- Open Access
Cytotoxicity and cellular uptake of tri-block copolymer nanoparticles with different size and surface characteristics
© Bhattacharjee et al.; licensee BioMed Central Ltd. 2012
- Received: 31 January 2012
- Accepted: 30 April 2012
- Published: 30 April 2012
Polymer nanoparticles (PNP) are becoming increasingly important in nanomedicine and food-based applications. Size and surface characteristics are often considered to be important factors in the cellular interactions of these PNP, although systematic investigations on the role of surface properties on cellular interactions and toxicity of PNP are scarce.
Fluorescent, monodisperse tri-block copolymer nanoparticles with different sizes (45 and 90 nm) and surface charges (positive and negative) were synthesized, characterized and studied for uptake and cytotoxicity in NR8383 and Caco-2 cells. All types of PNP were taken up by the cells. The positive smaller PNP45 (45 nm) showed a higher cytotoxicity compared to the positive bigger PNP90 (90 nm) particles including reduction in mitochondrial membrane potential (ΔΨm), induction of reactive oxygen species (ROS) production, ATP depletion and TNF-α release. The negative PNP did not show any cytotoxic effect. Reduction in mitochondrial membrane potential (ΔΨm), uncoupling of the electron transfer chain in mitochondria and the resulting ATP depletion, induction of ROS and oxidative stress may all play a role in the possible mode of action for the cytotoxicity of these PNP. The role of receptor-mediated endocytosis in the intracellular uptake of different PNP was studied by confocal laser scanning microscopy (CLSM). Involvement of size and charge in the cellular uptake of PNP by clathrin (for positive PNP), caveolin (for negative PNP) and mannose receptors (for hydroxylated PNP) were found with smaller PNP45 showing stronger interactions with the receptors than bigger PNP90.
The size and surface characteristics of polymer nanoparticles (PNP; 45 and 90 nm with different surface charges) play a crucial role in cellular uptake. Specific interactions with cell membrane-bound receptors (clathrin, caveolin and mannose) leading to cellular internalization were observed to depend on size and surface properties of the different PNP. These properties of the nanoparticles also dominate their cytotoxicity, which was analyzed for many factors. The effective reduction in the mitochondrial membrane potential (ΔΨm), uncoupling of the electron transfer chain in mitochondria and resulting ATP depletion, induction of ROS and oxidative stress likely all play a role in the mechanisms behind the cytotoxicity of these PNP.
- Polymer nanoparticles
- Oxidative stress
- Intracellular uptake
With the rapid appearance of nanotechnology-based products in the consumer market, human exposure to nanoparticles (NP) is unavoidable . However, a serious lack of knowledge regarding the health and safety issues of these nanotechnology-based products is genuinely felt. A very important question in nanotoxicological research concerns the factors that determine the cytotoxicity of nanomaterials. Obviously, one of the factors is related to size. Due to their small size, NP have a high surface area to mass ratio, which may play a role in the interactions of NP with biomolecules (proteins, cell wall constituents, etc.) and in mechanisms underlying their toxicity when compared to undissolved bulk material. These mechanisms can involve chemical reactions and physical adsorption processes with different biomolecules. Both can ultimately lead to cellular uptake  and (cyto)toxic effects . So far, little is also known on the mechanism of cellular uptake and intracellular distribution of different NP inside cells, and how factors like size can influence these.
Currently, many applications are foreseen in fields like NP-based drug delivery and bioimaging [4–6], and for food-based applications . Especially for drug delivery applications, the use of polymer nanoparticles (PNP) is emerging as promising . Recent advancements in polymer science allow synthesis of well-defined polymers (including tri-block copolymers) that can be tailor-made for specific purposes, like drug or food ingredient delivery and biodegradable polymers. Additionally, these tri-block copolymers can be tagged with fluorescent probes to render them fluorescent and thus traceable in biological environments. Thus, PNP derived from the tri-block copolymer can be utilized in the encapsulation of drugs or bioactive food ingredients, and hence can be exciting for drug or food ingredient delivery and sustained release preparations. Although much research is done on the synthesis of biologically valuable PNP, knowledge is lacking on how chemical and physical characteristics like size and charge influence the toxicity and bio-interactions of these PNP.
Therefore, it is essential to investigate how size and charge affect the cytotoxicity as well as other facets of NP-cell interactions, like cellular uptake. In order to interpret the results of such studies, it is essential that the investigated NP are well-characterized and comparable, so that only the size is different, while other factors like composition, surface groups, charge, etc. remain constant. Therefore, in this study particular care was taken that both the polymers and the PNP prepared thereof are well-defined and well-characterized to ensure that differences in biological properties only result from size differences for particles with the same surface groups.
The mechanism of nanomaterial toxicity is not completely clear, and it is possible that more than one mechanism is involved. Literature supports oxidative stress as being an important factor in the mechanism [9–15]. However, it remains to be established if oxidative stress is the mechanism underlying the NP induced cytotoxicity, or a phenomenon accompanying this cytotoxicity. Recently, it was recognized that mitochondria can interact with charged NP, which can then influence the electron transport chain (ETC) , although the mechanism underlying this interaction and its exact consequences remain largely unknown. It is possible that due to the damage on the mitochondrial membrane as well as the disruption of the ETC caused by the PNP, the resulting oxidative stress may cause the production of different cytokines (like tumor necrosis factor-α/TNF-α) , which in turn is known to be a biomarker of inflammation.
Previously, it was postulated that NP can enter cells by passive diffusion  or adhesion . However, this model has proven inadequate in explaining several findings. For example, this model fails to explain why negative NP, which should be repelled by the negative cell membrane, can enter cells in overwhelming amounts [20, 21]. Recently, receptor-mediated endocytosis was found to be crucial for the cellular uptake of different NP [2, 22, 23]. It is possible that cellular uptake of different PNP occurs through different cell membrane-bound receptors, like clathrin and caveolin receptors. These NP-receptor interactions have been related to antigen-antibody coupling reactions . It is hypothesized that surface-functionalized and charge-bearing NP present an “epitope”-like structure, which is recognized and bound to the binding sites of different cell membrane-bound receptors. This initiates a cascade of reactions by which the NP are internalized. Therefore, a detailed investigation on the role of NP-receptor interactions in the cellular uptake of NP is justified with an aim to understand how size and surface charge influences cytotoxicity as well as cellular uptake of different PNP. The cellular in vitro models chosen were rat macrophage NR8383 cells and human colonic adenocarcinoma-derived Caco-2 cells. They represent models for two important targets for NP toxicity upon oral exposure including the innate immune response by phagocytosing cells and human enterocytes.
In this article, a method is described for the synthesis of well-characterized fluorescent PNP of different sizes (45 and 90 nm) and different surface charges from their corresponding tri-block copolymers. The presence of a fluorescent probe in the interior of the PNP makes investigations like bioimaging through confocal laser scanning microscopy (CLSM) possible. The influence of size and charge of the PNP on cytotoxicity as well as on intracellular uptake was studied with a variety of cytotoxicological tools. The influence of cell membrane-bound receptors in the internalization of PNP was investigated with receptor blocking studies and further visualization with CLSM.
Synthesis of fluorescent polyethylene glycol400-polyhexylene adipate-polyethylene glycol400 [PEG400-PHA-PEG400] (Pol400) polymer
Data of Pol 400 with its end group conversion rates
Molecular weight (kDa)
Melting point ( o C)
1 H NMR 9.0
Conversion of terminal hydroxyls to differently charged end groups
The terminal hydroxyl (-OH) groups of Pol400 were converted into an amine by first reacting the polymer with chloroacetyl chloride and subsequently adding concentrated ammonia, which yielded Pol400-NH2 . Reacting the polymers with succinic anhydride yielded Pol400-COOH. In contact with water at neutral pH, this means that the terminal groups will be either positively charged (-NH3 +) or, negatively charged (COO–) due to the pKa values of these groups. The degree of conversion of the terminal hydroxyl groups was assessed by reaction with trichloroacetyl isocyanate (TAIC) . Reaction of TAIC with terminal hydroxyl groups gives a characteristic peak in the 1 H NMR spectrum at δ = 4.43 ppm. Upon converting these -OH groups to amino or carboxylate moieties, this reaction with TAIC is not possible anymore, and this peak is thus smaller or even absent, depending on the conversion to -NH3 + or -COO–. This analysis was used to quantify this conversion (Table 1 and Additional file 4), which turned out to be almost quantitative for all polymers. The data on the characterization of Pol400, including the conversions of the end hydroxyl groups to different functional groups (-NH2 and -COOH) are given in Table 1. The melting points of all polymers were determined by differential scanning calorimetry (DSC) and were found to be ~43°C for all polymers. This indicates that the melting point is only determined by the middle block, which has the same length in all synthesized polymers.
