Chen W (2014) A new X-ray activated nanoparticle photosensitizer for cancer treatment. J Biomed Nanotechnol 10(8):1501–1508

    Article  Google Scholar 

  7. 7.

    FDA approves Celgene drug Abraxane for late-stage pancreatic cancer | CTV News n.d.; Accessed 9 Jan 2018.

  8. 8.

    FDA Approval for Doxorubicin HCl Liposome—National Cancer Institute n.d.; Accessed 9 Jan 2018

  9. 9.

    Gastromark—FDA prescribing information, side effects and uses n.d.; Accessed 9 Jan 2018

  10. 10.

    Connor EE, Mwamuka J, Gole A, Murphy CJ, Wyatt MD (2005) Gold nanoparticles are taken up by human cells but do not cause acute cytotoxicity. Small 1(3):325–327

    Article  Google Scholar 

  11. 11.

    Davis ME, Chen Z (Georgia), Shin DM (2008) Nanoparticle therapeutics: an emerging treatment modality for cancer. Nat Rev Drug Discov 7(9):771–782

  12. 12.

    Bartlett DW, Su H, Hildebrandt IJ, Weber WA, Davis ME (2007) Impact of tumor-specific targeting on the biodistribution and efficacy of siRNA nanoparticles measured by multimodality in vivo imaging. Proc Natl Acad Sci U S A 104(39):15549–15554

    Article  Google Scholar 

  13. 13.

    Eby DM, Luckarift HR, Johnson GR (2009) Hybrid antimicrobial enzyme and silver nanoparticle coatings for medical instruments. ACS Appl Mater Interfaces 1(7):1553–1560

    Article  Google Scholar 

  14. 14.

    De Jong WH, Borm PJA (2008) Drug delivery and nanoparticles: applications and hazards. Int J Nanomedicine 3(2):133–149

    Article  Google Scholar 

  15. 15.

    Altınoğlu Eİ, Adair JH (2010) Near infrared imaging with nanoparticles. Wiley Interdiscip Rev Nanomed Nanobiotechnol 2(5):461–477

    Article  Google Scholar 

  16. 16.

    Medintz IL, Uyeda HT, Goldman ER, Mattoussi H (2005) Quantum dot bioconjugates for imaging, labelling and sensing. Nat Mater 4:435–446

    Article  Google Scholar 

  17. 17.

    Murphy CJ (2002) Optical sensing with quantum dots. Anal Chem 74(19):520A–526A

    Article  Google Scholar 

  18. 18.

    Zhang J, Campbell RE, Ting AY, Tsien RY (2002) Creating new fluorescent probes for cell biology. Nat Rev Mol Cell Biol 3(12):906–918

    Article  Google Scholar 

  19. 19.

    Baptista PV, Doria G, Quaresma P, Cavadas M, Neves CS, Gomes I et al (2011) Nanoparticles in molecular diagnostics. Prog Mol Biol Transl Sci 104:427–488

    Article  Google Scholar 

  20. 20.

    Baetke SC, Lammers T, Kiessling F (2015) Applications of nanoparticles for diagnosis and therapy of cancer. Br J Radiol 88(1054):20150207

    Article  Google Scholar 

  21. 21.

    Mornet S, Vasseur S, Grasset F, Duguet E (2004) Magnetic nanoparticle design for medical diagnosis and therapy. J Mater Chem 14(14):2161

    Article  Google Scholar 

  22. 22.

    Kang S, Herzberg M, Rodrigues DF, Elimelech M. Antibacterial effects of carbon nanotubes: size does matter! Langmuir 2008;24(13):6409–13

  23. 23.

    Muguruma H, Matsui Y, Shibayama Y (2007) Carbon nanotube–plasma polymer-based amperometric biosensors: enzyme-friendly platform for ultrasensitive glucose detection. Jpn J Appl Phys 46(9A):6078–6082

    Article  Google Scholar 

  24. 24.

    Clendenin J, Kim J-W, Tung S. An aligned carbon nanotube biosensor for DNA detection. 2007 2nd IEEE Int. Conf. Nano/Micro Eng. Mol. Syst., IEEE; 2007, p. 1028–1033

  25. 25.

    Timur S, Anik U, Odaci D, Gorton L (2007) Development of a microbial biosensor based on carbon nanotube (CNT) modified electrodes. Electrochem Commun 9(7):1810–1815

    Article  Google Scholar 

  26. 26.

    Kokura S, Handa O, Takagi T, Ishikawa T, Naito Y, Yoshikawa T (2010) Silver nanoparticles as a safe preservative for use in cosmetics. Nanomed Nanotechnol Biol Med. 6(4):570–574

    Article  Google Scholar 

  27. 27.

    Dukhin SS, Labib ME (2013) Convective diffusion of nanoparticles from the epithelial barrier toward regional lymph nodes. Adv Colloid Interf Sci 199–200:23–43

    Article  Google Scholar 

  28. 28.

    Oberdörster G, Maynard A, Donaldson K, Castranova V, Fitzpatrick J, Ausman K et al (2005) Principles for characterizing the potential human health effects from exposure to nanomaterials: elements of a screening strategy. Part Fibre Toxicol. 2(1):8

    Article  Google Scholar 

  29. 29.

    Holsapple MP, Farland WH, Landry TD, Monteiro-Riviere NA, Carter JM, Walker NJ et al (2005) Research strategies for safety evaluation of nanomaterials, part II: toxicological and safety evaluation of nanomaterials, current challenges and data needs. Toxicol Sci 88(1):12–17

    Article  Google Scholar 

  30. 30.

    Hoet PH, Brüske-Hohlfeld I, Salata OV (2004) Nanoparticles—known and unknown health risks. J Nanobiotechnology. 2(1):12

    Article  Google Scholar 

  31. 31.

    Ryman-Rasmussen JP, Riviere JE, Monteiro-Riviere NA (2006) Penetration of intact skin by quantum dots with diverse physicochemical properties. Toxicol Sci 91(1):159–165

    Article  Google Scholar 

  32. 32.

