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Lanthanide nanoparticles and nanorods have been widely used for diagnostic and therapeutic applications in biomedical nanotechnology due to their fluorescence properties and pro-angiogenic to endothelial cells, respectively. Recently, we have demonstrated that europium (III) hydroxide [EuIII(OH)3] nanorods, synthesized by the microwave technique and characterized by several physico-chemical techniques, can be used as pro-angiogenic agents which introduce future therapeutic treatment strategies for severe ischemic heart/limb disease, and peripheral ischemic disease. The toxicity of these inorganic nanorods to endothelial cells was supported by several in vitro assays. To determine the in vivo toxicity, these nanorods were administered to mice through intraperitoneal injection (IP) everyday over a period of seven days in a dose dependent (1.25 to 125 mgKg−1day−1) and time dependent manner (8–60 days). Bio-distribution of europium elements in different organs was analyzed by inductively coupled plasma mass spectrometry (ICPMS). Short-term (S-T) and long-term (L-T) toxicity studies (mice sacrificed on day 8 and 60 for S-T and L-T, respectively) show normal blood hematology and serum clinical chemistry with the exception of a slight elevation of liver enzymes. Histological examination of nanorod treated vital organs (liver, kidney, spleen and lungs) showed no or only mild histological changes that indicate mild toxicity at the higher dose of nanorods.
Nanoscience and nanotechnology are cutting edge technologies that are devoted to understand, create, design and use material structures, devices and systems at the atomic, molecular, or macromolecular range (~1–100 nanometers) with fundamentally new properties and function (Alivisatos et al., 1996; Craighead, 2000; Alivisatos, 2004; Patra et al., 2005; Patra et al., 2006; Patra et al., 2007; Patra et al., 2008a; Patra et al., 2008b; Patra et al., 2008c; Patra et al., 2008d; Patra et al., 2008e). Nanomedicine is the biomedical application of nanotechnology. Nanoparticles or nanorods have been widely used for useful research tools, advanced drug delivery systems (DDS), and new ways to detect and treat disease or repair damaged tissues and cells (Alivisatos et al., 1996; Bruchez et al., 1998; Parak et al., 2003; Alivisatos, 2004; Gao et al., 2004; Thrall, 2004; Gao et al., 2005; Jain, 2005a; Jain, 2005b; Medintz et al., 2005; Michalet et al., 2005; Prescher and Bertozzi, 2005; Patra et al., 2008a; Patra et al., 2008b; Patra et al., 2008c). In this context, several groups including our group have demonstrated that lanthanide (Eu, Tb, Gd) elements/nanoparticles play important roles in biology and medicine due to their unique physical, chemical, and electronic properties (Misra et al., 2004; Sigel and Sigel, 2004; Authors, 2006; Patra et al., 2006; Thompson and Orvig, 2006; Yu et al., 2006; Patra et al., 2007; Patra et al., 2008b; Patra et al., 2009). Recently, we have demonstrated that europium hydroxide [EuIII(OH)3] nanorods (inorganic nanorods) exhibit significant pro-angiogenic activities (Patra et al., 2008b). It is well established that the most important objective of angiogenesis (process involving the growth of new blood vessels from pre-existing vasculature) is to induce or stimulate vessel growth in patients with conditions characterized by insufficient blood flow, such as ischemic heart disease (IHD) and peripheral vascular diseases(Folkman and Shing, 1992; Folkman, 1993; Folkman, 1995; Risau, 1997; Isner and Losordo, 1999; Yancopoulos et al., 2000; Chavakis and Dimmeler, 2002; Dardik et al., 2005 Basu, 2001 #42; Folkman, 1974). Considering the overall impact of angiogenesis in our health care system, the pro-angiogenic properties of EuIII(OH)3 nanorods could be used to develop new treatment strategies for ischemic heart/limb disease, (Huston et al., 1999; Jones et al., 2002; Ebrahimian et al., 2006) in the near future. However, applications of any nanoparticles and nanorods in biomedical technology require that the nanoparticles/nanorods should be non-toxic in vivo. It is reported that exposure to certain nanomaterials and metallic salts of lanthanides might lead to adverse biological effects; this appears to be dependent upon the chemical and physical properties of the material (Ogawa et al., 1995; Shimada et al., 1996; Hirano and Suzuki, 1996 ; Jaiswal et al., 2003; Derfus et al., 2004; Gao et al., 2004; Gao et al., 2005). Our preliminary results demonstrated that these nanorods are not toxic to endothelial cells as observed by apoptosis assay and other in vitro assays (Patra et al., 2006; Patra et al., 2007; Patra et al., 2008b) as well as in vivo assay (CAM assay) (Patra et al., 2008b). These encouraging findings prompted us to further evaluate the in vivo toxicity in mice models. There are some reports on the toxicity study of lanthanide compounds (salts or chelates) (Haley et al., 1965; Ogawa et al., 1995; Shimada et al., 1996; Hirano and Suzuki, 1996 ; Zhang et al., 2002). Although Haley et al. in 1965 (Haley et al., 1965) reported the pharmacological and toxicological properties of europium chloride in mice models, there is not a single report on in vivo toxicity study using lanthanide nanoparticles or nanorods, especially EuIII(OH)3 nanorods. Again, the efficacy of these EuIII(OH)3 nanorods in promoting angiogenesis in the mammalian heart/limb and its feasibility, safety, and bio-availabilities with in vivo use has not been established. Since nanoparticles may interact with biological systems in unforeseen ways, an in vivo toxicity study of EuIII(OH)3 is one of the important steps before applying these nanomaterials for in vivo use.