Synthesis and characterization of different PNP
DLS data of PNP 90
Size in water (nm)
Size in F12-K (nm) (after 1 h)
Size in DMEM (nm) (after 1 h)
PNP 90 -NH 2
90 ± 5
145 ± 5
140 ± 5
PNP 90 -OH
90 ± 5
115 ± 5
120 ± 5
PNP 90 -COOH
90 ± 5
120 ± 5
130 ± 5
Evaluation of the cytotoxicity of nanoparticles
A. MTT assay
EC 50 values (μg/ml) obtained from different assays after 24 h exposure of NR8383 and Caco-2 cells to positively charged PNP 45 [] and PNP 90
PNP 90 -NH 2 (90 ± 5 nm)
PNP 45 -NH 2 (45 ± 5 nm)
Intracellular ROS production
Mitochondrial membrane potential (ΔΨm)
Mitochondrial membrane potential
Cellular ATP content
B. Phagocytic Index (PI) measurement
Assessment of intracellular reactive oxygen species (ROS) production by DCFH-DA assay
Assessment of mitochondrial membrane potential (ΔΨm)
Assessment of intracellular ATP content
Assessment of TNF-α production
Intracellular uptake of PNP90
Effect of size and surface charge on endocytosis-based cellular uptake of PNP
Effect of size and surface charge on clathrin and caveolin mediated endocytosis
Effect of size and surface charge on mannose receptors
Data were analyzed with Origin Pro (version 8.0) graphing software. For statistical analysis a student’s t-test was performed, and data with p < 0.05 (compared to negative control) were marked with an asterisk (*) sign. Each data point represents the average from three independent experiments (n = 3) (for CLSM studies n = 5) and is presented as the arithmetic mean ± standard error of mean. While comparing the effect of size, the results for PNP45 and PNP90 were also mutually compared and only the statistically significantly different (p < 0.05) data between the two were marked by “†” symbol.
Due to the nature of the tri-block copolymers synthesized and used in the present study, which have a hydrophobic middle block and hydrophilic terminal blocks, the PNP that were formed out of these polymers in water had a hydrophobic core and a hydrophilic corona. The size of the PNP depends largely on the size of the polymers and the ratio between their hydrophobic middle and hydrophilic terminal blocks . The hydrophobic middle blocks (the polyhexylene adipate polyester) avoid contact with water, whereas the hydrophilic (PEG) blocks try to remain in contact with the water. This means that for the polymers with the larger hydrophilic blocks the aggregate surface becomes crowded with PEG groups faster and the particles stop growing sooner than for the polymers with the smaller terminal groups. The polymers with the smaller PEG groups grow into larger particles, because in that case the surface does not get so easily crowded and more polymer molecules will add to the forming nanoparticle. The MTT assay data suggest that the positive PNP45 were more cytotoxic than the positive PNP90. Both the smaller and larger negative PNP did not induce any significant cytotoxic response at concentrations up to 12.5 μg/ml. Although some studies have been performed on the size-dependent cytotoxicity of NP, such studies on PNP are rare. In the present study the PNP45 and PNP90 that were used have very similar properties in surface charge density. To the best of our knowledge, this is the first report in which the effect of size on cytotoxicity of PNP is systematically investigated, while keeping the surface characteristics and PNP composition unchanged.
For inorganic NP more is known on the effect of size on cytotoxicity. Recently, it was reported that smaller gold nanoparticles (1.4 nm) were much more cytotoxic than bigger (15 nm) ones . In a similar experiment, silver NP of three different sizes (15, 30 and 55 nm) were tested on a rat alveolar macrophage cell line, which is comparable to the NR8383 cell line used in this study. The cytotoxicity of the smallest (15 nm) particles was highest and of the biggest ones (55 nm) the lowest . The cytotoxicity of a wide size-range of silica NP (30, 48, 118 and 535 nm) was tested on a mouse keratinocyte HEL-30 cell line. A clear size-dependent cytotoxic pattern was reported. The smaller (30 and 48 nm) silica NP showed a much higher toxicity than the bigger (118, 535 nm) ones . For copper NP similar results were reported . Some other reports also indicated an inverse relationship between size and toxicity of different NP including PNP [13, 33]. Auffan et al.  hypothesized that inorganic NP smaller than 30 nm are chemically very unstable due to the presence of many high energy surface states which makes them extremely reactive, which again results in an enhanced cytotoxicity. However, many of the surface properties of inorganic NP are significantly different from the surface properties of organic PNP. Therefore, although our results match the findings for inorganic NP, a true comparison is difficult.
It should be noted that in all the cellular experiments reported in this article, cell culture media (DMEM and F12-K) contained FCS rich in proteins (like albumin). It has been observed before that the presence of FCS can cause an increase in the sizes of these PNP by surface adsorption of proteins, although the PNP, in this case, still remained highly monodisperse . The presence of serum, by virtue of being high in protein content, has been reported to influence the toxicity and cellular uptake of NP . This protein adsorption can be of influence on cellular uptake and toxicity, but it is expected that such protein effects will also occur in the gastrointestinal tract upon oral exposure to PNP. Thus, testing in the presence of serum better reflects the physiological conditions for PNP that may be developed with food-based applications in mind.
Two series of PNP were investigated that differ in size and within each series PNP with different surface charges (-NH2, -OH and -COOH) were investigated. A distinct size-dependence was observed. For instance, although both amine-terminated PNP were toxic, the smaller PNP45 were more cytotoxic than the larger PNP90. Hence a size-dependent effect for PNP with comparable surface charge and surface functionalization was observed. In equivalent masses, the smaller PNP45 (45 nm) presented two times more surface area compared to the bigger PNP90 (90 nm). Upon expressing the toxicity data based on surface area, it was found that the toxicity increased with an increase in PNP surface area.
Production of intracellular ROS after exposure to different NP has been amply reported [35–39]. It is thought that these ROS push the cellular physiology to the limits by inducing oxidative stress. Our data, obtained from the DCFH-DA assays, show that only positive PNP induced intracellular ROS production with the smaller PNP showing a higher effect. These findings also match the pattern of cytotoxicity (MTT assay) for these PNP. In literature, systematic studies on the effect of size on the intracellular ROS production are rare. Jiang et al.  investigated the effect of size on intracellular ROS production by testing a wide range of titanium dioxide NP (4-195 nm) and reported the highest ROS induction for NP of 30 nm size. In a separate study, silver NP of 4, 20 and 70 nm were tested on macrophage U937 cells . It was found that the 20 nm silver NP were the most capable of producing oxidative stress. A similar study by Choi et al.  showed that within a series of different sizes of silver NP tested, the smallest (5 nm) NP were the most capable of inhibiting the growth of nitrifying bacteria through production of ROS. Landsiedel et al.  also mentioned an inverse relationship between the size of NP and their induction of intracellular ROS in their comprehensive review on different metal oxide NP (like CeO2, TiO2, SiO2, ZrO2).