    Schneider M, Stracke F, Hansen S, Schaefer UF (2009) Nanoparticles and their interactions with the dermal barrier. Dermatoendocrinol 1(4):197–206

    Article  Google Scholar 

  33. 33.

    Tinkle SS, Antonini JM, Rich BA, Roberts JR, Salmen R, DePree K et al (2003) Skin as a route of exposure and sensitization in chronic beryllium disease. Environ Health Perspect 111(9):1202–1208

    Article  Google Scholar 

  34. 34.

    Singh R, Lillard JW Jr (2009) Nanoparticle-based targeted drug delivery. Exp Mol Pathol 86(3):215–223

    Article  Google Scholar 

  35. 35.

    Radomski A, Jurasz P, Alonso-Escolano D, Drews M, Morandi M, Malinski T et al (2005) Nanoparticle-induced platelet aggregation and vascular thrombosis. Br J Pharmacol 146(6):882–893

    Article  Google Scholar 

  36. 36.

    Madl AK, Plummer LE, Carosino C, Pinkerton KE (2014) Nanoparticles, lung injury, and the role of oxidant stress. Annu Rev Physiol 76(1):447–465

    Article  Google Scholar 

  37. 37.

    Lucchini RG, Dorman DC, Elder A, Veronesi B (2012) Neurological impacts from inhalation of pollutants and the nose-brain connection. Neurotoxicology 33(4):838–841

    Article  Google Scholar 

  38. 38.

    Zhu M-T, Feng W-Y, Wang Y, Wang B, Wang M, Ouyang H et al (2009) Particokinetics and extrapulmonary translocation of intratracheally instilled ferric oxide nanoparticles in rats and the potential health risk assessment. Toxicol Sci 107(2):342–351

    Article  Google Scholar 

  39. 39.

    Barua S, Mitragotri S (2014) Challenges associated with penetration of nanoparticles across cell and tissue barriers: a review of current status and future prospects. Nano Today 9(2):223–243

    Article  Google Scholar 

  40. 40.

    Nguyen KC, Rippstein P, Tayabali AF, Willmore WG (2015) Mitochondrial toxicity of cadmium telluride quantum dot nanoparticles in mammalian hepatocytes. Toxicol Sci 146(1):31–42

    Article  Google Scholar 

  41. 41.

    Singh BR, Singh BN, Khan W, Singh HB, Naqvi AH (2012) ROS-mediated apoptotic cell death in prostate cancer LNCaP cells induced by biosurfactant stabilized CdS quantum dots. Biomaterials 33(23):5753–5767

    Article  Google Scholar 

  42. 42.

    Ambrosone A, Mattera L, Marchesano V, Quarta A, Susha AS, Tino A et al (2012) Mechanisms underlying toxicity induced by CdTe quantum dots determined in an invertebrate model organism. Biomaterials 33(7):1991–2000

    Article  Google Scholar 

  43. 43.

    Ruenraroengsak P, Novak P, Berhanu D, Thorley AJ, Valsami-Jones E, Gorelik J et al (2012) Respiratory epithelial cytotoxicity and membrane damage (holes) caused by amine-modified nanoparticles. Nanotoxicology 6(1):94–108

    Article  Google Scholar 

  44. 44.

    Wang T, Bai J, Jiang X, Nienhaus GU (2012) Cellular uptake of nanoparticles by membrane penetration: a study combining confocal microscopy with FTIR spectroelectrochemistry. ACS Nano 6(2):1251–1259

    Article  Google Scholar 

  45. 45.

    Mao Z, Xu B, Ji X, Zhou K, Zhang X, Chen M et al (2015) Titanium dioxide nanoparticles alter cellular morphology via disturbing the microtubule dynamics. Nano 7(18):8466–8475

    Google Scholar 

  46. 46.

    Wu X, Tan Y, Mao H, Zhang M (2010) Toxic effects of iron oxide nanoparticles on human umbilical vein endothelial cells. Int J Nanomedicine 5:385–399

    Article  Google Scholar 

  47. 47.

    Walkey CD, Olsen JB, Guo H, Emili A, Chan WCW (2012) Nanoparticle size and surface chemistry determine serum protein adsorption and macrophage uptake. J Am Chem Soc 134(4):2139–2147

    Article  Google Scholar 

  48. 48.

    Kostura L, Kraitchman DL, Mackay AM, Pittenger MF, Bulte JWM (2004) Feridex labeling of mesenchymal stem cells inhibits chondrogenesis but not adipogenesis or osteogenesis. NMR Biomed 17(7):513–517

    Article  Google Scholar 

  49. 49.

    Chen Y-C, Hsiao J-K, Liu H-M, Lai I-Y, Yao M, Hsu S-C et al (2010) The inhibitory effect of superparamagnetic iron oxide nanoparticle (Ferucarbotran) on osteogenic differentiation and its signaling mechanism in human mesenchymal stem cells. Toxicol Appl Pharmacol 245(2):272–279

    Article  Google Scholar 

  50. 50.

    Kedziorek DA, Muja N, Walczak P, Ruiz-Cabello J, Gilad AA, Jie CC et al (2010) Gene expression profiling reveals early cellular responses to intracellular magnetic labeling with superparamagnetic iron oxide nanoparticles. Magn Reson Med 63(4):1031–1043

    Article  Google Scholar 

  51. 51.

    Puppi J, Mitry RR, Modo M, Dhawan A, Raja K, Hughes RD (2011) Use of a clinically approved iron oxide MRI contrast agent to label human hepatocytes. Cell Transplant 20(6):963–976

    Article  Google Scholar 

  52. 52.

    Wang L, Hu C, Shao L (2017) The antimicrobial activity of nanoparticles: present situation and prospects for the future. Int J Nanomedicine 12:1227–1249

    Article  Google Scholar 

  53. 53.

