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基于铜和银的纳米粒子的初始形态对其在淡水湿地中中营养模型中长期归宿和植物可利用性的影响。

Effect of Initial Speciation of Copper- and Silver-Based Nanoparticles on Their Long-Term Fate and Phytoavailability in Freshwater Wetland Mesocosms.

机构信息

Center for the Environmental Implications of NanoTechnology (CEINT) and ‡Civil & Environmental Engineering, Carnegie Mellon University , Pittsburgh, Pennsylvania 15213, United States.

出版信息

Environ Sci Technol. 2017 Nov 7;51(21):12114-12122. doi: 10.1021/acs.est.7b02972. Epub 2017 Oct 23.

Abstract

Ag- and CuO-engineered nanomaterials (ENMs) or their sulfidized forms are introduced into freshwater wetlands through wastewater effluent and agricultural runoff. Knowledge about the rates of transformations of these ENMs in realistic environments and the impact of the form of the incoming ENM (i.e., sulfidized or pristine) on bioavailability and fate is limited. Here, five freshwater wetland mesocosms were exposed to 3 g of total metal as CuO, CuS, Ag, or AgS ENMs or soluble CuNO added weekly for 1 month. Total metal and metal speciation was measured in sediment and plant samples collected 1, 3, 6, and 9 months after addition. The form of the added ENM did not affect the metal distribution, and ENMs distributed similarly to added ionic Cu or Ag. For the dosing condition used, ∼50% of the added Ag or Cu metal mass was found in Egeria densa plant tissue, with the remainder primarily in the surficial sediment. Ag and CuO ENMs transformed quickly in sediment, with no evidence of CuO and only ∼4% of silver present as Ag ENM 1 week after the last ENM addition. In contrast to sediment, Ag and CuO ENMs were persistent in E. densa tissues for up to 9 and 6 months, respectively. The persistence of ENMs in E. densa suggests that chronic exposures, or food web transfers, for both the transformed and the initially added ENMs are possible.

摘要

Ag 和 CuO 工程纳米材料(ENMs)或其硫化形式通过废水和农业径流被引入淡水湿地。关于这些 ENMs 在实际环境中的转化速率以及进入 ENM 的形式(即硫化或原始)对生物利用度和归宿的影响的知识是有限的。在这里,五个淡水湿地中观模型暴露于 3 g 总金属作为 CuO、CuS、Ag 或 AgS ENMs 或可溶性 CuNO,每周添加一次,持续 1 个月。在添加后 1、3、6 和 9 个月收集沉积物和植物样品时,测量了总金属和金属形态。添加的 ENM 的形式不影响金属分布,并且 ENMs 与添加的离子 Cu 或 Ag 分布相似。对于使用的剂量条件,添加的 Ag 或 Cu 金属质量的约 50%存在于水蕴草植物组织中,其余主要存在于表层沉积物中。Ag 和 CuO ENMs 在沉积物中迅速转化,在最后一次添加 ENM 1 周后,没有发现 CuO,只有约 4%的银以 Ag ENM 的形式存在。与沉积物相比,Ag 和 CuO ENMs 在水蕴草组织中分别持续了长达 9 个月和 6 个月。ENMs 在水蕴草中的持久性表明,对于转化的和最初添加的 ENMs,都可能存在慢性暴露或食物网转移。

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