The decrease of the mitochondrial membrane potential (ΔΨm) by cationic PNP is an important finding. It shows that cationic PNP can indeed interact with intracellular mitochondria and compromise their integrity. The decrease in ΔΨm after exposure to cationic PNP can have further consequences. This compromised state of the mitochondrial membrane can increase its permeability which may result in leaching of the mitochondrial calcium to the cytoplasm causing a cellular overload of calcium, release of cytochrome c and subsequently trigger apoptosis . Similarly, a compromised mitochondrial membrane also can hamper the normal electron transport chain. This can result in decreased ATP production. The finding of ATP depletion of cells upon exposure to cationic PNP matches well with the observed effect on the mitochondrial membrane potential (ΔΨm). Previously, Bhattacharjee et al.  reported that positive silicon NP (1.6 ± 0.2 nm) were able to induce ROS production in isolated mitochondrial fractions from rat liver tissue. Similarly, Xia et al.  observed that cationic polystyrene nano-beads can interact with and subsequently harm intracellular mitochondria. Due to the continuous involvement of mitochondria in the respiratory cycle by virtue of the electron transport chain (ETC) processes occurring on the outer membrane, it was suggested that interaction of positive NP with mitochondrial membranes can disturb the mitochondrial membrane potential. This was shown in the present study to occur upon exposure of the cells to positive PNP. As a result, positive PNP might uncouple the cascade of reactions in the ETC and thus not only hamper ATP production but also increase the intracellular ROS production . A recent study reported that intracellular ATP depletion occurred upon exposure of human endothelial EAhy926 cells to differently sized polystyrene NP . The data obtained in the present study are in line with the literature and this could shed some light on the poorly understood mechanism of intracellular ROS production induced by NP. In our opinion, reduction of the mitochondrial membrane potential (ΔΨm) followed by intracellular ATP depletion, as observed after exposure to cationic PNP, may also be a mechanism of cytotoxicity, related to or independent of intracellular ROS production and warrants further investigation.
It has been reported that several NP can induce production of inflammatory cytokines like TNF-α in different cell lines, including a primary rat brain microvessel cell line and human alveolar epithelial A549 cells [26, 47, 48]. However, a comparative study on the effect of NP size on TNF-α induction is rare, especially for PNP. Recently, size-dependent TNF-α induction was reported when titanium dioxide NP (5 and 200 nm) were intra-tracheally instilled in rats . It was observed that 5 nm particles were much more effective in inducing TNF-α than 200 nm ones. A similar type of inverse relationship between size of NP and TNF-α production was reported by Hanley et al.  for silver oxide NP. Our data on TNF-α production match these reported literature data and point towards an inverse relationship between size of PNP and TNF-α production.
Our data on the cellular uptake show that smaller PNP45 (45 nm) were taken up in appreciably larger amounts (as determined by CLSM) than the bigger PNP90 (90 nm), irrespective of surface charge. Win et al.  reported a similar type of inverse relationship between size of PNP and cellular uptake in Caco-2 cells. Recently, fluorescent and carboxyl-terminated polystyrene NP of 20 and 200 nm sizes were tested on both rat and human primary hepatocyte cells  and it was found that the smaller 20 nm polystyrene NP showed a higher intracellular uptake than the bigger ones. Many other groups reported a higher intracellular uptake for smaller NP [51, 53–55]. Zhang et al.  performed a molecular modeling and thermodynamics study to understand this size dependence. From calculations and thermodynamics they predicted that NP of ~22 nm radius (i.e. ~44 nm in size) are more easily internalized by cells. Similarly, other computational models [57–59] also predicted an energetically favorable receptor-mediated intracellular uptake for NP of 30-50 nm sizes. These authors were also able to predict an upper threshold radius of ~60 nm (i.e. ~120 nm size), where receptor-based endocytosis will not be favorable anymore. These findings fit quite well with our data.
The inhibition of endocytosis (by performing the experiments at 4°C or exposure to a mixture of 2-deoxyglucose and sodium azide) had a stronger effect on the uptake of PNP45 than on the uptake of PNP90. An explanation may be that smaller PNP enjoy a higher degree of binding with cell membrane receptors. Hence, inhibition of receptor-based endocytosis affects the cellular uptake of smaller particles more. An optimal size of 50 nm was proposed for uptake as well as saturation kinetics of NP uptake by Chithrani et al. , who investigated the uptake of gold NP of three different sizes (14, 50 and 74 nm) in HeLa cells . Recently, Jiang et al.  also reported that receptor-based endocytosis was highest for 40-50 nm gold and silver NP tested on herceptic receptor ErbB2 expressed on macrophage cells. This preference for 40-50 nm NP also matches our data.
Like in the general receptor inhibition studies, our data show that selective blocking of the clathrin, caveolin or, mannose receptors had in all cases a stronger effect on the uptake of smaller PNP45 particles than that of the larger PNP90 particles. These results are independent of surface charge of the PNP, although the preference of clathrin receptors for positive PNP and caveolin receptors negative PNP is evident from the results. However, it should also be noted that blockers lack absolute specificity and also that other endocytotic pathways for cellular PNP uptake remain available after blocking one receptor type. Furthermore, because different in vitro cellular systems have different physiologies and have different levels of expression of clathrin or caveolin receptors, results from different studies cannot always be easily compared . Whether combined inhibition of the clathrin, caveolin and mannose receptors would completely abolish the cellular uptake of the PNP, or that residual uptake would remain because also other uptake mechanisms are of importance, remains to be investigated. There is only a limited amount of systematically performed size-dependent analyses on interactions of PNP with endocytosis receptors. Rejman et al.  performed a very extensive study on cellular uptake mechanisms of latex particles in murine melanoma B16-F10 cells and found a preference for clathrin receptors by smaller and caveolin receptors by bigger PNP. More recently, it was reported that carboxyl-terminated polystyrene NP of 43 nm size got internalized by the cells through a clathrin-dependent pathway . Oh et al.  also found that uptake of smaller metal hydroxide nanoparticles (50, 109, 200 nm), when tested on a human osteosarcoma (MNNG/HOS) cell line, showed a stronger clathrin receptor dependence of cellular uptake than the bigger ones (375 nm). So, although the effects are clearly different for the differently charged PNP and the different receptors, our results seem to be in line with the findings of the majority of these reports that smaller (or medium-sized) NP have stronger interactions with endocytosis receptors than larger NP.
Mannose receptors are a unique group of receptors that are often expressed on macrophage cell surfaces and recognize and endocytose a wide variety of carbohydrates. Though it is not clear yet how these receptors recognize such a huge variety of molecules, the orientation of the carbohydrate molecule is important. It is also known that hexoses with equatorially placed hydroxyl groups have a strong binding affinity towards these receptors .
Although our PNP do not contain carbohydrate groups, especially those that contain –OH groups on the surface have some chemical resemblance with carbohydrates with -OH groups. The results of the inhibition studies match with this, since the maximum inhibition of intracellular uptake was observed for both hydroxyl- or acid-terminated PNP. This once again points towards a complex range of interactions between PNP and cell membranes and their receptors leading to particle internalization. Although we are the first to actually show that inhibition of mannose receptors inhibits cellular uptake of PNP, there have been a few reports already where these receptors have been targeted for facilitated drug delivery. Park et al.  used mannosylated polyethyleneimine coupled to silica NP to increase the transfection efficiency in macrophage cells by targeting the mannose receptors. Similar strategies have been employed by other groups to increase the delivery efficacy in biological systems [67–69]. Our results on mannose receptors are in line with data available in literature that point towards strong NP-receptor interactions. These results can be further developed for more sophisticated applications like drug delivery or food-based delivery of functional ingredients.
Well-characterized, monodisperse and fluorescent PNP of different sizes (45 and 90 nm) and surface properties were synthesized. The PNP exhibited an inverse relationship between size and cytotoxicity as well as between size and cellular uptake. A size-dependent induction of intracellular ROS production identifies oxidative stress as a possible mechanism of cytotoxicity with subsequent release of inflammatory cytokines representing another mechanism for NP induced adverse effects. Reduction in the mitochondrial membrane potential, uncoupling of the electron transfer chain in mitochondria and resulting ATP depletion, induction of ROS and oxidative stress likely all play a role in the mode of action for the cytotoxicity of these PNP.
Although at the concentrations tested, only positive PNP show cytotoxic effects, all PNP were taken up by the cells. An involvement of clathrin, caveolin and mannose receptors could be seen in cell internalization of PNP with their relative importance depending on the surface properties of the PNP. Overall the results presented provide insight in size and surface charge-specific cellular uptake and cytotoxicity of PNP and possible modes of action underlying these effects. Typically, larger PNP and negatively charged PNP are less toxic in our tests than smaller and positively charged PNP. Translation of these results to recommendations for their preferential use in development of safer NP requires validation of their lower toxicity in vivo studies.