    Poirier M, Simard J-C, Antoine F, Girard D (2014) Interaction between silver nanoparticles of 20 nm (AgNP20 ) and human neutrophils: induction of apoptosis and inhibition of de novo protein synthesis by AgNP20 aggregates. J Appl Toxicol 34(4):404–412

    Article  Google Scholar 

  54. 54.

    Choi S-J, Oh J-M, Choy J-H (2009) Toxicological effects of inorganic nanoparticles on human lung cancer A549 cells. J Inorg Biochem 103(3):463–471

    Article  Google Scholar 

  55. 55.

    Park E-J, Park K (2009) Oxidative stress and pro-inflammatory responses induced by silica nanoparticles in vivo and in vitro. Toxicol Lett 184(1):18–25

    Article  Google Scholar 

  56. 56.

    Lévy M, Lagarde F, Maraloiu V-A, Blanchin M-G, Gendron F, Wilhelm C et al (2010) Degradability of superparamagnetic nanoparticles in a model of intracellular environment: follow-up of magnetic, structural and chemical properties. Nanotechnology 21(39):395103

    Article  Google Scholar 

  57. 57.

    Liu J, Katahara J, Li G, Coe-Sullivan S, Hurt RH (2012) Degradation products from consumer nanocomposites: a case study on quantum dot lighting. Environ Sci Technol. 46(6):3220–3227

    Article  Google Scholar 

  58. 58.

    Oh E, Liu R, Nel A, Gemill KB, Bilal M, Cohen Y et al (2016) Meta-analysis of cellular toxicity for cadmium-containing quantum dots. Nat Nanotechnol 11(5):479–486

    Article  Google Scholar 

  59. 59.

    Huo S, Jin S, Ma X, Xue X, Yang K, Kumar A et al (2014) Ultrasmall gold nanoparticles as carriers for nucleus-based gene therapy due to size-dependent nuclear entry. ACS Nano 8(6):5852–5862

    Article  Google Scholar 

  60. 60.

    Pan Y, Neuss S, Leifert A, Fischler M, Wen F, Simon U et al (2007) Size-dependent cytotoxicity of gold nanoparticles. Small 3(11):1941–1949

    Article  Google Scholar 

  61. 61.

    Soenen SJ, Rivera-Gil P, Montenegro J-M, Parak WJ, De Smedt SC, Braeckmans K (2011) Cellular toxicity of inorganic nanoparticles: common aspects and guidelines for improved nanotoxicity evaluation. Nano Today 6(5):446–465

    Article  Google Scholar 

  62. 62.

    Schmid G (2008) The relevance of shape and size of Au55 clusters. Chem Soc Rev 37(9):1909–1930

    Article  Google Scholar 

  63. 63.

    Zhang S, Gao H, Bao G (2015) Physical principles of nanoparticle cellular endocytosis. ACS Nano 9(9):8655–8671

    Article  Google Scholar 

  64. 64.

    Nel A, Xia T, Mädler L, Li N (2006) Toxic potential of materials at the nanolevel. Science 311(5761):622–627

    Article  Google Scholar 

  65. 65.

    De Jong WH, Hagens WI, Krystek P, Burger MC, Sips AJAM, Geertsma RE (2008) Particle size-dependent organ distribution of gold nanoparticles after intravenous administration. Biomaterials 29(12):1912–1919

    Article  Google Scholar 

  66. 66.

    Talamini L, Violatto MB, Cai Q, Monopoli MP, Kantner K, Krpetić Ž et al (2017) Influence of size and shape on the anatomical distribution of endotoxin-free gold nanoparticles. ACS Nano 11(6):5519–5529

    Article  Google Scholar 

  67. 67.

    Zhao Y, Sun X, Zhang G, Trewyn BG, Slowing II, Lin VS-Y (2011) Interaction of mesoporous silica nanoparticles with human red blood cell membranes: size and surface effects. ACS Nano 5(2):1366–1375

    Article  Google Scholar 

  68. 68.

    Kong B, Seog JH, Graham LM, Lee SB (2011) Experimental considerations on the cytotoxicity of nanoparticles. Nanomedicine (Lond) 6(5):929–941

    Article  Google Scholar 

  69. 69.

    Ispas C, Andreescu D, Patel A, Goia DV, Andreescu S, Wallace KN (2009) Toxicity and developmental defects of different sizes and shape nickel nanoparticles in zebrafish. Environ Sci Technol. 43(16):6349–6356

    Article  Google Scholar 

  70. 70.

    Favi PM, Gao M, Johana Sepúlveda Arango L, Ospina SP, Morales M, Pavon JJ et al (2015) Shape and surface effects on the cytotoxicity of nanoparticles: gold nanospheres versus gold nanostars. J Biomed Mater Res A 103(11):3449–3462

    Article  Google Scholar 

  71. 71.

    Hamilton RF, Wu N, Porter D, Buford M, Wolfarth M, Holian A (2009) Particle length-dependent titanium dioxide nanomaterials toxicity and bioactivity. Part Fibre Toxicol. 6(1):35

    Article  Google Scholar 

  72. 72.

    Champion JA, Mitragotri S (2006) Role of target geometry in phagocytosis. Proc Natl Acad Sci U S A 103(13):4930–4934

    Article  Google Scholar 

  73. 73.

    Park KH, Chhowalla M, Iqbal Z, Sesti F (2003) Single-walled carbon nanotubes are a new class of ion channel blockers. J Biol Chem 278(50):50212–50216

    Article  Google Scholar 

  74. 74.

    Zhao X, Ng S, Heng BC, Guo J, Ma L, Tan TTY et al (2013) Cytotoxicity of hydroxyapatite nanoparticles is shape and cell dependent. Arch Toxicol 87(6):1037–1052

    Article  Google Scholar 

  75. 75.

    Hu W, Peng C, Lv M, Li X, Zhang Y, Chen N et al (2011) Protein corona-mediated mitigation of cytotoxicity of graphene oxide. ACS Nano 5(5):3693–3700

    Article  Google Scholar 

  76. 76.