In this present article our goal is to study in vivo bio-toxicity and bio-availabilities of EuIII(OH)3 nanorods in mice models in a systematic way. We have examined short-term (S-T: mice sacrificed on day eight after seven days of consecutive IP injections of nanorods) (acute) and long-term (L-T: mice sacrificed on day 60) (chronic) in vivo toxicity of EuIII(OH)3 nanorods and their bio-availabilities in mice models. We have collected the various vital organs (liver, spleen, lungs, kidney) and performed histopathological examination using H&E staining to compare the acute and chronic toxicity of controlled tissue vs. nanorod treated tissue. We have also determined bio-distribution of the europium element in different organs using inductively coupled plasma mass spectrometry (ICP-MS). Intraperitoneal (IP) injection of EuIII(OH)3 nanorods in mice at different doses (1.25 to 125 mgKg−1day−1) has not shown any biochemical and hematological toxicities with the exception of a slight elevation of liver enzymes. Histological examination of nanorod-treated vital organs (liver, kidney, spleen and lungs) assayed on day eight (S-T) or 60 (L-T) showed none or only mild histological changes that indicated mild toxicity with the higher dose of nanorods. The remarkable findings of pro-angiogenic and fluorescence properties and non-toxic behavior of EuIII(OH)3 nanorods suggests that these nanorods could be used for future therapeutic alternative treatment strategies for severe ischemic heart disease, peripheral ischemic disease, and limb ischemic disease.
Europium (III)nitrate hydrate [Eu(NO3)3.xH2O, 99.99%] and aqueous ammonium hydroxide [aq.NH4OH, 28–30% ] were purchased from Aldrich, USA and were used without further purifications. The human umbilical vein endothelial cells (HUVEC) and its individual components for making EBM complete media were purchased from Cambrex Bio Science Walkersville, Inc, MD, USA. TUNEL labeling assay kit (In Situ Cell Death Detection Kit: Cat. No.#12 156 792 910) was purchased from Roche Applied Science, IN, USA.
Synthesis of EuIII(OH)3 nanorods was carried out in a modified domestic microwave oven (DMO) prepared using an interaction in an aqueous solution of Europium(III)nitrate and aq.NH4OH using microwave (MW) irradiation (Patra et al., 2008b). In a typical synthesis, 10 ml of aqueous NH4OH were added to 20 ml of a 0.05 (M) aqueous solution of Eu(III)nitrate(pH = 5.5) in a 100 ml round-bottomed flask and were irradiated for 5 to 60 min with 60% of the instrument’s power (on/off irradiation cycles ratio of 3/2) in order to control the reaction and reduce the risk of superheating the solvent. A white and colloidal precipitate, without any special morphology, was obtained upon the addition of NH4OH to the Eu(III) nitrate solution in absence of MW heating. The pH of the solution before and after the reaction was measured and these were 9.4 and 7.5, respectively. The microwave refluxing apparatus is a modified domestic microwave oven (GOLD STAR 1000W with a 2.45 GHz) (Matsumurainoue et al., 1994; Patra et al., 2008b) In the post-reaction treatment the resulting products were collected, centrifuged, washed several times using distilled water, and then dried overnight under vacuum at room temperature. The yield of the as-prepared products was more than 95%.
100 mg of solid crystalline EuIII(OH)3 nanorods were added into 10 ml of sterile TE (tris- EDTA) buffer and kept five min in a sonicator bath to make a homogeneous suspension of 10 mg/ml (stock solution). The freshly prepared suspension in TE buffer was used for all cell culture experiments and in vivo toxicity experiments.
The milipore H2O, used for all experiments in our research, was tested for endotoxin using the Gel clot method according to manufacturer’s instructions (Cat # GS 250Cape Cod Associates, Cape Cod). The formation of a gel-clot indicates the presence of endotoxin in a sample. However, we have not found any gel-clot confirming the absence of endotoxin in the water. Similarly, prior to incubation with endothelial cells (HUVECs) for apoptosis studies, we tested the nanorods suspension in TE-buffer for possible endotoxin contamination.