Synthesis of the fluorescent tri-block copolymers
The fluorescent probe, 4-(diethanolamino)-7-nitro-benzo-[1, 2, 5]oxadiazole, was synthesized and characterized as reported in literature . For the synthesis of Pol400, a dry 100 ml three-necked round-bottom flask containing properly grinded and dried 1,6-hexanediol (2.0 g; 17 mmol) and 0.1 mg of fluorescent probe (~4 × 10–4 mmol) was fitted with a reflux condenser and flushed with dry nitrogen for 30 min. Subsequently, the flask was heated on an oil bath at 120°C with gentle stirring until the hexanediol melted. Then 50 μl of dry triethylamine was added to the mixture followed by drop-wise addition of 3.28 g (17.8 mmol) of dry adipoyl chloride. The mixture was gently stirred at 120°C for 48 h until no more HCl was produced. Then, excess (40 g; 100 mmol) of PEG400 (carefully dried under reduced pressure) was added at 120°C and the reaction mixture was heated while stirring for another 48 h. The resulting viscous mixture was poured into 50 ml of dry ether and the precipitate was filtered and washed repeatedly with dry ether. The precipitate was then stirred with 100 ml of distilled water and centrifuged at 900 rpm for 4 min. This process was repeated thrice. The resulting polymer was finally dried by overnight freeze drying and characterized by 1 H NMR (Bruker Avance III 400 MHz NMR spectrometer; CDCl3), IR (infrared) spectroscopy, DSC, SEC and UV–vis spectroscopy. Pol2000 with the same fluorescent probe was synthesized and characterized as described previously .
Synthesis of fluorescent Pol400 and Pol2000 polymers with different end groups
A. Conversion to amines
In a dry three-necked 100 ml round-bottom flask fitted with a reflux condenser, 0.03 mmol of Pol400 (330 mg) was heated at 120°C until it melted. Then 11.2 mg (0.1 mmol) of chloroacetyl chloride was added slowly under stirring. The mixture was then stirred for 6 h. For conversion to the amine-terminated polymers, the mixture was cooled and 6.8 mg of 25 % (w/w) aqueous ammonia (0.1 mmol of ammonia) was added. The mixture was allowed to stir for another 12 h before workup. The polymer was purified and dried as mentioned before for Pol400. Similarly, Pol2000 with amine terminal groups was obtained .
B. Conversion to acid
In a similar experimental set up as mentioned for the conversion to the amines, 10 mg (0.1 mmol) of succinic anhydride was added in portions to 0.03 mmol of molten Pol400 polymer and allowed to react for 12 h at 120°C. The purification was performed as described above.
C. Estimation of terminal hydroxyl group conversion with trichloroacetyl isocyanate (TAIC)
In an NMR tube with Pol400 polymer sample dissolved in CDCl3, 10 μl of TAIC was added and the tube was vortexed for 5 min . Then after another 10 min 1 H NMR spectra were recorded and the peak appearing at δ = 4.43 ppm was integrated and compared with the value obtained from unmodified polymer to obtain the conversions of the terminal -OH groups .
Synthesis and characterization of nanoparticles
Nanoparticles were prepared by the nanoprecipitation method using a slight modification of the method described by Khoee et al. . First, 10 mg of tri-block copolymer (Pol400 or Pol2000 to obtain PNP90 and PNP45, respectively) were dissolved in 2 ml THF with mild heating (~35°C) and the solution was then injected into 10 ml of vigorously stirred ultrapure water in an open beaker . The dispersion was stirred for another 30 min. Then THF was removed under reduced pressure and the aqueous dispersion was filtered through 0.2 μm cellulose filters. Essentially no material remained on the filter. These stock solutions were diluted in measuring flasks to obtain solutions with well-defined concentrations. The hydrodynamic radius of the PNP, both in aqueous dispersions and in F12-K and DMEM cell culture media were determined by DLS at 90o (0.1 μg/ml), and their zeta (ζ) potential (0.1 μg/ml) was obtained with a Malvern Zetasizer. The cell culture mediums (F12-K and DMEM) were also checked by DLS and ζ-potential measurements. While the DLS failed to measure any particulate material > 5 nm in size, the ζ-potential measurements varied between -5 to -10 mV, which can be attributed to the anionic protein molecules originating from the FCS. The serial dilutions of PNP in F12-K or DMEM media were also checked by DLS to exclude any agglomeration of PNP occurring within the tested concentration range. The probability of monomers of the tri-block copolymer leaking out of the PNP resulting in the disintegration of the PNP was excluded by both the SEC and DLS performed at different intervals.
Scanning Electron Microscopy (SEM)
A clean circular cover glass, 8 mm diameter, (Menzel, Braunschweig, Germany) was fitted on a sample holder by carbon adhesive tabs (EMS, Washington, USA) and 50 μl of an aqueous suspension of PNP was put on the glass and the water was allowed to evaporate until the PNP that remained behind were completely dried . The dry sample was sputter-coated with 2 nm tungsten (MED 020, Leica, Vienna, Austria). Samples were analyzed at 2 kV at room temperature in a field emission scanning electron microscope (Magellan 90, FEI, Eindhoven, the Netherlands).
Rat alveolar macrophage (NR8383) and human colonic adenocarcinoma (Caco-2) cells were obtained from ATCC (Manassas,VA) [14, 15]. The NR8383 and Caco-2 cells were cultured in 150 cm2 cell culture flasks with 25 ml F12-K culture medium (Gibco 21127) and DMEM medium, respectively, both supplemented with 10 % (v/v) heat-inactivated fetal calf serum (FCS) and 0.1 % (v/v) gentamicin, in a humidified atmosphere containing 5 % CO2 at 37°C.
Cytotoxicity measurement by MTT assay
A. NR8383 cells
An NR8383 cell suspension was centrifuged at 140 g for 5 min before re-suspending the cell pellet in F12-K medium followed by counting and adjusting the cellular concentration to 2 × 105 cells/ml. The cells were then seeded in a 96-well plate (50 μl/well) and the plate was kept in a 5 % CO2 incubator at 37°C for 24 h. Subsequently, 50 μl of serial dilutions of freshly prepared and well-vortexed different PNP90 in F12-K medium were added to the cells to obtain the required final concentrations [14, 15]. The concentration range of 0-400 μg/ml was chosen because these concentrations appeared to detect the differences in toxic responses of the cells to the different PNP. This was followed by incubation for another 24 h after which 5 μl of MTT solution in PBS (5 mg/ml) was added to each well and the plate was incubated for another 4 h. Then 100 μl of pure dimethylsulfoxide (DMSO) was added to each well to dissolve the formazan crystals. As the NR8383 cells are a suspension cell line, the medium in the wells of the 96-well plates could not be evacuated before addition of DMSO to the wells as also described before . The absorption of each well was measured at 562 nm in a 96-well plate reader and the background absorption at 612 nm was subtracted. Mitochondrial metabolic activity for each concentration of PNP was expressed as % of the corresponding negative control reading. Medium without PNP and medium with Triton-X (0.1 %) were used as negative and positive controls respectively. Additional control experiments were performed in order to exclude a possible interference with the absorption by the PNP themselves by measuring the absorbance values in a similar set-up after mixing MTT reagent as well as only F12-K medium with different dilutions of PNP90.
B. Caco-2 cells
The Caco-2 cells were plated at a concentration of 105 cells/ml in a 96-well plate (100 μl/well) and were incubated at 37°C for 24 h [14, 15]. Then different freshly prepared and well-vortexed PNP90 in DMEM medium were added to the cells (100 μl/well) to achieve the final concentrations followed by further incubation of 24 h at 37°C. 5 μl of MTT solution (in PBS) was then added to each well followed by an incubation of 4 h. Each well was then carefully emptied (because unlike NR8383 the Caco-2 cells attach to the bottom of the wells) without dislodging the precipitated crystals and the crystals were dissolved in pure DMSO (100 μl/well). Finally, each well was measured as mentioned above. Control experiments, as mentioned before, were also done.
