Despite increasing application of silver nanoparticles (NPs) in industry and consumer products, there is still little known about their potential toxicity, particularly to organisms in aquatic environments. To investigate the fate and effects of silver NPs in fish, rainbow trout (Oncorhynchus mykiss) were exposed via the water to commercial silver particles of three nominal sizes: 10 nm (N(10)), 35 nm (N(35)), and 600-1600 nm (N(Bulk)), and to silver nitrate for 10 days. Uptake into the gills, liver, and kidneys was quantified by inductively coupled plasma-optical emission spectrometry, and levels of lipid peroxidation in gills, liver, and blood were determined by measurements of thiobarbituric acid reactive substances. Expression of a suite of genes, namely cyp1a2, cyp3a45, hsp70a, gpx, and g6pd, known to be involved in a range of toxicological response to xenobiotics was analyzed in the gills and liver using real-time PCR. Uptake of silver particles from the water into the tissues of exposed fish was low but nevertheless occurred for current estimated environmental exposures. Of the silver particles tested, N(10) were found to be the most highly concentrated within gill tissues and N(10) and N(Bulk) were the most highly concentrated in liver. There were no effects on lipid peroxidation in any of the tissues analyzed for any of the silver particles tested, and this is likely due to the low uptake rates. However, exposure to N(10) particles was found to induce expression of cyp1a2 in the gills, suggesting a possible increase in oxidative metabolism in this tissue.
Effects on the liver C3A cell line treated with a panel of engineered nanomaterials (NMs) consisting of two zinc oxide particles (ZnO; coated 100 nm and uncoated 130 nm), two multi-walled carbon nanotubes (MWCNTs), one silver (Ag < 20 nm), one 7 nm anatase, two rutile TiO2 nanoparticles (10 and 94 nm) and two derivatives with positive and negative covalent functionalisation of the 10 nm rutile were evaluated. The silver particles elicited the greatest level of cytotoxicity (24 h LC50 - 2 µg/cm(2)). The silver was followed by the uncoated ZnO (24 h LC50 - 7.5 µg/cm(2)) and coated ZnO (24 h LC50 - 15 µg/cm(2)) particles with respect to cytotoxicity. The ZnO NMs were found to be about 50-60% soluble which could account for their toxicity. By contrast, the Ag was <1% soluble. The LC50 was not attained in the presence of any of the other engineered NMs (up to 80 µg/cm(2)). All NMs significantly increased IL-8 production. Meanwhile, no significant change in TNF-α, IL-6 or CRP was detected. Urea and albumin production were measured as indicators of hepatic function. These markers were only altered by the coated and uncoated ZnO, which significantly decreased albumin production.
With the increasing use and incorporation of nanoparticles (NPs) into consumer products, screening for potential toxicity is necessary to ensure customer safety. NPs have been shown to translocate to the bloodstream following inhalation and ingestion, and such studies demonstrate that the liver is an important organ for accumulation. Silver (Ag) NPs are highly relevant for human exposure due to their use in food contact materials, dietary supplements, and antibacterial wound treatments. Due to the large number of different NPs already used in various products and being developed for new applications, it is essential that relevant, quick, and cheap methods of in vitro risk assessment suitable for these new materials are established. Therefore, this study used a simple hepatocytes model combined with an in vivo injection model to simulate the passage of a small amount of NPs into the bloodstream following exposure, e.g., via ingestion or inhalation, and examined the potential of Ag NPs of 20 nm diameter to cause toxicity, inflammation, and oxidative stress in the liver following in vivo exposures of female Wistar rats via iv injection to 50 μg of NPs and in vitro exposures using the human hepatocyte cell line C3A. We found that Ag NPs were highly cytotoxic to hepatocytes (LC(50) lactate dehydrogenase: 2.5 μg/cm(2)) and affected hepatocyte homeostasis by reducing albumin release. At sublethal concentrations with normal cell or tissue morphology, Ag NPs were detected in cytoplasm and nuclei of hepatocytes. We observed similar effects of Ag NPs on inflammatory mediator expression in vitro and in vivo with increase of interleukin-8 (IL-8)/macrophage inflammatory protein 2, IL-1RI, and tumor necrosis factor-α expression in both models and increased IL-8 protein release in vitro. This article presents evidence of the potential toxicity and inflammogenic potential of Ag NPs in the liver following ingestion. In addition, the similarities between in vitro and in vivo responses are striking and encouraging for future reduction, refinement, and replacement of animal studies by the use of hepatocyte cell lines in particle risk assessment.
An increasing number and quantity of manufactured nanoparticles are entering the environment as the diversity of their applications increases, and this will lead to the exposure of both humans and wildlife. However, little is known regarding their potential health effects. We compared the potential biological effects of silver (Ag; nominally 35 and 600-1,600 nm) and cerium dioxide (CeO(2;) nominally <25 nm and 1-5 µm) particles in a range of cell (human hepatocyte and intestinal and fish hepatocyte) and animal (Daphnia magna, Cyprinus carpio) models to assess possible commonalities in toxicity across taxa. A variety of analytical techniques were employed to characterize the particles and investigate their biological uptake. Silver particles were more toxic than CeO(2) in all test systems, and an equivalent mass dose of Ag nanoparticles was more toxic than larger micro-sized material. Cellular uptake of all materials tested was shown in C3A hepatocytes and Caco-2 intestinal cells, and for Ag, into the intestine, liver, gallbladder, and gills of carp exposed via the water. The commonalities in toxicity of these particle types across diverse biological systems suggest that cross-species extrapolations may be possible for metal nanoparticle test development in the future. Our findings also suggest transport of particles through the gastrointestinal barrier, which is likely to be an important uptake route when assessing particle risk.
BackgroundFollowing exposure via inhalation, intratracheal instillation or ingestion some nanomaterials (NM) have been shown to translocate to the liver. Since oxidative stress has been implicated as a possible mechanism for NM toxicity this study aimed to investigate the effects of various materials (five titanium dioxide (TiO2), two zinc oxide (ZnO), two multi-walled carbon nanotubes (MWCNT) and one silver (Ag) NM) on oxidative responses of C3A cell line as a model for potential detrimental properties of nanomaterials on the liver.ResultsWe noted a dose dependant decrease in the cellular glutathione content following exposure of the C3A cells to Ag, the ZnO and the MWCNTs. Intracellular ROS levels were also measured and shown to increase significantly following exposure of the C3A to the low toxicity NMs (MWCNT and TiO2). The antioxidant Trolox in part prevented the detrimental effect of NMs on cell viability, and decreased the NM induced IL8 production after exposure to all but the Ag particulate. Following 4 hr exposure of the C3A cells to sub-lethal levels of the NMs, the largest amount of DNA damage was induced by two of the TiO2 samples (7 nm and the positively charged 10 nm particles).ConclusionsAll ten NMs exhibited effects on the hepatocyte cell line that were at least in part ROS/oxidative stress mediated. These effects included mild genotoxicity and IL8 production for all NM except the Ag possibly due to its highly cytotoxic nature.
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