In the TUNEL assay, cells were seeded into 6-well plates at a density of 105 in 2 ml of medium per well and grown overnight on cover slips at 37°C and 5% CO2 in EBM complete media. The cells were then treated with EuIII(OH)3 nanorods and allowed for another 24 hours of incubation at different concentrations (0–100 μg/ml). After 24 hrs of incubation, the cover slips were rinsed extensively with PBS, and cells were fixed with freshly prepared 4% para-formaldehyde in PBS for 15 min at room temperature and then re-hydrated with PBS. Once all the cells were fixed, the cover slips were mounted onto glass slides with Fluor Save mounting media and used for confocal microscopy. For the TUNEL assay, cells were mounted onto glass slides with mounting media containing DAPI (4′-6-Diamidino-2-phenylindole) and examined with confocal microscopy according to the manufacturer’s instructions. The apoptotic cells were counted (6 fields per sample) and photographed using a digital fluorescence camera.
Six to eight-week-old male wild type mice (C57BL6) were purchased from the National Cancer Institute (NCI), USA. All mice experiments were done under protocols approved by the Mayo Clinic Institutional Animal Care and Use Committee (IACUC).
EuIII(OH)3 nanorods suspension in TE buffer with different concentrations (1.25 mgKg−1day−1, 12.5 mgKg−1day−1 and 125 mgKg−1day−1) was administered to each mouse through intraperitonial injection (IP) every day with the help of a tuberculin syringe over a period of seven days. In the control group, an equal volume of TE buffer was injected through IP in the same way. Each group contained ten mice. Mice were classified as a short-term (S-T) toxicity study (acute toxicity study) and a long-term (L-T) toxicity study (chronic toxicity study) where mice were sacrificed on day 8 and day 60, respectively, for examination for biochemical toxicity studies, hematological toxicity studies, and histological studies. Mice were allowed free access to autoclaved standard pellet food and sterile water throughout the experiments. Animals were weighed and observed regularly for clinical signs and monitored daily for morbidity and mortality. At least ten mice were used in each set.
We would like to introduce why we have chosen this wide dose range (1.25–125 mgKg−1day−1) of EuIII(OH)3 nanorods. According to existing literature, we have not found a single report on in vivo toxicity of lanthanide nanoparticles or nanorods, especially EuIII(OH)3 nanorods. Cell proliferation experiments showed that up to 100 μg of nanorods are not toxic to endothelial cells according to our published literature. (Patra et al., 2008b) However, in the case of the in vivo angiogenesis (CAM assay: chick chorioallantoic membrane) assay, we have observed the toxic effect of nanorods at a concentration of 20 μg. These observations indicate that the toxic effect of EuIII(OH)3 nanorods can vary from the in vitro to the in vivo condition. Therefore, in order to determine the systematic in vivo toxicity of these inorganic nanorods in mice models, we have selected three doses (wide range) from 1.25 mg−1Kg−1day−1 (lowest) to 125 mg−1Kg−1day−1(highest). Ogawa et al. (Ogawa et al., 1995) experimented with a toxicity study of europium chloride salt (not nanorods/particles) in rats at a maximum dose of 1000 mg/Kg/day, and they concluded that the no-observed effect level was 200 mg/Kg/day. Again, Bruce et al. (Bruce et al., 1963) reported an intraperitoneal LD50 for europium nitrate in female mice of 320 mg/kg and in female rats of 210 mg/kg. The oral LD50 in the latter species was 75 Gm. This is also another reason for using a wider dose range (1.25–125 mg−1Kg−1day−1) of EuIII(OH)3 nanorods in order to study their biocompatibility, efficacy, feasibility, safety, and bio-availability.
We have chosen the administration of EuIII(OH)3 nanorods by intraperitoneal (IP) injection as it is predominantly used for its ease of administration compared to other parenteral methods during animal testing for the administration of systemic drugs and fluids. Additionally, we can administer a large volume of EuIII(OH)3 nanorod suspensions (~100 μl) to the mice if we choose this IP route compared to the intravenous (IV) method. For our in vivo toxicity experiments, we have injected a constant volume of 100 μl of nanorod solution to the control as well as the experimental group. However, we can’t inject this large volume of solution via the intravenous (IV) route. For these reasons, we have chosen IP administration vs. the intravenous route.
Mice were sacrificed on day eight (short-term) and on day 60 (long-term) from the date of injection to determine the acute toxicity and chronic toxicity of EuIII(OH)3 nanorods through examination of their blood chemistry profiles. Blood was collected by intracardiac puncture following anesthesia with ketamine-xylazine. Whole blood was immediately heparinized for hematological toxicity. Hematology analysis includes CBC without differential hemoglobin (g/dL), hematocrit (%), erythrocytes [x10(12)/L, mean cell volume (MCV) (fL), RBC distribution width (%), Leukocytes [x10(9)/L] and platelet count [x10(9)/L]. In another set of experiments whole blood was placed in a clotted vial and centrifuged, and collected serum was submitted for biochemical analysis. Serum biochemical analysis was carried out to determine the serum level of alkaline phosphates (ALP), aspartate aminotransferase (AST), alanine aminotransferase (ALT), Phosphorus (Inorganic), calcium, albumin, creatinine (CRN), glucose, total protein (TP), total bilirubin (TBLi), blood urea nitrogen (BUN), etc (Hainfeld et al., 2006).