C. Phagocytic index measurement in NR8383 cells
An NR8383 cell suspension (2 × 105 cells/ml) was seeded in a 96-well plate (50 μl/well) in F12-K medium, followed by addition of 50 μl/well of serial dilutions of freshly prepared and well-vortexed PNP90 in F12-K medium to obtain the required final test concentrations of PNP [14, 15]. Plain F12-K medium without PNP90 and medium containing 100 μM CuSO4 were used as negative and positive control, respectively. After 24 h the cells were exposed to yellow-green fluorescent latex beads (1 μm size) at a ratio of beads to cells in each well of 50:1. After 4 h of incubation counting samples were taken from the wells and viewed first under a fluorescent microscope to visualize the fluorescent beads, followed by bright-field view to visualize the cells. Samples were also taken out of each well to assess the cell viability by trypan blue exclusion test. The phagocytic index was determined by calculating the average number of fluorescent beads phagocytosed per viable cell and expressed as % of the negative control. Control experiments were run with only PNP in absence of fluorescent latex beads (1 μm) and no phagocytic vacuole inside the NR8383 cells could be seen.
Measurement of intracellular ROS by DCFH-DA assay
A. NR8383 cells
The cell suspension was adjusted to 2 × 105 cells/ml and seeded in a 96-well plate (50 μl/well) in F12-K medium. 50 μl/well of serial dilutions of freshly prepared and well-vortexed PNP90 in F12-K medium were added to obtain the required final test concentrations of PNP. A concentration of 10 mM H2O2 was used as positive control, and F12-K medium without PNP as negative control. After 6 h of exposure to the PNP, 5 μl of a 20 mM solution of DCFH-DA was added to each well and the plates were incubated for another 18 h in a 5 % CO2 atmosphere at 37°C. The fluorescence was then measured on a fluorometer (λ ex = 485 nm and λ em = 538 nm). The fluorescence induction factor for each concentration of PNP90 was calculated by dividing the reading of each well by the average reading of the negative control and expressed as %. Control experiments were performed by incubating the PNP90 at their test concentrations with DCFH-DA in the absence of cells to check the possibility of a positive fluorescence reading caused by reaction of DCFH-DA with PNP90 alone [14, 15].
B. Caco-2 cells
The cells were suspended in DMEM medium to a concentration of 105 cells/ml after trypsinization and were seeded in a 96-well plate (100 μl/well). After 24 h the cells were exposed to 100 μl/well of final concentrations of freshly prepared and well-vortexed different PNP90 in DMEM medium. Following another 6 h of PNP90 exposure, 5 μl of a 20 mM solution of DCFH-DA was added to each well. The plate was further incubated for 18 h before measurement of the fluorescence was carried out as described above.
Measurement of mitochondrial membrane potential (ΔΨm)
The NR8383 and Caco-2 cells were plated and exposed to serial dilutions of freshly prepared and well-vortexed PNP of both sizes (45 and 90 nm) as mentioned before. The mitochondrial membrane potential (ΔΨm) was measured by a commercially available kit from Invitrogen (MitoProbeTM; Transition Pore Assay Kit; catalogue no. M34153) and expressed as % of negative control (0 μg/ml). A 100 μM solution of ionomycin in DMSO (supplied with the kit) and F12-K or DMEM medium without PNP were used as positive and negative controls, respectively.
Measurement of intracellular ATP content
The NR8383 and Caco-2 cells were seeded in a 96-well plate and exposed to different freshly prepared and well-vortexed PNP90 and PNP45 as mentioned before. After 24 h the intracellular ATP content of each well was measured by a commercial ATP measuring kit (Sigma Aldrich, Product No. FLASC) and results were expressed as % of negative control. Cells exposed to medium without PNP and to medium with 75 mM 2,4-DNP (2,4-dinitrophenol) were used as negative and positive controls, respectively.
Measurement of TNF-α release in NR8383 cells
The NR8383 cells were seeded in a 96-well plate and exposed to different concentrations of freshly prepared and well-vortexed PNP90 of each type, as mentioned above. After 24 h the supernatants were collected, centrifuged at 1000 g for 10 min, and then spectrophotometrically analyzed for the TNF-α content with a commercial rat TNF-α kit (Invitrogen), using the procedure from the manufacturer’s manual. Medium without PNP and medium with 0.1 μg/ml lipopolysaccharide (LPS)  were used as negative and positive controls, respectively.
Confocal laser scanning microscopy (CLSM)
For performing CLSM a drop of the NR8383 or, Caco-2 cell suspension was placed on a glass slide and viewed through an oil immersion lens (100×) of a confocal microscope (Zeiss Exciter). For assessment of the average fluorescence intensity, readings from 20 individual cells from five different optical fields (for each PNP90) in focus selected from five separate experiments (n = 5) were used. All the measurements were done at the same excitation wavelength (λ ex = 488 nm and λ em = 543 nm), laser power, pinhole opening and detector gain. To exclude any background fluorescence, control samples of NR8383 or, Caco-2 cells not exposed to the different PNP9090, were also investigated by CLSM. These NR8383 or, Caco-2 cells did not show any background fluorescence. Non-fluorescent PNP9090 were also tested to exclude any additional fluorescence from the PNP.
Effect of inhibition of endocytosis
A. Inhibition of endocytosis by performing the experiment at 4°C
The NR8383 and Caco-2 cells (after trypsinization) were seeded and exposed to non-toxic 1 μg/ml concentrations of different PNP9090 in a 96-well plate as mentioned above and were both pre-incubated and incubated at 4°C. Results of the CLSM images (λ ex = 488 nm; λ em = 543 nm) were compared to results from similar incubations performed at 37°C . A figure of colony of NR8383 cells that have taken up fluorescent PNP9090 -NH2 is provided as Additional file 7. Control experiments with cells exposed to PNP without a fluorescent probe (non-fluorescent PNP) of similar sizes and surface groups were done. Non-fluorescent PNP in absence of cellular system were also tested by CLSM and did not show any fluorescence signal. The results for PNP90 were then compared with PNP45.
B. Inhibition of endocytosis by exposure to a mixture of 2-deoxyglucose and sodium azide
An NR8383 or Caco-2 cell suspension was exposed to a mixture of 50 mM 2-deoxyglucose and 10 mM sodium azide  for 30 min at 37 ºC before being centrifuged and generously washed with PBS at least three times to remove the exposure medium. Finally, the cells were plated and exposed to different PNP90 at 37°C as described before. The results for PNP90 were then compared with PNP45.
Inhibition of clathrin and caveolin receptor-mediated endocytosis
The NR8383 and Caco-2 cells were exposed to 450 mM sucrose (to inhibit clathrin receptors)  or to 1 μM methyl-beta-cyclodextrin (MβCD) (to inhibit caveolin receptors)  for 30 min before being washed, plated and exposed to different PNP90 at 37°C. Control experiments were done by incubating the cells with 10 μg/ml of Alexa Fluor 488 nm-conjugated transferrin (selective inhibitor for clathrin/λ ex = 495 nm and λ em = 519 nm)  or 5 μg/ml of Alexa Fluor 488 nm-conjugated cholera toxin subunit-B (selective inhibitor for caveolin/λ ex = 495 nm and λ em = 519 nm)  for 30 min on ice followed by thorough washing with PBS thrice and then performing CLSM on the cells in order to confirm the blockade of the clathrin and caveolin receptors. It was seen that the inhibitors used (sucrose and MβCD) could block > 90 % of the normal uptake of transferrin or cholera toxin for both the cell lines (Additional file 8) without any additional cytotoxicity. The results for PNP90 were then compared with PNP45.
Inhibition of mannose receptor mediated endocytosis
The NR8383 cells were exposed to a 2 mg/ml concentration of α-mannan for 2 h in order to inhibit the mannose receptors  before being washed, plated and exposed to different PNP90 and PNP45 at 37°C.
The authors thank the Wageningen UR strategic research programme Bionanotechnology and Graduate School VLAG for funding. JvdG acknowledges Human Frontier Science Program for financial support. The authors thank Tiny Franssen-Verheijen and Remco Fokkink for help with SEM pictures and DLS measurements, respectively.