    Yang H, Liu C, Yang D, Zhang H, Xi Z (2009) Comparative study of cytotoxicity, oxidative stress and genotoxicity induced by four typical nanomaterials: the role of particle size, shape and composition. J Appl Toxicol 29(1):69–78

    Article  Google Scholar 

  77. 77.

    Soenen SJ, Parak WJ, Rejman J, Manshian B (2015) (Intra)cellular stability of inorganic nanoparticles: effects on cytotoxicity, particle functionality, and biomedical applications. Chem Rev 115(5):2109–2135

    Article  Google Scholar 

  78. 78.

    Gurr J-R, Wang ASS, Chen C-H, Jan K-Y (2005) Ultrafine titanium dioxide particles in the absence of photoactivation can induce oxidative damage to human bronchial epithelial cells. Toxicology 213(1–2):66–73

    Article  Google Scholar 

  79. 79.

    Zhang H, Gilbert B, Huang F, Banfield JF (2003) Water-driven structure transformation in nanoparticles at room temperature. Nature 424(6952):1025–1029

    Article  Google Scholar 

  80. 80.

    Schaeublin NM, Braydich-Stolle LK, Schrand AM, Miller JM, Hutchison J, Schlager JJ et al (2011) Surface charge of gold nanoparticles mediates mechanism of toxicity. Nano 3(2):410–420

    Google Scholar 

  81. 81.

    El Badawy AM, Silva RG, Morris B, Scheckel KG, Suidan MT, Tolaymat TM (2011) Surface charge-dependent toxicity of silver nanoparticles. Environ Sci Technol 45(1):283–287

    Article  Google Scholar 

  82. 82.

    Zhang Y, Kohler N, Zhang M (2002) Surface modification of superparamagnetic magnetite nanoparticles and their intracellular uptake. Biomaterials 23(7):1553–1561

    Article  Google Scholar 

  83. 83.

    Cheyne RW, Smith TA, Trembleau L, McLaughlin AC (2011) Synthesis and characterisation of biologically compatible TiO2 nanoparticles. Nanoscale Res Lett 6(1):423

    Article  Google Scholar 

  84. 84.

    Kango S, Kalia S, Celli A, Njuguna J, Habibi Y, Kumar R (2013) Surface modification of inorganic nanoparticles for development of organic–inorganic nanocomposites—a review. Prog Polym Sci 38(8):1232–1261

    Article  Google Scholar 

  85. 85.

    Liu Y, Li W, Lao F, Liu Y, Wang L, Bai R et al (2011) Intracellular dynamics of cationic and anionic polystyrene nanoparticles without direct interaction with mitotic spindle and chromosomes. Biomaterials 32(32):8291–8303

    Article  Google Scholar 

  86. 86.

    Hühn D, Kantner K, Geidel C, Brandholt S, De Cock I, Soenen SJH et al (2013) Polymer-coated nanoparticles interacting with proteins and cells: focusing on the sign of the net charge. ACS Nano 7(4):3253–3263

    Article  Google Scholar 

  87. 87.

    Alexis F, Pridgen E, Molnar LK, Farokhzad OC (2008) Factors affecting the clearance and biodistribution of polymeric nanoparticles. Mol Pharm 5(4):505–515

    Article  Google Scholar 

  88. 88.

    Lundqvist M, Stigler J, Elia G, Lynch I, Cedervall T, Dawson KA (2008) Nanoparticle size and surface properties determine the protein corona with possible implications for biological impacts. Proc Natl Acad Sci U S A 105(38):14265–14270

    Article  Google Scholar 

  89. 89.

    Gunawan C, Lim M, Marquis CP, Amal R (2014) Nanoparticle–protein corona complexes govern the biological fates and functions of nanoparticles. J Mater Chem B 2(15):2060

    Article  Google Scholar 

  90. 90.

    Sukhanova A, Poly S, Shemetov A, Nabiev IR. Quantum dots induce charge-specific amyloid-like fibrillation of insulin at physiological conditions. In: Choi SH, Choy J-H, Lee U, Varadan VK, editors. vol. 8548, International Society for Optics and Photonics; 2012, p. 85485F

  91. 91.

    Linse S, Cabaleiro-Lago C, Xue W-F, Lynch I, Lindman S, Thulin E et al (2007) Nucleation of protein fibrillation by nanoparticles. Proc Natl Acad Sci U S A 104(21):8691–8696

    Article  Google Scholar 

  92. 92.

    Xu P, Van Kirk EA, Zhan Y, Murdoch WJ, Radosz M, Shen Y (2007) Targeted charge-reversal nanoparticles for nuclear drug delivery. Angew Chemie Int Ed 46(26):4999–5002

    Article  Google Scholar 

  93. 93.

    Asati A, Santra S, Kaittanis C, Perez JM (2010) Surface-charge-dependent cell localization and cytotoxicity of cerium oxide nanoparticles. ACS Nano 4(9):5321–5331

    Article  Google Scholar 

  94. 94.

    Arami H, Khandhar A, Liggitt D, Krishnan KM (2015) In vivo delivery, pharmacokinetics, biodistribution and toxicity of iron oxide nanoparticles. Chem Soc Rev 44(23):8576–8607

    Article  Google Scholar 

  95. 95.

    Zhang T, Hu Y, Tang M, Kong L, Ying J, Wu T et al (2015) Liver toxicity of cadmium telluride quantum dots (CdTe QDs) due to oxidative stress in vitro and in vivo. Int J Mol Sci 16(10):23279–23299

    Article  Google Scholar 

  96. 96.

    Xia T, Li N, Nel AE (2009) Potential health impact of nanoparticles. Annu Rev Public Health 30(1):137–150

    Article  Google Scholar 

  97. 97.