After intraperitonial injection (IP) each day with different doses (0 mgKg−1day−1, 1.25 mgKg−1day−1, 12.5 mgKg−1day−1 and 125 mgKg−1day−1) over a period of seven days, the animals were sacrificed. The vital organs (liver, kidney, spleen and lungs) were collected from the mice sacrificed on day eight (S-T toxicity study) and day 60 (L-T toxicity study) and fixed with a 10% formalin neutral buffer solution, embedded in paraffin, and cut into 5-μm-thick sections. Sections were stained with hematoxylin and eosin (H&E) staining for general histology according to our published literature (Reinders et al., 2003). Reporting and representation of histologic findings is dependent upon the subjective judgment of the investigator. To avoid this to some extent, the evaluation should be blinded and the slides should be randomized. Therefore, the slides for H&E staining were randomized using some secret code numbers and evaluated blindly by a pathologist. The results were again re-analyzed by another pathologist in the same way.
We have also collected the vital organs (liver, kidney, spleen and lung) separately and submitted them for inductively coupled plasma mass spectrometry (ICP-MS) analysis for the determination of europium elements in order to evaluate the bio-distribution of europium in different vital organs.
Characterization techniques for EuIII(OH)3 nanorods are described briefly as follows.
The structure and phase purity of the as–synthesized samples were determined by X-ray diffraction (XRD) analysis using a Bruker AXS D8 Advance Powder X-ray diffractometer (using CuKαλ =1.5418 Å radiation).
The particle morphology (microstructures of the samples) was studied with TEM on a FEI Technai 12 operating at 80KV.
The collected organs (liver, kidney, spleen, lungs) were weighed and then dissolved in a 75% HNO3 solution (by volume) such that the amount of acid added was equal to ten times the weight of the sample (wet). The samples were then heated overnight at 50 °C with occasional venting by loosening the caps. The resulting solution was then diluted with deionized water up to a total dilution of 200 times the original weight of the sample. These solutions were again heated overnight at 50 °C. Finally, the solutions were cooled and diluted another 10 fold with the addition of yttrium as an internal standard element and subsequently analyzed on the ICP-MS. We used calibration standards at 0.1, 1.0, and 10.0 ppm Eu for the analysis. We analyzed the samples at three different Eu emission lines (Eu3819, Eu3907 and Eu41290) to insure that there were no spectral interferences. All lines were observed from an axial viewpoint of the plasma to increase sensitivity. The mean and standard deviation data were based on five replicates per sample. Several of the samples were re-diluted and analyzed as duplicates to insure reproducibility.
Mean and standard deviations were calculated. We have calculated the P values using the ‘Student-Newman-Keuls Multiple Comparisons Test’ (ANOVA) by comparing different groups (control group vs. treatment groups), and we found that these values are considered not significant (P > 0.05) (Table 1–4).
The crystal structure of the as-synthesized products were identified using X-ray diffraction (XRD) analysis (Fig. 1). XRD pattern of as-synthesized nanorods, obtained after 60 min MW heating indicated the crystalline nature of the product (Fig. 1). All reflections are distinctly indexed to a pure hexagonal phase of EuIII(OH)3 materials. No peaks from other phases were detected. The diffraction peaks were consistent with the standard data files (the JCPDS card No. 01-083-2305) for all reflections.
The morphologies of the as-synthesized materials were characterized by low-resolution transmission electron microscopy (LRTEM). Fig. 2(a–b) depicts the TEM images of EuIII(OH)3 materials at low magnification (Fig. 2a) and high magnification (Fig. 2b), respectively. The TEM images clearly show that the EuIII(OH)3 materials entirely consists of nanorods with a diameter 35– 50 nm and length in 200–300 nm.
The exact mechanism for the formation of Eu(OH)3 nanorods using microwave irradiation under a solvothermal condition needs further investigation. Eu(OH)3 nanorods that were fabricated have a hexagonal crystal structure similar to that of ZnO (Huang et al., 2001) and Ln(OH)3 (Wang and Li, 2002; Xu et al., 2003) and LnPO4 (Ln = La -Dy) nanowires (Fang et al., 2003), which are well-known to exhibit anisotropic growth. In this solution phase process, the morphology of the final product was largely determined by the anisotropic nature of the building block, that is, the 1-D characteristic of the infinite hexagonal chains in the crystalline phase. Eu(OH)3 has a hexagonal crystal structure; therefore, the formation of the Eu(OH)3 nanorods can be explained by its highly anisotropic growth.