- Lewinski N, Colvin V, Drezek R: Cytotoxicity of Nanoparticles. Small 2008, 4: 26–49. 10.1002/smll.200700595PubMedView ArticleGoogle Scholar
- Chithrani BD, Ghazani AA, Chan WCW: Determining the size and shape dependence of gold nanoparticle uptake into mammalian cells. Nano Lett 2006, 6: 662–668. 10.1021/nl052396oPubMedView ArticleGoogle Scholar
- Clift MJD, Bhattacharjee S, Brown DM, Stone V: The effects of serum on the toxicity of manufactured nanoparticles. Toxicol Lett 2010, 198: 358–365. 10.1016/j.toxlet.2010.08.002PubMedView ArticleGoogle Scholar
- Bhattacharjee S, Ershov D, Gucht Jvd, Alink GM, Rietjens IMCM, Zuilhof H, Marcelis ATM: Surface charge-specific cytotoxicity and cellular uptake of tri-block copolymer nanoparticles. Nanotoxicology 2011, : 1–14.Google Scholar
- Gelperina S, Kisich K, Iseman MD, Heifets L: The Potential Advantages of Nanoparticle Drug Delivery Systems in Chemotherapy of Tuberculosis. Am J Resp Crit Care 2005, 172: 1487–1490. 10.1164/rccm.200504-613PPView ArticleGoogle Scholar
- Irvine DJ: Drug delivery: One nanoparticle, one kill. Nat Mater 2011, 10: 342–343. 10.1038/nmat3014PubMedView ArticleGoogle Scholar
- Sozer N, Kokini JL: Nanotechnology and its applications in the food sector. Trends Biotechnol 2009, 27: 82–89. 10.1016/j.tibtech.2008.10.010PubMedView ArticleGoogle Scholar
- Sinha R, Kim GJ, Nie S, Shin DM: Nanotechnology in cancer therapeutics: bioconjugated nanoparticles for drug delivery. Mol Cancer Ther 2006, 5: 1909–1917. 10.1158/1535-7163.MCT-06-0141PubMedView ArticleGoogle Scholar
- Donaldson K, Stone V, Borm PJA, Jimenez LA, Gilmour PS, Schins RPF, Knaapen AM, Rahman I, Faux SP, Brown DM, MacNee W: Oxidative stress and calcium signaling in the adverse effects of environmental particles (PM10). Free Radical Bio Med 2003, 34: 1369–1382. 10.1016/S0891-5849(03)00150-3View ArticleGoogle Scholar
- Hussain S, Hess K, Gearhart J, Geiss K, Schlager J: In vitro toxicity of nanoparticles in BRL 3A rat liver cells. Toxicol in Vitro 2005, 19: 975–983. 10.1016/j.tiv.2005.06.034PubMedView ArticleGoogle Scholar
- Pisanic TR, Blackwell JD, Shubayev VI, Finones RR, Jin S: Nanotoxicity of iron oxide nanoparticle internalization in growing neurons. Biomaterials 2007, 28: 2572–2581. 10.1016/j.biomaterials.2007.01.043PubMedView ArticleGoogle Scholar
- Eom H-J, Choi J: p38 MAPK activation, DNA damage, cell cycle arrest and apoptosis as mechanisms of toxicity of silver nanoparticles in Jurkat T cells. Environ Sci Technol 2010, 44: 8337–8342. 10.1021/es1020668PubMedView ArticleGoogle Scholar
- Nel A, Xia T, Madler L, Li N: Toxic potential of materials at the nanolevel. Science 2006, 311: 622–627. 10.1126/science.1114397PubMedView ArticleGoogle Scholar
- Bhattacharjee S, de Haan LHJ, Evers NM, Jiang X, Marcelis ATM, Zuilhof H, Rietjens IMCM, Alink GM: Role of surface charge and oxidative stress in cytotoxicity of organic monolayer-coated silicon nanoparticles towards macrophage NR8383 cells. Part Fibre Toxicol 2010, 7: 25. 10.1186/1743-8977-7-25PubMed CentralPubMedView ArticleGoogle Scholar
- Ruizendaal L, Bhattacharjee S, Pournazari K, Rosso-Vasic M, de Haan LHJ, Alink GM, Marcelis ATM, Zuilhof H: Synthesis and cytotoxicity of silicon nanoparticles with covalently attached organic monolayers. Nanotoxicology 2009, 3: 339–347. 10.3109/17435390903288896View ArticleGoogle Scholar
- Xia T, Kovochich M, Liong M, Zink JI, Nel AE: Cationic polystyrene nanosphere toxicity depends on cell-specific endocytic and mitochondrial injury pathways. ACS Nano 2008, 2: 85–96. 10.1021/nn700256cPubMedView ArticleGoogle Scholar
- Sayes CM, Reed KL, Warheit DB: Assessing toxicity of fine and nanoparticles: Comparing in vitro measurements to in vivo pulmonary toxicity profiles. Toxicol Sci 2007, 97: 163–180. 10.1093/toxsci/kfm018PubMedView ArticleGoogle Scholar
- Brigger I, Dubernet C, Couvreur P: Nanoparticles in cancer therapy and diagnosis. Adv Drug Deliver Rev 2002, 54: 631–651. 10.1016/S0169-409X(02)00044-3View ArticleGoogle Scholar
- Vasir JK, Labhasetwar V: Quantification of the force of nanoparticle-cell membrane interactions and its influence on intracellular trafficking of nanoparticles. Biomaterials 2008, 29: 4244–4252. 10.1016/j.biomaterials.2008.07.020PubMed CentralPubMedView ArticleGoogle Scholar
- Chen LA, Mccrate JM, Lee JCM, Li H: The role of surface charge on the uptake and biocompatibility of hydroxyapatite nanoparticles with osteoblast cells. Nanotechnology 2011, 22: 105708. 10.1088/0957-4484/22/10/105708PubMed CentralPubMedView ArticleGoogle Scholar
- Asati A, Santra S, Kaittanis C, Perez JM: Surface-charge-dependent cell localization and cytotoxicity of cerium oxide nanoparticles. ACS Nano 2010, 4: 5321–5331. 10.1021/nn100816sPubMed CentralPubMedView ArticleGoogle Scholar
- Huang M, Ma ZS, Khor E, Lim LY: Uptake of FITC-chitosan nanoparticles by A549 cells. Pharm Res 2002, 19: 1488–1494. 10.1023/A:1020404615898PubMedView ArticleGoogle Scholar
- Spankuch B, Steinhauser I, Wartlick H, Kurunci-Csacsko E, Strebhardt KI, Langer K: Downregulation of Plk1 expression by receptor-mediated uptake of antisense oligonucleotide-loaded nanoparticles. Neoplasia 2008, 10: 223–234.PubMed CentralPubMedView ArticleGoogle Scholar
- Lynch I, Dawson KA, Linse S: Detecting cryptic epitopes created by nanoparticles. Sci STKE 2006, 2006: 14.Google Scholar
- Loccufier J, Vanbos M, Schacht E: Convenient method for the analysis of primary and secondary hydroxyl end groups in polyethers. Polym Bull 1991, 27: 201–204. 10.1007/BF00296031View ArticleGoogle Scholar
- Schrand AM, Rahman MF, Hussain SM, Schlager JJ, Smith DA, Syed AF: Metal-based nanoparticles and their toxicity assessment. Wiley Interdiscip Rev Nanomed Nanobiotechnol 2010, 2: 544–568. 10.1002/wnan.103PubMedView ArticleGoogle Scholar
- Suh HR, Jeong BM, Rathi R, Kim SW: Regulation of smooth muscle cell proliferation using paclitaxel-loaded poly(ethylene oxide)-poly(lactide/glycolide) nanospheres. J Biomed Mater Res 1998, 42: 331–338. 10.1002/(SICI)1097-4636(199811)42:2<331::AID-JBM19>3.0.CO;2-LPubMedView ArticleGoogle Scholar
- Zhang Y, Zhuo R-x: Synthesis and in vitro drug release behavior of amphiphilic triblock copolymer nanoparticles based on poly (ethylene glycol) and polycaprolactone. Biomaterials 2005, 26: 6736–6742. 10.1016/j.biomaterials.2005.03.045PubMedView ArticleGoogle Scholar