    Peng L, He M, Chen B, Wu Q, Zhang Z, Pang D et al (2013) Cellular uptake, elimination and toxicity of CdSe/ZnS quantum dots in HepG2 cells. Biomaterials 34(37):9545–9558

    Article  Google Scholar 

  98. 98.

    Cho J, Kushiro K, Teramura Y, Takai M (2014) Lectin-tagged fluorescent polymeric nanoparticles for targeting of sialic acid on living cells. Biomacromolecules 15(6):2012–2018

    Article  Google Scholar 

  99. 99.

    Gregory AE, Titball R, Williamson D (2013) Vaccine delivery using nanoparticles. Front Cell Infect Microbiol 3:13

    Article  Google Scholar 

  100. 100.

    Guo G, Liu W, Liang J, He Z, Xu H, Yang X (2007) Probing the cytotoxicity of CdSe quantum dots with surface modification. Mater Lett 61(8–9):1641–1644

    Article  Google Scholar 

  101. 101.

    Hardman R (2006) A toxicologic review of quantum dots: toxicity depends on physicochemical and environmental factors. Environ Health Perspect 114(2):165–172

    Article  Google Scholar 

  102. 102.

    Huang J, Wang L, Lin R, Wang AY, Yang L, Kuang M et al (2013) Casein-coated iron oxide nanoparticles for high MRI contrast enhancement and efficient cell targeting. ACS Appl Mater Interfaces 5(11):4632–4639

    Article  Google Scholar 

  103. 103.

    Donaldson K, Stone V, Tran CL, Kreyling W, Borm PJA (2004) Nanotoxicology. Occup Environ Med 61(9):727–728

    Article  Google Scholar 

  104. 104.

    Bouwmeester H, Poortman J, Peters RJ, Wijma E, Kramer E, Makama S et al (2011) Characterization of translocation of silver nanoparticles and effects on whole-genome gene expression using an in vitro intestinal epithelium coculture model. ACS Nano 5(5):4091–4103

    Article  Google Scholar 

  105. 105.

    Brandenberger C, Rothen-Rutishauser B, Mühlfeld C, Schmid O, Ferron GA, Maier KL et al (2010) Effects and uptake of gold nanoparticles deposited at the air-liquid interface of a human epithelial airway model. Toxicol Appl Pharmacol 242(1):56–65

    Article  Google Scholar 

  106. 106.

    Sriram G, Bigliardi PL, Bigliardi-Qi M (2015) Fibroblast heterogeneity and its implications for engineering organotypic skin models in vitro. Eur J Cell Biol 94(11):483–512

    Article  Google Scholar 

  107. 107.

    Abbott A (2003) Cell culture: biology’s new dimension. Nature 424(6951):870–872

    Article  Google Scholar 

  108. 108.

    Lee J, Cuddihy MJ, Kotov NA (2008) Three-dimensional cell culture matrices: state of the art. Tissue Eng Part B Rev 14(1):61–86

    Article  Google Scholar 

  109. 109.

    Kuhn SJ, Hallahan DE, Giorgio TD (2006) Characterization of superparamagnetic nanoparticle interactions with extracellular matrix in an in vitro system. Ann Biomed Eng 34(1):51–58

    Article  Google Scholar 

  110. 110.

    Li XJ, Valadez AV, Zuo P, Nie Z (2012) Microfluidic 3D cell culture: potential application for tissue-based bioassays. Bioanalysis 4(12):1509–1525

    Article  Google Scholar 

  111. 111.

    Lee J, Lilly GD, Doty RC, Podsiadlo P, Kotov NA. In vitro toxicity testing of nanoparticles in 3D cell culture. Small. 2009;5(10):NA-NA

  112. 112.

    Fabian E, Landsiedel R, Ma-Hock L, Wiench K, Wohlleben W, van Ravenzwaay B (2008) Tissue distribution and toxicity of intravenously administered titanium dioxide nanoparticles in rats. Arch Toxicol 82(3):151–157

    Article  Google Scholar 

  113. 113.

    Recordati C, De Maglie M, Bianchessi S, Argentiere S, Cella C, Mattiello S, et al. Tissue distribution and acute toxicity of silver after single intravenous administration in mice: nano-specific and size-dependent effects. Part Fibre Toxicol. 2016;13(1).

  114. 114.

    Asare N, Duale N, Slagsvold HH, Lindeman B, Olsen AK, Gromadzka-Ostrowska J et al (2016) Genotoxicity and gene expression modulation of silver and titanium dioxide nanoparticles in mice. Nanotoxicology 10(3):312–321

    Article  Google Scholar 

  115. 115.

    Zhang X-D, Wu H-Y, Wu D, Wang Y-Y, Chang J-H, Zhai Z-B et al (2010) Toxicologic effects of gold nanoparticles in vivo by different administration routes. Int J Nanomedicine 5:771–781

    Article  Google Scholar 

  116. 116.

    Kwon J, Kim J, Park S, Khang G, Kang PM, Lee D (2013) Inflammation-responsive antioxidant nanoparticles based on a polymeric prodrug of vanillin. Biomacromolecules 14(5):1618–1626

    Article  Google Scholar 

  117. 117.

    Narayanan D, Geena MG, Lakshmi H, Koyakutty M, Nair S, Menon D (2013) Poly-(ethylene glycol) modified gelatin nanoparticles for sustained delivery of the anti-inflammatory drug ibuprofen-sodium: an in vitro and in vivo analysis. Nanomed Nanotechnol Biol Med. 9(6):818–828

    Article  Google Scholar 

  118. 118.

    Hauck TS, Anderson RE, Fischer HC, Newbigging S, Chan WCW (2010) In vivo quantum-dot toxicity assessment. Small 6(1):138–144

    Article  Google Scholar 

  119. 119.

    Haque MM, Im H-Y, Seo J-E, Hasan M, Woo K, Kwon O-S (2013) Acute toxicity and tissue distribution of CdSe/CdS-MPA quantum dots after repeated intraperitoneal injection to mice. J Appl Toxicol 33(9):940–950

    Article  Google Scholar 

  120. 120.