We suggest that the high microwave susceptibility of water (dielectric constant e = 80.4) makes it an excellent microwave-absorbing agent, thus leading to high heating rates and significantly shortened reaction times. The movement and polarization of water molecules under the rapidly changing electric field of the microwave reactor may result in transient, anisotropic microdomains for the reaction system, facilitating the anisotropic growth of Eu(OH)3 nanorods (Patra et al., 2005; Mazloumi et al., 2009).
In order to determine the chemical nature of the as-synthesized products, it was further characterized by thermo gravimetric analysis (TGA) and differential scanning calorimetric (DSC) analysis according to our earlier literature (Patra et al., 2008b). The combined results of XRD, TEM, TGA and DSC indicating that as-synthesized product is crystalline EuIII(OH)3 nanorods.
Recently, we have already demonstrated the pro-angiogenic properties of EuIII(OH)3 nanorods through various in vitro (such as cell proliferation assay using [3H]-Thymidine, cell cycle assay) and in vivo analyses (CAM: chick chorioallantoic membrane assays) (Patra et al., 2008b). Like other pro-angiogenic cytokines, these nanorods promote in vitro endothelial cell proliferation and in vivo angiogenic sprouting in CAM assays. The internalization of EuIII(OH)3 nanorods inside the cells was visualized with a TEM according to previously published procedures (McDowell and Trump, 1976; Spurr, 1969). We have already demonstrated that mitogen activated protein kinase (MAPK) activation and formation of reactive oxygen species (ROS) is the plausible mechanism for inorganic nanorods induced angiogenesis.
One of the main purposes of the current study was to evaluate the potential toxicity of Eu(OH)3 nanorods. In order to obtain detailed information of toxicity, we performed in vivo serum biochemical analysis, blood chemistry, histopathological examination, and in vitro apoptosis assays. The toxicity of these inorganic nanorods to endothelial cells was further supported by apoptosis assay/TUNEL assay (dUTP nick-end labeling) and is shown in Fig. 3. To determine the toxicity of these nanorods, we performed the TUNEL assay on HUVECs in the presence of these nanorods according to published literatures (Wu et al., 2002; Chen et al., 2006; Patra et al., 2006; Patra et al., 2007; Patra et al., 2008b). As we have already demonstrated cell viability tests using a trypan blue dye exclusion test, apoptosis assay, cell proliferation assay, cell cycle assay, etc. in our published literature (Patra et al., 2008b), therefore we have not presented the similar in vitro data in this article. Fig. 3.a illustrates the TUNEL assay of HUVECs treated with tris-EDTA buffer (−Ve control experiment) where we have not found any red apoptotic nuclei indicating no apoptosis. Fig. 3.b shows the TUNEL assay of HUVECs treated with camptothecin for 4h at 37°C as a positive inducer where red nuclei indicate the apoptosis of all HUVEC cells. Apoptosis assay of HUVECs treated with EuIII(OH)3 nanorods (50 μg/mL) were presented in Fig. 3c where we did not observe any apoptotic cells. However, HUVECs treated with nanorods at the concentration of 100 μg/mL (Fig. 3.d) show some red apoptotic cells indicating that a higher concentration of nanorods are apoptotic (~8%) to endothelial cells. Results from the TUNEL assay clearly demonstrated that at concentrations up to 50 μg/ml of EuIII(OH)3 nanorods, there was no induction of apoptosis in HUVECs.
Recently, the potentially hazardous health effects of nanoparticles are emerging issues among toxicologists and regulatory authorities. Nanotechnology will indeed develop in areas where potential advantages would exceed potential risks and where the potential risks are limited and can be addressed (Roco, 2003). Current approaches strongly suggest that consequences of nanotechnology are best addressed within the existing system applications such as biology, chemistry, or electronics. The aim of current study is to determine the distribution pattern and potential toxicity of inorganic nanorods using EuIII(OH)3 nanorods and histopathological changes of organs in the presence of these nanorods. EuIII(OH)3 nanorod suspension in TE buffer with different concentrations (1.25 mgKg−1day−1, 12.5 mgKg−1day−1 and 125 mgKg−1day−1) was administered to each mouse through intraperitonial injection (IP) each day over a period of seven days. Briefly, on day eight and day 60 toxicity studies using 60 mice with intraperitonial injection of EuIII(OH)3 nanorods (maximum dose125 mgKg−1day−1) showed normal hematology (Table-1 & -3) and blood chemistry (Table -2 & -4). Histological examination of vital organs including liver, kidney, spleen, and lungs from each mouse, assayed on day eight or day 60 after injection of nanorods showed none or only mild histological changes indicating evidence of mild toxicity at the highest dose of nanorods (Fig. 4.a–p). None of those mice were dead; and we have not observed any significant change in the average weight loss, or any adverse effect of mice before and after the administration of EuIII(OH)3 for S-T and L-T toxicity studies even at highest dose (125 mg/Kg/day/mice). We have also collected and taken the weight of the specific organs (liver, kidney, lungs, spleen) after sacrificing the mice on day eight and day 60, and we have not observed any significant change of weight of different organs.
