4.5 Article

Isotopically modified silver nanoparticles to assess nanosilver bioavailability and toxicity at environmentally relevant exposures

期刊

ENVIRONMENTAL CHEMISTRY
卷 11, 期 3, 页码 247-256

出版社

CSIRO PUBLISHING
DOI: 10.1071/EN13141

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资金

  1. US-EPA [RD-834557501-0]
  2. UK-NERC [NE/F005008/1]
  3. Toxic Substance Hydrology Program of the US Geological Survey
  4. Facility for Environmental Nanoscience Analysis and Characterisation (FENAC)
  5. NERC [NE/H013199/1, FENAC010001] Funding Source: UKRI
  6. Natural Environment Research Council [FENAC010001, NE/H013199/1] Funding Source: researchfish

向作者/读者索取更多资源

A major challenge in understanding the environmental implications of nanotechnology lies in studying nanoparticle uptake in organisms at environmentally realistic exposure concentrations. Typically, high exposure concentrations are needed to trigger measurable effects and to detect accumulation above background. But application of tracer techniques can overcome these limitations. Here we synthesised, for the first time, citrate-coated Ag nanoparticles using Ag that was 99.7% Ag-109. In addition to conducting reactivity and dissolution studies, we assessed the bioavailability and toxicity of these isotopically modified Ag nanoparticles (Ag-109 NPs) to a freshwater snail under conditions typical of nature. Weshowed that accumulation of Ag-109 from Ag-109 NPs is detectable in the tissues of Lymnaea stagnalis after 24-h exposure to aqueous concentrations as low as 6 ng L-1 as well as after 3 h of dietary exposure to concentrations as low as 0.07 mu g g(-1). Silver uptake from unlabelled Ag NPs would not have been detected under similar exposure conditions. Uptake rates of Ag-109 from Ag-109 NPs mixed with food or dispersed in water were largely linear over a wide range of concentrations. Particle dissolution was most important at low waterborne concentrations. We estimated that 70% of the bioaccumulated Ag-109 concentration in L. stagnalis at exposures,0.1 mg L-1 originated from the newly solubilised Ag. Above this concentration, we predicted that 80% of the bioaccumulated Ag-109 concentration originated from the Ag-109 NPs. It was not clear if agglomeration had a major influence on uptake rates.

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