    Chen N, He Y, Su Y, Li X, Huang Q, Wang H et al (2012) The cytotoxicity of cadmium-based quantum dots. Biomaterials 33(5):1238–1244

    Article  Google Scholar 

  121. 121.

    Nagy A, Hollingsworth JA, Hu B, Steinbrück A, Stark PC, Rios Valdez C et al (2013) Functionalization-dependent induction of cellular survival pathways by CdSe quantum dots in primary normal human bronchial epithelial cells. ACS Nano 7(10):8397–8411

    Article  Google Scholar 

  122. 122.

    Zhan Q, Tang M (2014) Research advances on apoptosis caused by quantum dots. Biol Trace Elem Res 161(1):3–12

    Article  Google Scholar 

  123. 123.

    Yong K-T, Law W-C, Hu R, Ye L, Liu L, Swihart MT et al (2013) Nanotoxicity assessment of quantum dots: from cellular to primate studies. Chem Soc Rev 42(3):1236–1250

    Article  Google Scholar 

  124. 124.

    Fitzpatrick JAJ, Andreko SK, Ernst LA, Waggoner AS, Ballou B, Bruchez MP (2009) Long-term persistence and spectral blue shifting of quantum dots in vivo. Nano Lett 9(7):2736–2741

    Article  Google Scholar 

  125. 125.

    Yang RSH, Chang LW, Wu J-P, Tsai M-H, Wang H-J, Kuo Y-C et al (2007) Persistent tissue kinetics and redistribution of nanoparticles, quantum dot 705, in mice: ICP-MS quantitative assessment. Environ Health Perspect 115(9):1339–1343

    Article  Google Scholar 

  126. 126.

    Liu N, Mu Y, Chen Y, Sun H, Han S, Wang M et al (2013) Degradation of aqueous synthesized CdTe/ZnS quantum dots in mice: differential blood kinetics and biodistribution of cadmium and tellurium. Part Fibre Toxicol. 10:37

    Article  Google Scholar 

  127. 127.

    Ballou B, Lagerholm BC, Ernst LA, Bruchez MP, Waggoner AS (2004) Noninvasive imaging of quantum dots in mice. Bioconjug Chem 15(1):79–86

    Article  Google Scholar 

  128. 128.

    Larson DR, Zipfel WR, Williams RM, Clark SW, Bruchez MP, Wise FW et al (2003) Water-soluble quantum dots for multiphoton fluorescence imaging in vivo. Science 300(5624):1434–1436

    Article  Google Scholar 

  129. 129.

    Hu R, Law W-C, Lin G, Ye L, Liu J, Liu J et al (2012) PEGylated phospholipid micelle-encapsulated near-infrared PbS quantum dots for in vitro and in vivo bioimaging. Theranostics 2(7):723–733

    Article  Google Scholar 

  130. 130.

    Pons T, Pic E, Lequeux N, Cassette E, Bezdetnaya L, Guillemin F et al (2010) Cadmium-free CuInS2/ZnS quantum dots for sentinel lymph node imaging with reduced toxicity. ACS Nano 4(5):2531–2538

    Article  Google Scholar 

  131. 131.

    Erogbogbo F, Yong K-T, Roy I, Hu R, Law W-C, Zhao W et al (2011) In vivo targeted cancer imaging, sentinel lymph node mapping and multi-channel imaging with biocompatible silicon nanocrystals. ACS Nano 5(1):413–423

    Article  Google Scholar 

  132. 132.

    Wang F, Yu L, Monopoli MP, Sandin P, Mahon E, Salvati A et al (2013) The biomolecular corona is retained during nanoparticle uptake and protects the cells from the damage induced by cationic nanoparticles until degraded in the lysosomes. Nanomedicine 9(8):1159–1168

    Article  Google Scholar 

  133. 133.

    Aggarwal P, Hall JB, McLeland CB, Dobrovolskaia MA, McNeil SE (2009) Nanoparticle interaction with plasma proteins as it relates to particle biodistribution, biocompatibility and therapeutic efficacy. Adv Drug Deliv Rev 61(6):428–437

    Article  Google Scholar 

  134. 134.

    Zyuzin MV, Yan Y, Hartmann R, Gause KT, Nazarenus M, Cui J et al (2017) Role of the protein corona derived from human plasma in cellular interactions between nanoporous human serum albumin particles and endothelial cells. Bioconjug Chem 28(8):2062–2068

    Article  Google Scholar 

  135. 135.

    Zhang Y, Zhang Y, Hong G, He W, Zhou K, Yang K et al (2013) Biodistribution, pharmacokinetics and toxicology of Ag2S near-infrared quantum dots in mice. Biomaterials 34(14):3639–3646

    Article  Google Scholar 

  136. 136.

    Abbott Chalew TE, Schwab KJ (2013) Toxicity of commercially available engineered nanoparticles to Caco-2 and SW480 human intestinal epithelial cells. Cell Biol Toxicol 29(2):101–116

    Article  Google Scholar 

  137. 137.

    Bannunah AM, Vllasaliu D, Lord J, Stolnik S (2014) Mechanisms of nanoparticle internalization and transport across an intestinal epithelial cell model: effect of size and surface charge. Mol Pharm 11(12):4363–4373

    Article  Google Scholar 

  138. 138.

    Piret J-P, Vankoningsloo S, Mejia J, Noël F, Boilan E, Lambinon F et al (2012) Differential toxicity of copper (II) oxide nanoparticles of similar hydrodynamic diameter on human differentiated intestinal Caco-2 cell monolayers is correlated in part to copper release and shape. Nanotoxicology 6(7):789–803

    Article  Google Scholar 

  139. 139.

    Koeneman BA, Zhang Y, Hristovski K, Westerhoff P, Chen Y, Crittenden JC et al (2009) Experimental approach for an in vitro toxicity assay with non-aggregated quantum dots. Toxicol in Vitro 23(5):955–962

    Article  Google Scholar 

  140. 140.