Blood tests done on day eight or 60 of the acute-toxicity experiments do not suggest any significant systemic toxicity at any of the dose levels (Table 1–4) except the slight elevation of liver enzymes, especially AST, for only the S-T toxicity study. In particular, even at the highest dose levels (dose125 mgKg−1day−1), inorganic nanorods do not cause anemia, neutropenia, lymphopenia, or thrombocytopenia suggestive of hematological toxicity (Table-1 and --3).3). The hematology and blood chemistry data of control mice are in the range with previously reported data (Hainfeld et al., 2006). The normal range of creatinine and blood urea nitrogen (BUN) are between 0.2–0.4 mg dl−1 and 26–33 mg dl−1, respectively (Hainfeld et al., 2006). In our case, we have observed the normal value of creatinine and BUN are 0.1±0 mg dl−1 and 222±8, respectively. There is no difference in the value of BUN or creatinine in the blood of inorganic nanorod treated mice and control mice indicating no renal toxicity (Table-2 & -4) (Limpeanchob et al., 2006). Liver enzymes are normally found within the cells of the liver. If the liver is injured or damaged, the liver enzymes spill into the blood, causing elevated liver enzyme levels. According to reported literature (Hainfeld et al., 2006), the normal range of AST, ALT, ALP and AST/ALT in Balb/C mice are in the range of 38.8±9.9 to 123±52.5; 40.8±6.7 to 226±105; 100.4±28 to180±60; 1.8± 0.5 to 6.0± 2.5, respectively. There are slight elevations of liver enzymes, especially aspartate aminotransferase (AST) and alanine aminotransferase (ALT) in inorganic nanorod treated mice compared to untreated mice (Table-2). Although the AST level was increased (observed only for short term toxicity study; Table-2) in response to EuIII(OH)3 nanorods, bilirubin whole (0.1 mg/dL) is the most important factor for advanced liver toxicity and did not increase. Again, for the long-term (L-T) toxicity study we did not find any significant difference of ALT & AST values between control untreated mice and nanorod treated mice even at the high dose of 125 mg/Kg/day. The clinical significance of the increase in ALT & AST requires more investigation in future studies (Shah et al., 2001). However, there is no significant change in the ratio of AST to ALT between controlled, untreated and nanorod treated mice for S-T and as well as L-T toxicity studies (Hainfeld et al., 2006).
In human blood, albumin is the main protein (the primary component of total protein); and it is made by the liver. There is no change of albumin in nanorod treated mice compared to normal untreated mice indicating no liver disease which results in decreased albumin production. Elevated bilirubin levels can be indicative of liver disorders or blockage of bile ducts. However, we have not observed any elevation of bilirubin between control untreated mice and nanorod treated mice indicating no liver abnormalities. Other blood tests can also signal liver function problems by detecting abnormalities involving plasma proteins and blood clotting factors. No change of total protein plasma proteins (albumin and globulins) between control and nanorod treated mice indicating no abnormalities in liver even at highest dose of nanorod treatment. The inorganic phosphorous (P) in the form of phosphate has physiologic and pathologic importance in maintaining the neutrality of blood and tissue owing to a remarkable capacity for binding acid and base. In serum clinical chemistry data, total phosphorous, calcium, albumin, creatinine, glucose were not affected by the treatment of EuIII(OH)3 nanorods in mice compared to untreated mice. The combined blood hematology and serum clinical chemistry data (Table 1–4) do not show any sub clinical systemic toxicity detectable by our laboratory tests (Uckun et al., 2002).
Histological studies are considered to be a reliable method to detect structural changes due to toxicities(Reinders et al., 2003). The histopathological findings of liver, kidney, spleen and lung for the S-T study are presented in Fig. 4.(a–p).
The sections from control animals are showing normal alveolar geometry and normal appearing alveolar septum (Fig. 4a). The same histopathological findings are seen after a dose of 1.25 mg−1kg−1day−1 (Fig. 4b). With a dose of 12.5 mg−1kg−1day,−1 mild thickening of the alveolar membrane and localized Para bronchiolar lipophagocytic changes were detected with both 12.5 mg−1kg−1day−1 and 125 mg−1kg−1day−1 doses indicating mild lung toxicity (Fig. 4c, d).
Sections from the control animals are showing normal hepatic architecture, hepatocytes, portal triad and central vein (Fig. 4e). The same histopathological findings are seen with 1.25 mg−1kg−1day−1 (Fig. 4f). After a dose of 12.5 mg−1kg−1day−1 mild hepatocytes cloudy swelling was observed (Fig. 4g). Sinusoidal congestion and mild lobular inflammation were also observed with a dosage of 125 mg−1kg−1day,−1 indicating mild liver toxicity (Fig. 4h).
