Sang Hee Lee

Repeated-dose toxicity and inflammatory responses in mice by oral administration of silver nanoparticles

Toxicity of nanoparticles depends on many factors including size, shape, chemical composition, surface area, surface charge, and others. In this study, we compared the toxicity of different sized-silver nanoparticles (AgNPs) which are being widely used in consumer products due to its unique antimicrobial activity. When mice were treated with AgNPs 1mg/kg for 14 days by oral administration, small-sized AgNPs (22nm, 42nm, and 71nm) were distributed to the organs including brain, lung, liver, kidney, and testis while large-sized AgNPs (323nm) were not detected in those tissues. The levels of TGF-β in serum were also significantly increased in the treated group of small-sized AgNPs but not in large-sized AgNPs. In addition, B cell distribution was increased in small-sized AgNPs but not in large-sized-AgNPs by the phenotype analysis. However, body weight or in the ratio of organ/body weight were not different between the control group and all the AgNPs-treated groups. The repeated-dose toxicity of AgNPs (42nm) was also investigated in mice by oral administration for 28 days. By the administration of AgNPs (0.25mg/kg, 0.50mg/kg, 1.00mg/kg), adverse impacts on liver and kidney were observed in a high dose-treated group (1.00mg/kg), when determined by blood chemistry and histipathological analysis. Cytokines including IL-1, IL-6, IL-4, IL-10, IL-12, and TGF-β were also increased in a dose-dependent manner by repeated oral administration. In addition, B cell distribution in lymphocyte and IgE production were increased. Based on these results, it is suggested that repeated oral administration of nano-sized AgNPs may cause organ toxicity and inflammatory responses in mice.

Bioavailability and toxicokinetics of citrate-coated silver nanoparticles in rats.

Bioavailability, tissue distribution, blood concentration, and excretion of citrate-coated silver nanoparticles (AgNPs; size, 7.9 ± 0.95 nm by TEM diameter) were investigated. Male SD rats were treated by a single oral or intravenous administration of either 1 or 10 mg/kg AgNPs. Silver concentration of blood was determined at 10 min, and at 1, 2, 4, 8, 24, 48, and 96 h after treatment. Silver in the liver, lungs, and kidneys was also measured at 24 and 96 h after treatment. Excretion of silver nanoparticles via feces and urine was determined at 24 h after treatment. After oral administration, most AgNPs were found in feces, and their blood concentration was very low. This suggests that absorption through the gastrointestinal tract was not good. However, a high level of silver in the blood was detected after tail vein injection. When rats were injected with 1 mg/kg AgNPs, the silver concentration of blood was significantly elevated at 10 min after injection; the level subsequently decreased. In the rats treated with 10 mg/kg AgNPs, the elevated level did not decrease, but was maintained during the experimental period. On the basis of the values of AUCoral/AUCiv, the bioavailability of orally administered AgNPs was 1.2% in the group treated with 1 mg/kg AgNPs and 4.2% in the group treated with 10 mg/kg AgNPs. AgNPs accumulated in the liver, lungs, and kidneys; the accumulated AgNPs were released into the blood stream. AgNP levels in the urine were extremely low compared to the levels in the feces. When rats were injected with AgNPs, these particles were also detected in feces at 24 h after treatment, which suggests bile secretion of AgNPs.

Acute inhalation toxicity of silver nanoparticles

The acute inhalation toxicity of silver nanoparticles was studied in Sprague-Dawley rats. Seven-week-old rats, weighing approximately 218 g (males) and 153 g (females), were divided into four groups (five rats in each group): fresh-air control, low-dose (0.94 × 10(6) particle/cm(3), 76 µg/m(3)), middle-dose (1.64 × 10(6) particle/ cm(3), 135 µg/m( 3)), and high-dose (3.08 × 10(6) particle/cm(3), 750 µg/m(3)). The animals were then exposed to silver nanoparticles (average diameter 18-20 nm) for 4 hours in a whole-body inhalation chamber. The experiment was conducted following Organization Economic Cooperation and Development (OECD) test guideline 403 with the application of good laboratory practice (GLP). In addition to mortality and clinical observations, the body weights, food consumption, and pulmonary function tests were recorded weekly. At the end of the study, the rats were subjected to a full necropsy, and the organ weights measured. The lung function was also measured twice per week after the initial 4-hour exposure. No significant body weight changes or clinical changes were found during the 2-week observation period. The lung function tests also indicated no significant difference between the fresh air control and the exposed groups. Thus, LC50 silver nanoparticles are suggested for higher than 3.1 × 10(6) particles/cm(3) (750 µg/m(3)).The acute inhalation toxicity of silver nanoparticles was studied in Sprague-Dawley rats. Seven-week-old rats, weighing approximately 218 g (males) and 153 g (females), were divided into four groups (five rats in each group): fresh-air control, low-dose (0.94 10 particle/cm, 76 mg/m), middle-dose (1.64 10 particle/ cm, 135 mg/m), and high-dose (3.08 10 particle/cm, 750 mg/m). The animals were then exposed to silver nanoparticles (average diameter 18 20 nm) for 4 hours in a whole-body inhalation chamber. The experiment was conducted following Organization Economic Cooperation and Development (OECD) test guideline 403 with the application of good laboratory practice (GLP). In addition to mortality and clinical observations, the body weights, food consumption, and pulmonary function tests were recorded weekly. At the end of the study, the rats were subjected to a full necropsy, and the organ weights measured. The lung function was also measured twice per week after the initial 4-hour exposure. No significant body weight changes or clinical changes were found during the 2-week observation period. The lung function tests also indicated no significant difference between the fresh air control and the exposed groups. Thus, LC50 silver nanoparticles are suggested for higher than 3.1 10 particles/cm (750 mg/m).