- Pan Y, Neuss S, Leifert A, Fischler M, Wen F, Simon U, Schmid G, Brandau W, Jahnen-Dechent W: Size-dependent cytotoxicity of gold nanoparticles. Small 2007, 3: 1941–1949. 10.1002/smll.200700378PubMedView ArticleGoogle Scholar
- Carlson C, Hussain SM, Schrand AM, Braydich-Stolle LK, Hess KL, Jones RL, Schlager JJ: Unique cellular interaction of silver nanoparticles: size-dependent generation of reactive oxygen species. J Phys Chem B 2008, 112: 13608–13619. 10.1021/jp712087mPubMedView ArticleGoogle Scholar
- Yu KO, Grabinski CM, Schrand AM, Murdock RC, Wang W, Gu BH, Schlager JJ, Hussain SM: Toxicity of amorphous silica nanoparticles in mouse keratinocytes. J Nanopart Res 2009, 11: 15–24. 10.1007/s11051-008-9417-9View ArticleGoogle Scholar
- Prabhu BM, Ali SF, Murdock RC, Hussain SM, Srivatsan M: Copper nanoparticles exert size and concentration dependent toxicity on somatosensory neurons of rat. Nanotoxicology 2010, 4: 150–160. 10.3109/17435390903337693PubMed CentralPubMedView ArticleGoogle Scholar
- Oberdorster G, Oberdorster E, Oberdorster J: Nanotoxicology: An emerging discipline evolving from studies of ultrafine particles. Environ Health Persp 2005, 113: 823–839. 10.1289/ehp.7339View ArticleGoogle Scholar
- Auffan M, Rose J, Bottero J-Y, Lowry GV, Jolivet J-P, Wiesner MR: Towards a definition of inorganic nanoparticles from an environmental, health and safety perspective. Nat Nanotechnol 2009, 4: 634–641. 10.1038/nnano.2009.242PubMedView ArticleGoogle Scholar
- Horie M, Fukui H, Nishio K, Endoh S, Kato H, Fujita K, Miyauchi A, Nakamura A, Shichiri M, Ishida N, et al.: Evaluation of acute oxidative stress induced by NiO nanoparticles in vivo and in vitro. J Occup Health 2011, 53: 64–74. 10.1539/joh.L10121PubMedView ArticleGoogle Scholar
- Kim S, Choi JE, Choi J, Chung KH, Park K, Yi J, Ryu DY: Oxidative stress-dependent toxicity of silver nanoparticles in human hepatoma cells. Toxicol in Vitro 2009, 23: 1076–1084. 10.1016/j.tiv.2009.06.001PubMedView ArticleGoogle Scholar
- Pujalte I, Passagne I, Brouillaud B, Treguer M, Durand E, Ohayon-Courtes C, L'Azou B: Cytotoxicity and oxidative stress induced by different metallic nanoparticles on human kidney cells. Part Fibre Toxicol 2011, 8: 10. 10.1186/1743-8977-8-10PubMed CentralPubMedView ArticleGoogle Scholar
- Stone V, Donaldson K: Nanotoxicology: Signs of stress. Nat Nanotechnol 2006, 1: 23–24.PubMedView ArticleGoogle Scholar
- Wang F, Gao F, Lan MB, Yuan HH, Huang YP, Liu JW: Oxidative stress contributes to silica nanoparticle-induced cytotoxicity in human embryonic kidney cells. Toxicol in Vitro 2009, 23: 808–815. 10.1016/j.tiv.2009.04.009PubMedView ArticleGoogle Scholar
- Jiang J, Oberdorster G, Elder A, Gelein R, Mercer P, Biswas P: Does nanoparticle activity depend upon size and crystal phase? Nanotoxicology 2008, 2: 33–42. 10.1080/17435390701882478PubMed CentralPubMedView ArticleGoogle Scholar
- Park J, Lim DH, Lim HJ, Kwon T, Choi JS, Jeong S, Choi IH, Cheon J: Size dependent macrophage responses and toxicological effects of Ag nanoparticles. Chem Commun 2011, 47: 4382–4384. 10.1039/c1cc10357aView ArticleGoogle Scholar
- Choi O, Hu ZQ: Size dependent and reactive oxygen species related nanosilver toxicity to nitrifying bacteria. Environ Sci Technol 2008, 42: 4583–4588. 10.1021/es703238hPubMedView ArticleGoogle Scholar
- Landsiedel R, Ma-Hock L, Kroll A, Hahn D, Schnekenburger J, Wiench K, Wohlleben W: Testing Metal-Oxide Nanomaterials for Human Safety. Adv Mater 2010, 22: 2601–2627. 10.1002/adma.200902658PubMedView ArticleGoogle Scholar
- Xia T, Kovochich M, Liong M, Zink JI, Nel AE: Cationic Polystyrene Nanosphere Toxicity Depends on Cell-Specific Endocytic and Mitochondrial Injury Pathways. ACS Nano 2007, 2: 85–96.View ArticleGoogle Scholar
- Xia T, Kovochich M, Brant J, Hotze M, Sempf J, Oberley T, Sioutas C, Yeh JI, Wiesner MR, Nel AE: Comparison of the abilities of ambient and manufactured nanoparticles to induce cellular toxicity according to an oxidative stress paradigm. Nano Lett 2006, 6: 1794–1807. 10.1021/nl061025kPubMedView ArticleGoogle Scholar
- Frohlich E, Samberger C, Kueznik T, Absenger M, Roblegg E, Zimmer A, Pieber TR: Cytotoxicity of nanoparticles independent from oxidative stress. J Toxicol Sci 2009, 34: 363–375. 10.2131/jts.34.363PubMedView ArticleGoogle Scholar
- Monteiller C, Tran L, MacNee W, Faux S, Jones A, Miller B, Donaldson K: The pro-inflammatory effects of low-toxicity low-solubility particles, nanoparticles and fine particles, on epithelial cells in vitro: the role of surface area. Occup Environ Med 2007, 64: 609–615. 10.1136/oem.2005.024802PubMed CentralPubMedView ArticleGoogle Scholar
- Trickler WJ, Lantz SM, Murdock RC, Schrand AM, Robinson BL, Newport GD, Schlager JJ, Oldenburg SJ, Paule MG, Slikker W, et al.: Silver nanoparticle induced blood-brain barrier inflammation and increased permeability in primary rat brain microvessel endothelial cells. Toxicol Sci 2010, 118: 160–170. 10.1093/toxsci/kfq244PubMedView ArticleGoogle Scholar
- Liu R, Zhang XY, Pu YP, Yin LH, Li YH, Zhang XQ, Liang GY, Li XB, Zhang J: Small-sized titanium dioxide nanoparticles mediate immune toxicity in rat pulmonary alveolar macrophages in vivo. J Nanosci Nanotechno 2010, 10: 5161–5169. 10.1166/jnn.2010.2420View ArticleGoogle Scholar
- Hanley C, Thurber A, Hanna C, Punnoose A, Zhang JH, Wingett DG: The influences of cell type and ZnO nanoparticle size on immune cell cytotoxicity and cytokine induction. Nanoscale Res Lett 2009, 4: 1409–1420. 10.1007/s11671-009-9413-8PubMed CentralPubMedView ArticleGoogle Scholar
- Win KY, Feng SS: Effects of particle size and surface coating on cellular uptake of polymeric nanoparticles for oral delivery of anticancer drugs. Biomaterials 2005, 26: 2713–2722. 10.1016/j.biomaterials.2004.07.050PubMedView ArticleGoogle Scholar
- Johnston HJ, Semmler-Behnke M, Brown DM, Kreyling W, Tran L, Stone V: Evaluating the uptake and intracellular fate of polystyrene nanoparticles by primary and hepatocyte cell lines in vitro. Toxicol Appl Pharmacol 2010, 242: 66–78. 10.1016/j.taap.2009.09.015PubMedView ArticleGoogle Scholar