Sections from the control animals are showing normal renal cortex with normal appearing glomerular tufts and tubules and normal renal papilla (Fig. 4i). After a dose of 1.25 mg−1kg−1day,−1 still the sections are showing normal renal cortex with normal appearing glomerular tufts and tubules and normal renal papilla (Fig. 4j). Cloudy swelling in renal cortical tubular epithelium is seen at 12.5 mg−1kg−1day−1 dose (Fig. 4k). Mild glomerular mesangial cell proliferation and arteriolar congestion are detected at 125 dose mg−1kg−1day−1 dose (Fig. 4l).
Sections from the control animals are showing normal splenic architecture with normal lymphoid follicles and sinuses (Fig. 4m). Normal histopathology findings are still seen after a dose of 1.25 mg−1kg−1day−1 (Fig. 4n). No pathological changes are seen with a dose of 12.5 mg−1kg−1day−1 (Fig. 4o). At a dose of 125 mg−1kg−1day,−1 mild follicular hyperplasia is seen indicating mild toxicity of the spleen (Fig. 4p). The reported histopathological changes may represent cellular compensatory changes to the injected nanorods and don’t necessary indicate a toxic effect.
We have also examined the histologic specimens of vital tissues (liver, kidney, spleen and lung) collected from mice sacrificed on day 60 using H & E staining, and they showed normal histology of liver, kidney, spleen and lung (Fig. 5.a–l).
The europium element was detected in diverse organs such as liver, kidney, spleen and lungs (Fig. 6). The particles were distributed in all organs, and the distribution pattern was shown in Fig. 6. The concentration of europium element in different organs was analyzed by inductively coupled plasma mass spectrometry (ICPMS). The bio-distribution of europium element (per gram of tissue) in different organs of mice for short-term (ST; 7 days) and long-term (LT; 60 days) treatment with different doses (1.25 mg−1kg−1day−1, 1.25 mg−1kg−1day−1, 1.25 mg−1kg−1day−1, and 125-L-T = 1.25 mg−1kg−1day−1, long-term) after intra-peritoneal injection for seven days are shown in Fig. 6. The accumulated europium concentration in liver, kidney, spleen and lungs was ~440, ~788, ~4390 and ~75 μg/g of tissue, respectively, for the treatment of 125 mg−1kg−1day−1 which is a very high dose. However, using the medium dose of EuIII(OH)3 nanorods (12.5 mgKg−1day−1) the concentration in liver, kidney, spleen and lungs was ~2, ~6, ~440 and ~6.2 μg/g of tissue, respectively. The distribution of europium in liver, kidney and lungs was almost negligible which is not damaging for liver, kidney, and lungs. The concentration of europium is higher in the spleen as compared to other organs at all doses of EuIII(OH)3 nanorods. These results support the reported literature (Nakamura et al., 1997; Palasz and Czekaj, 2000). Nakamura et al. reported that lanthanide ions are cleared from blood within one day, but they remain much longer in the organs. Long-term toxicity testing of EuIII(OH)3 nanorods for more than 60 days also reveals the similar pattern of bio-distribution.
In our study, EuIII(OH)3 nanorods were administered to mice through the intraperitoneal (IP) route. Thus, the majority of the nanorods would be taken up by the liver via the first-pass effects and then redistributed from the liver to the other organs. Our results show that EuIII(OH)3 nanorods are rapidly and widely redistributed in the body except in the case of the lungs. We studied tissues that are enriched with the reticuloendothelial system (RES) such as the liver, spleen, and lungs and non-RES organs such as kidney. The highest concentrations of EuIII(OH)3 nanorods were observed in the liver and spleen. Among the RES organs, EuIII(OH)3 nanorods were distributed in small amounts only in the lungs, thereby suggesting that the localization of the EuIII(OH)3 nanorods in the liver, lungs, and spleen was not consistent with the RES system (Kim et al., 2006). We have observed that high doses of EuIII(OH)3 nanorods (125 mg−1kg−1day−1) have no lethal toxicity; even with long-term toxicity studies, there were no deaths of mice using high doses of inorganic nanorods for more than 60 days (100 % survival). It is reported that hydrodynamic size (Svedberg et al., 2005) of nanoparticles (NPs) also affects NPs clearance from circulation (Moghimi, 1995a; Moghimi, 1995b; Moghimi and Hunter, 2001; Moghimi et al., 2001; Choi et al., 2007; Longmire et al., 2008; Zamboni, 2008). For instance, it has been reported that small NPs (< 20 nm) are excreted renally, (Banerjee et al., 2002; Choi et al., 2007) while medium sized NPs (30–150 nm) have accumulated in the bone marrow, (Moghimi, 1995a) heart, kidney, and stomach; (Banerjee et al., 2002) and large NPs (150–300 nm) have been found in the liver and spleen (Moghimi, 1995b). While these size ranges provide general clearance mechanisms, other physical parameters simultaneously affect NPs movement.