Combined repeated-dose toxicity study of silver nanoparticles with the reproduction/developmental toxicity screening test

Abstract Combined repeated-dose toxicity study of citrate-capped silver nanoparticles (7.9 ± 0.95 nm) with reproduction/developmental toxicity was investigated in rats orally treated with 62.5, 125 and 250 mg/kg, once a day for 42 days for males and up to 52 days for females. The test was performed based on the Organization for Economic Cooperation and Development test guideline 422 and Good Laboratory Practice principles. No death was observed in any of the groups. Alopecia, salivation and yellow discolouration of the lung were observed in a few rats but the symptoms were not dose-dependent. Haematology, serum biochemical investigation and histopathological analysis revealed no statistically significant differences between control group and the treated groups. Toxicity endpoints of reproduction/developmental screening test including mating, fertility, implantation, delivery and foetus were measured. There was no evidence of toxicity.

Peroxiredoxin II preserves cognitive function against age-linked hippocampal oxidative damage

Reactive oxygen species (ROS), routinely produced in biological reactions, contribute to both normal aging and age-related decline in cognitive function. However, little is known regarding the involvement of specific antioxidants in the underlying mechanism(s). Here, we examined if peroxiredoxin II (Prx II) scavenges intracellular ROS that cause age-dependent mitochondrial decay in hippocampal CA1 pyramidal neurons and subsequent impairment of learning and memory. Age-dependent mitochondrial ROS generation and long-term potentiation (LTP) decline were more prominent in hippocampal neurons in Prx II(-/-) than in wild-type mice. Additionally, Prx II(-/-) mice failed to activate synaptic plasticity-related cellular signaling pathways involving CREB, CaMKII, and ERK, or to maintain functional integrity of their mitochondria. Dietary vitamin E alleviated Prx II deficiency-related deficits, including mitochondrial decay and CREB signaling, resulting in restoration of the abrupt cognitive decline in aged Prx II(-/-) mice. These results suggest that Prx II help maintain hippocampal synaptic plasticity against age-related oxidative damage.

Oxidative stress in juvenile common carp (Cyprinus carpio) exposed to TiO 2 nanoparticles

Acute toxicity and oxidative stress caused by exposure of titanium dioxide nanoparticles (TiO2-NPs) in juvenile common carp (Cyprinus carpio) were investigated. TiO2-NPs solution was prepared using deionized water and dispersed by sonication. Juvenile carp were exposed to different concentrations (5, 10, 20, 40, and 80 mg/L) of TiO2-NPs. TiO2-NP characteristics (particle morphology, size distribution, and zetapotential) were analyzed using transmission electron microscopy (TEM) and dynamic light scattering (DLS). Different tissue samples (skin, liver, brain, and gill) of fish were dissected, and the biochemical responses (catalase [CAT] and glutathione S-transferase [GST] activities) were measured. The results showed that acute exposure to TiO2-NPs induced GST and CAT levels to vary in all observed organs. The effective concentration of TiO2-NPs was 20 mg/L in the liver and brain and 40 mg/L in the gill. Histopathological changes were as follows: (1) skin: hypertrophy and increased number of mucous cells and thickening of the epidermal layer; (2) gill: hypertrophy of chloride cells, degeneration of mucous cells, and increased acidification of mucous cells; and (3) liver: hyperplasia and cytoplasm vacuolation of hepatic cells. No lethal effects were observed during the acute test. Our results show that there is a potential risk of TiO2-NP exposure to aquatic organisms in the environment.

Combined repeated dose and reproductive/developmental toxicities of copper monochloride in rats.

This study investigated the combined repeated dose and reproductive/developmental toxicity of copper monochloride in rats. The test substance was administered once daily by gavage at 0, 1.3, 5, 20, or 80 mg/kg/day. Male rats were dosed for a total of 30 days beginning 14 days before mating. Female rats were dosed from 2 weeks before mating to day 3 of lactation throughout the mating and gestation period. At 80 mg/kg/day, deaths were observed in 3 out of 12 females. There was a dose‐dependent increase in the incidence of clinical signs and a reduction in the food consumption. Hematological and serum biochemical investigations revealed a decrease in the red blood cell, hemoglobin, hematocrit, mean corpuscular volume, mean corpuscular hemoglobin (MCH), and serum total protein levels and an increase in the white blood cell and platelets in males, and a decrease in the MCH and an increase in the platelets in females. Histopathological examination showed an increased incidence of squamous cell hyperplasia of the stomach in both genders as well as increased hematopoiesis of the femur in males. There was an increase in the number of icteric and runt pups at birth. At 20 mg/kg/day, there was an increase in the incidence of clinical signs and squamous cell hyperplasia of the stomach in both genders. At 5 mg/kg/day, an increase in the incidence of squamous cell hyperplasia of the stomach was observed in females. There were no adverse effects in the lowest group in both genders. Based on these findings, the no‐observed‐adverse‐effect levels of copper monochloride were concluded to be 5 mg/kg/day in male rats and 1.3 mg/kg/day in female rats for general toxicity and 20 mg/kg/day for reproductive/developmental toxicity.