- Oh W-K, Kim S, Choi M, Kim C, Jeong YS, Cho B-R, Hahn J-S, Jang J: Cellular uptake, cytotoxicity, and innate immune response of silica − titania hollow nanoparticles based on size and surface functionality. ACS Nano 2010, 4: 5301–5313. 10.1021/nn100561ePubMedView ArticleGoogle Scholar
- Lai SK, Hida K, Man ST, Chen C, Machamer C, Schroer TA, Hanes J: Privileged delivery of polymer nanoparticles to the perinuclear region of live cells via a non-clathrin, non-degradative pathway. Biomaterials 2007, 28: 2876–2884. 10.1016/j.biomaterials.2007.02.021PubMedView ArticleGoogle Scholar
- Foged C, Brodin B, Frokjaer S, Sundblad A: Particle size and surface charge affect particle uptake by human dendritic cells in an in vitro model. Int J Pharm 2005, 298: 315–322. 10.1016/j.ijpharm.2005.03.035PubMedView ArticleGoogle Scholar
- Zhang SL, Li J, Lykotrafitis G, Bao G, Suresh S: Size-dependent endocytosis of nanoparticles. Adv Mater 2009, 21: 419–424. 10.1002/adma.200801393PubMed CentralPubMedView ArticleGoogle Scholar
- Bao G, Bao XR: Shedding light on the dynamics of endocytosis and viral budding. Proc Natl Acad Sci 2005, 102: 9997–9998. 10.1073/pnas.0504555102PubMed CentralPubMedView ArticleGoogle Scholar
- Gao HJ, Shi WD, Freund LB: Mechanics of receptor-mediated endocytosis. Proc Natl Acad Sci 2005, 102: 9469–9474. 10.1073/pnas.0503879102PubMed CentralPubMedView ArticleGoogle Scholar
- Tzlil S, Deserno M, Gelbert WM, Ben-Shaul A: A statistical-thermodynamic model of viral budding. Biophys J 2004, 86: 2037–2048. 10.1016/S0006-3495(04)74265-4PubMed CentralPubMedView ArticleGoogle Scholar
- Chithrani BD, Chan WCW: Elucidating the mechanism of cellular uptake and removal of protein-coated gold nanoparticles of different sizes and shapes. Nano Lett 2007, 7: 1542–1550. 10.1021/nl070363yPubMedView ArticleGoogle Scholar
- Jiang W, KimBetty YS, Rutka JT, Warren CWC: Nanoparticle-mediated cellular response is size-dependent. Nat Nanotechnol 2008, 3: 145–150. 10.1038/nnano.2008.30PubMedView ArticleGoogle Scholar
- Thurn KT, Brown EMB, Wu A, Vogt S, Lai B, Maser J, Paunesku T, Woloschak GE: Nanoparticles for applications in cellular Imaging. Nanoscale Res Lett 2007, 2: 430–441. 10.1007/s11671-007-9081-5PubMed CentralPubMedView ArticleGoogle Scholar
- Rejman J, Oberle V, Zuhorn IS, Hoekstra D: Size-dependent internalization of particles via the pathways of clathrin-and caveolae-mediated endocytosis. Biochem J 2004, 377: 159–169. 10.1042/BJ20031253PubMed CentralPubMedView ArticleGoogle Scholar
- Oh JM, Choi SJ, Lee GE, Kim JE, Choy JH: Inorganic metal hydroxide nanoparticles for targeted cellular uptake through clathrin-mediated endocytosis. Chem-Asian J 2009, 4: 67–73. 10.1002/asia.200800290PubMedView ArticleGoogle Scholar
- Stahl PD, Ezekowitz RAB: The mannose receptor is a pattern recognition receptor involved in host defense. Curr Opin Immunol 1998, 10: 50–55. 10.1016/S0952-7915(98)80031-9PubMedView ArticleGoogle Scholar
- Park IY, Kim IY, Yoo MK, Choi YJ, Cho M-H, Cho CS: Mannosylated polyethylenimine coupled mesoporous silica nanoparticles for receptor-mediated gene delivery. Int J Pharm 2008, 359: 280–287. 10.1016/j.ijpharm.2008.04.010PubMedView ArticleGoogle Scholar
- Cui ZR, Hsu CH, Mumper RJ: Physical characterization and macrophage cell uptake of mannan-coated nanoparticles. Drug Dev Ind Pharm 2003, 29: 689–700. 10.1081/DDC-120021318PubMedView ArticleGoogle Scholar
- Kim TH, Jin H, Kim HW, Cho MH, Cho CS: Mannosylated chitosan nanoparticle-based cytokine gene therapy suppressed cancer growth in BALB/c mice bearing CT-26 carcinoma cells. Mol Cancer Ther 2006, 5: 1723–1732. 10.1158/1535-7163.MCT-05-0540PubMedView ArticleGoogle Scholar
- Rieger J, Freichels H, Imberty A, Putaux JL, Delair T, Jerome C, Auzely-Velty R: Polyester nanoparticles presenting mannose residues: toward the development of new vaccine delivery systems combining biodegradability and targeting properties. Biomacromolecules 2009, 10: 651–657. 10.1021/bm801492cPubMedView ArticleGoogle Scholar
- Gentili PL, Mugnai M, Bussotti L, Righini R, Foggi P, Cicchi S, Ghini G, Viviani S, Brandi A: The ultrafast energy transfer process in naphtole-nitrobenzofurazan bichromophoric molecular systems - A study by ferntosecond UV-vis pump-probe spectroscopy. J Photoch Photobio A 2007, 187: 209–221. 10.1016/j.jphotochem.2006.10.020View ArticleGoogle Scholar
- Khoee S, Hassanzadeh S, Goliaie B: Effects of hydrophobic drug-polyesteric core interactions on drug loading and release properties of poly(ethylene glycol)-polyester-poly(ethylene glycol) triblock core-shell nanoparticles. Nanotechnology 2007, 18: 175602. 10.1088/0957-4484/18/17/175602View ArticleGoogle Scholar
- van Berlo D, Haberzettl P, Gerloff K, Li H, Scherbart AM, Albrecht C, Schins RPF: Investigation of the Cytotoxic and Proinflammatory Effects of Cement Dusts in Rat Alveolar Macrophages. Chem Res Toxicol 2009, 22: 1548–1558. 10.1021/tx900046xPubMedView ArticleGoogle Scholar
- Howard KA, Paludan SR, Behlke MA, Besenbacher F, Deleuran B, Kjems J: Chitosan/siRNA Nanoparticle-mediated TNF-alpha Knockdown in Peritoneal Macrophages for Anti-inflammatory Treatment in a Murine Arthritis Model. Mol Ther 2009, 17: 162–168. 10.1038/mt.2008.220PubMed CentralPubMedView ArticleGoogle Scholar
- Hislop JN, Everest HM, Flynn A, Harding T, Uney JB, Troskie BE, Millar RP, McArdle CA: Differential Internalization of Mammalian and Non-mammalian Gonadotropin-releasing Hormone Receptors. J Biol Chem 2001, 276: 39685–39694. 10.1074/jbc.M104542200PubMedView ArticleGoogle Scholar
- Srinivasan D, Fujino H, Regan JW: Differential Internalization of the Prostaglandin F2α Receptor Isoforms: Role of Protein Kinase C and Clathrin. J Pharmacol Exp Ther 2002, 302: 219–224. 10.1124/jpet.302.1.219PubMedView ArticleGoogle Scholar
- Stuart AD, Brown TDK: Entry of feline calicivirus is dependent on clathrin-mediated endocytosis and acidification in endosomes. J Virol 2006, 80: 7500–7509. 10.1128/JVI.02452-05PubMed CentralPubMedView ArticleGoogle Scholar
- Xu X, Xie Q, Shen Y, Lu G, Yao H, Chen Y, Zhou J: Involvement of mannose receptor in the preventive effects of mannose in lipopolysaccharide-induced acute lung injury. Eur J Pharmacology 2010, 641: 229–237. 10.1016/j.ejphar.2010.05.021View ArticleGoogle Scholar
This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.