We have calculated the relative tissue distribution (i.e., how much of the dose was retrieved in the different tissues) and how much of the dose that is not accounted for. The persistence of europium in the body is an important parameter for determining a hazard. However, in this article we have only focused on the effect of nanorods in a time dependent (8–60 days) and dose dependent manner (1.25–125 mg−1Kg−1day−1) in animals. The clinical significance, biohazard, and long term persistence of europium in the body require more investigation in future studies.
The relative distribution pattern of the europium element in different vital organs is almost the same for the mice sacrificed on day eight as well as day 60. However, the amount of europium is less than in the latter case. We have calculated the amount of europium present in different tissues from the mice sacrificed on day eight (short-term study) and day 60 (long-term study), respectively. We have injected EuIII(OH)3 nanorods intraperitonially for seven days in each mouse (weight of each mice is ~25 g) at three doses such as 1.25 mg−1Kg−1day−1(163.8 μg), 12.5 mg−1Kg−1day−1(1638 μg), and 125 mg−1Kg−1day−1(16380 μg), respectively. We have observed that total 3.2 wt. % (52.7 μg) and 8.2 wt. % (1338.2 μg) of europium is retained in the vital organs (liver, kidney, spleen and lung) from each mouse treated with nanorods at 12.5 mg−1Kg−1day−1 and 125 mg−1Kg−1day−1 for the short-term toxicity study. Similarly, we have found that only 3.3 wt. % (539.5 μg) of europium is retained in vital organs (liver, kidney, spleen and lung) of each mouse treated with nanorods at 125 mg−1Kg−1day−150 μg for 7 day injection). These observations indicate that with increasing time, retention of europium is decreased over time from eight days to 60 days. The rest of the europium (which we can’t account for) is eliminated from the body maybe due to excretion (urine and feces) or accumulation in other parts of the body.
Our ultimate goal is to utilize the pro-angiogenic properties and non-toxic behavior of EuIII(OH)3 nanorods for future therapeutic treatment strategies of severe ischemic heart disease, peripheral ischemic disease, limb ischemic disease, etc. Our therapeutic dose of EuIII(OH)3 nanorods would be administered locally to the ischemic part of the disease at a microgram level which is at a far lower dose compared to the dose of our toxicity experiments (milligram level). As the therapeutic dose of EuIII(OH)3 nanorods is very low compared to the toxicity dose, we believe that these nanorods can be used safely for the treatment of several ischemic disease.
EuIII(OH)3 nanorods have been synthesized in our laboratory by microwave irradiation and characterized using several analytical tools. The as-synthesized materials are non-toxic to endothelial cells observed by apoptosis assay. Intraperitonial injection of EuIII(OH)3 nanorods at several doses in mice showed normal blood hematology and serum clinical chemistry except the slight elevation of liver enzymes. Histological examination of vital organs including liver, kidney, spleen, and lungs from each mouse, assayed on day eight or day 60 after injection of nanorods, showed none or only mild histological changes that indicates mild toxicity at highest dose of nanorods. Taken together, our results demonstrated that EuIII(OH)3 nanorods of 200–300-nm size caused no or mild toxicity under the experimental conditions of this study. The remarkable findings of pro-angiogenic properties and non-toxic behavior of EuIII(OH)3 nanorods suggests that these nanorods could be used for future therapeutic alternative treatment strategies for severe ischemic heart disease, peripheral ischemic disease, and limb ischemic disease.
The authors are also grateful to Prof. Rick A. Knurr of Department of Geology & Geophysics at University of Minnesota for ICPMS analysis and J. Charlesworth of the EM Core Facility at Mayo Clinic for the TEM analysis. We are also thankful to Mrs. Denise R Lecy and Colleen L. Allen for editorial assistance.
This work was partly supported by the National Institutes of Health (NIH) grant (HL70567 to D.M) and also partly supported by UOFM-MEDICA# 5P1, a grant from Minnesota Partnership for translational Nanotechnology in Cancer to P. M.
CONFLICT OF INTEREST STATEMENT
Mayo Foundation for Medical Education and Research has filed a patent (Patent Application No.# PCT/US2007/075926) entitled “RARE EARTH NANOPARTICLES” which lists Drs. Chittaranjan Patra, Priyabrata Mukherjee and Debabrata Mukhopadhyay as inventors. Dr. Patra, Dr. Mukhopadhyay, and Dr. Mukherjee disclosed that they and Mayo Clinic have a financial interest in the technology related to this research. That technology has been licensed to a privately held biotechnology company. Mayo Clinic holds equity in this company, and Mayo Clinic and Drs. Patra, Mukherjee and Mukhopadhyay have contractual rights to receive future royalties from the licensing of this technology.”