    Gerloff K, Albrecht C, Boots AW, Förster I, Schins RPF (2009) Cytotoxicity and oxidative DNA damage by nanoparticles in human intestinal Caco-2 cells. Nanotoxicology 3(4):355–364

    Article  Google Scholar 

  141. 141.

    Alkilany AM, Nagaria PK, Hexel CR, Shaw TJ, Murphy CJ, Wyatt MD (2009) Cellular uptake and cytotoxicity of gold nanorods: molecular origin of cytotoxicity and surface effects. Small 5(6):701–708

    Article  Google Scholar 

  142. 142.

    Wang L, Nagesha DK, Selvarasah S, Dokmeci MR, Carrier RL (2008) Toxicity of CdSe nanoparticles in Caco-2 cell cultures. J Nanobiotechnology 6(1):11

    Article  Google Scholar 

  143. 143.

    Jos A, Pichardo S, Puerto M, Sánchez E, Grilo A, Cameán AM (2009) Cytotoxicity of carboxylic acid functionalized single wall carbon nanotubes on the human intestinal cell line Caco-2. Toxicol in Vitro 23(8):1491–1496

    Article  Google Scholar 

  144. 144.

    Thubagere A, Reinhard BM (2010) Nanoparticle-induced apoptosis propagates through hydrogen-peroxide-mediated bystander killing: insights from a human intestinal epithelium in vitro model. ACS Nano 4(7):3611–3622

    Article  Google Scholar 

  145. 145.

    Rhoads LS, Silkworth WT, Roppolo ML, Whittingham MS (2010) Cytotoxicity of nanostructured vanadium oxide on human cells in vitro. Toxicol in Vitro 24(1):292–296

    Article  Google Scholar 

  146. 146.

    Häfeli UO, Riffle JS, Harris-Shekhawat L, Carmichael-Baranauskas A, Mark F, Dailey JP et al (2009) Cell uptake and in vitro toxicity of magnetic nanoparticles suitable for drug delivery. Mol Pharm 6(5):1417–1428

    Article  Google Scholar 

  147. 147.

    Freese C, Schreiner D, Anspach L, Bantz C, Maskos M, Unger RE et al (2014) In vitro investigation of silica nanoparticle uptake into human endothelial cells under physiological cyclic stretch. Part Fibre Toxicol. 11(1):68

    Article  Google Scholar 

  148. 148.

    Feng W, Nie W, Cheng Y, Zhou X, Chen L, Qiu K et al (2015) In vitro and in vivo toxicity studies of copper sulfide nanoplates for potential photothermal applications. Nanomed Nanotechnol Biol Med 11(4):901–912

    Article  Google Scholar 

  149. 149.

    Sun D, Liu Y, Yu Q, Zhou Y, Zhang R, Chen X et al (2013) The effects of luminescent ruthenium(II) polypyridyl functionalized selenium nanoparticles on bFGF-induced angiogenesis and AKT/ERK signaling. Biomaterials 34(1):171–180

    Article  Google Scholar 

  150. 150.

    Choi J, Reipa V, Hitchins VM, Goering PL, Malinauskas RA (2011) Physicochemical characterization and in vitro hemolysis evaluation of silver nanoparticles. Toxicol Sci 123(1):133–143

    Article  Google Scholar 

  151. 151.

    Ashokan A, Chandran P, Sadanandan AR, Koduri CK, Retnakumari AP, Menon D et al (2012) Development and haematotoxicological evaluation of doped hydroxyapatite based multimodal nanocontrast agent for near-infrared, magnetic resonance and X-ray contrast imaging. Nanotoxicology 6(6):652–666

    Article  Google Scholar 

  152. 152.

    Xia Y, Li M, Peng T, Zhang W, Xiong J, Hu Q et al (2013) In vitro cytotoxicity of fluorescent silica nanoparticles hybridized with aggregation-induced emission luminogens for living cell imaging. Int J Mol Sci 14(1):1080–1092

    Article  Google Scholar 

  153. 153.

    Yan M, Zhang Y, Xu K, Fu T, Qin H, Zheng X (2011) An in vitro study of vascular endothelial toxicity of CdTe quantum dots. Toxicology 282(3):94–103

    Article  Google Scholar 

  154. 154.

    Rizvi SB, Rouhi S, Taniguchi S, Yang SY, Green M, Keshtgar M et al (2014) Near-infrared quantum dots for HER2 localization and imaging of cancer cells. Int J Nanomedicine 9:1323–1337

    Google Scholar 

  155. 155.

    Xie Y, Williams NG, Tolic A, Chrisler WB, Teeguarden JG, Maddux BLS et al (2012) Aerosolized ZnO nanoparticles induce toxicity in alveolar type II epithelial cells at the air-liquid interface. Toxicol Sci 125(2):450–461

    Article  Google Scholar 

  156. 156.

    Lanone S, Rogerieux F, Geys J, Dupont A, Maillot-Marechal E, Boczkowski J et al (2009) Comparative toxicity of 24 manufactured nanoparticles in human alveolar epithelial and macrophage cell lines. Part Fibre Toxicol. 6(1):14

    Article  Google Scholar 

  157. 157.

    Hanagata N, Zhuang F, Connolly S, Li J, Ogawa N, Xu M (2011) Molecular responses of human lung epithelial cells to the toxicity of copper oxide nanoparticles inferred from whole genome expression analysis. ACS Nano 5(12):9326–9338

    Article  Google Scholar 

  158. 158.

    Murphy FA, Schinwald A, Poland CA, Donaldson K (2012) The mechanism of pleural inflammation by long carbon nanotubes: interaction of long fibres with macrophages stimulates them to amplify pro-inflammatory responses in mesothelial cells. Part Fibre Toxicol 9(1):8

    Article  Google Scholar 

  159. 159.

    Nagy A, Steinbrück A, Gao J, Doggett N, Hollingsworth JA, Iyer R (2012) Comprehensive analysis of the effects of CdSe quantum dot size, surface charge, and functionalization on primary human lung cells. ACS Nano 6(6):4748–4762

    Article  Google Scholar 

  160. 160.

    Guadagnini R, Moreau K, Hussain S, Marano F, Boland S. Toxicity evaluation of engineered nanoparticles for medical applications using pulmonary epithelial cells. Nanotoxicology. 2015;9 Suppl 1(sup1):25–32

  161. 161.

    Manshian BB, Soenen SJ, Al-Ali A, Brown A, Hondow N, Wills J et al (2015) Cell type-dependent changes in CdSe/ZnS quantum dot uptake and toxic endpoints. Toxicol Sci 144(2):246–258

    Article  Google Scholar 

  162. 162.

    Brunetti V, Chibli H, Fiammengo R, Galeone A, Malvindi MA, Vecchio G et al (2013) InP/ZnS as a safer alternative to CdSe/ZnS core/shell quantum dots: in vitro and in vivo toxicity assessment. Nano 5(1):307–317

    Google Scholar 

  163. 163.

    Orlowski P, Krzyzowska M, Zdanowski R, Winnicka A, Nowakowska J, Stankiewicz W et al (2013) Assessment of in vitro cellular responses of monocytes and keratinocytes to tannic acid modified silver nanoparticles. Toxicol in Vitro 27(6):1798–1808

    Article  Google Scholar 

  164. 164.

    Stępnik M, Arkusz J, Smok-Pieniążek A, Bratek-Skicki A, Salvati A, Lynch I et al (2012) Cytotoxic effects in 3T3-L1 mouse and WI-38 human fibroblasts following 72 hour and 7 day exposures to commercial silica nanoparticles. Toxicol Appl Pharmacol 263(1):89–101

    Article  Google Scholar 

  165. 165.

    Jeong SH, Kim HJ, Ryu HJ, Ryu WI, Park Y-H, Bae HC et al (2013) ZnO nanoparticles induce TNF-α expression via ROS-ERK-Egr-1 pathway in human keratinocytes. J Dermatol Sci 72(3):263–273

    Article  Google Scholar 

  166. 166.

    Vankoningsloo S, Piret J-P, Saout C, Noel F, Mejia J, Zouboulis CC et al (2010) Cytotoxicity of multi-walled carbon nanotubes in three skin cellular models: effects of sonication, dispersive agents and corneous layer of reconstructed epidermis. Nanotoxicology 4(1):84–97

    Article  Google Scholar 

  167. 167.

    Kocbek P, Teskac K, Kreft ME, Kristl J. Toxicological aspects of long-term treatment of keratinocytes with ZnO and TiO2 nanoparticles. Small 2010;6(17):1908–17

  168. 168.

    Zhang LW, Yu WW, Colvin VL, Monteiro-Riviere NA (2008) Biological interactions of quantum dot nanoparticles in skin and in human epidermal keratinocytes. Toxicol Appl Pharmacol 228(2):200–211

    Article  Google Scholar 

  169. 169.

    Guller AE, Generalova AN, Petersen EV, Nechaev AV, Trusova IA, Landyshev NN et al (2015) Cytotoxicity and non-specific cellular uptake of bare and surface-modified upconversion nanoparticles in human skin cells. Nano Res 8(5):1546–1562

    Article  Google Scholar 

  170. 170.

    Shukla RK, Sharma V, Pandey AK, Singh S, Sultana S, Dhawan A (2011) ROS-mediated genotoxicity induced by titanium dioxide nanoparticles in human epidermal cells. Toxicol in Vitro 25(1):231–241

    Article  Google Scholar 

  171. 171.

    Mukherjee SP, Davoren M, Byrne HJ (2010) In vitro mammalian cytotoxicological study of PAMAM dendrimers—towards quantitative structure activity relationships. Toxicol in Vitro 24(1):169–177

    Article  Google Scholar 

  172. 172.

    Peuschel H, Sydlik U, Haendeler J, Büchner N, Stöckmann D, Kroker M, et al. (2010) c-Src-mediated activation of Erk1/2 is a reaction of epithelial cells to carbon nanoparticle treatment and may be a target for a molecular preventive strategy. Biol Chem 391(11):1327–1332.

    Article  Google Scholar 

  173. 173.

    Tsoi KM, Dai Q, Alman BA, Chan WCW (2013) Are quantum dots toxic? Exploring the discrepancy between cell culture and animal studies. Acc Chem Res 46(3):662–671

    Article  Google Scholar 

  174. 174.

    Zanganeh S, Spitler R, Erfanzadeh M, Alkilany AM, Mahmoudi M (2016) Protein corona: opportunities and challenges. Int J Biochem Cell Biol 75:143–147

    Article  Google Scholar 

Download references


The authors thank Vladimir Ushakov for proofreading the manuscript.


This study was supported by the Ministry of Education and Science of the Russian Federation, State Contract no. 16.1034.2017/ ПЧ.

Availability of data and materials

The datasets generated during and/or analyzed during the current study are available from the corresponding authors on reasonable request.

Author information




IN and AS defined the topic of review and selected the key publications. All authors wrote different parts of the manuscript. All authors commented on the manuscript. All authors read and approved the final manuscript.

Corresponding authors

Correspondence to Alyona Sukhanova or Igor Nabiev.

Ethics declarations

Competing interests

The authors declare that they have no competing interests.

Publisher’s Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Rights and permissions

Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 International License (, which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Sukhanova, A., Bozrova, S., Sokolov, P. et al. Dependence of Nanoparticle Toxicity on Their Physical and Chemical Properties. Nanoscale Res Lett 13, 44 (2018).

Download citation

  • Received:

  • Accepted:

  • Published:

  • DOI:


  • Nanoparticles
  • Quantum dots
  • Nanotoxicity
  • Surface chemistry
  • Theranostics
  • Imaging