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Impact of water composition on association of Ag and CeO2 nanoparticles with aquatic macrophyte Elodea canadensis

机译:水分组成对Ag和CeO2纳米粒子与水生植物加拿大伊乐藻结合的影响

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In this study, the potential association of (citrate-stabilized) Ag (14.1 +/- 1.0 nm) and CeO2 (6.7 +/- 1.2 nm) engineered nanoparticles (ENPs), or their ionic counterparts, with the submerged aquatic plant Elodea canadensis, was examined and, in particular, parameters affecting the distribution of the nanoparticles (or metal ions) between plant biomass and the water phase were assessed using five distinct aqueous matrices (i.e. tap water, 10 % Hoagland's solution and three natural surface water samples). Individual plants were exposed to varying concentrations of Ag and CeO2 ENPs or Ag+ and Ce3+ ions during 72-h-lasting batch experiments. A dose-dependent increase of silver or cerium in plant biomass was observed for both the nanoparticles and the ions, whereby exposure to the latter systematically resulted in significantly higher biomass concentrations. Furthermore, the apparent plant uptake of CeO2 ENPs appeared to be higher than that for Ag ENPs when comparing similar exposure concentrations. These findings suggest that association with E. canadensis might be affected by particle characteristics such as size, composition, surface charge or surface coating. Moreover, the stability of the ENPs or ions in suspension/solution may be another important aspect affecting plant exposure and uptake. The association of the nanoparticles or ions with E. canadensis was affected by the physicochemical characteristics of the water sample. The silver biomass concentration was found to correlate significantly with the electrical conductivity (EC), dry residue (DR) and Cl-, K, Na and Mg content in the case of Ag ENPs or with the EC, inorganic carbon (IC) and Cl-, NO3 (-), Na and Mg content in the case of Ag+ ions, whereas significant relationships between the cerium biomass concentration and the EC, DR, IC and Ca content or the pH, EC, DR, IC and Cl-, Ca and Mg content were obtained for CeO2 ENPs or Ce3+ ions, respectively. Results also indicated that the Ag ENPs and Ag+ ions might potentially be toxic towards E. canadensis whereas no evidence of phytotoxicity was noted in the case of CeO2 ENPs or Ce3+ ions.
机译:在这项研究中,(柠檬酸盐稳定的)Ag(14.1 +/- 1.0 nm)和CeO2(6.7 +/- 1.2 nm)工程纳米颗粒(ENPs)或它们的离子对应物与淹没的水生加拿大伊乐藻的潜在关联进行了检查,尤其是使用五种不同的水性基质(即自来水,10%的霍格兰溶液和三种天然地表水样品)评估了影响植物生物质和水相之间纳米颗粒(或金属离子)分布的参数。 。在持续72小时的分批实验中,单个植物暴露于不同浓度的Ag和CeO2 ENP或Ag +和Ce3 +离子。对于纳米颗粒和离子,都观察到了植物生物量中银或铈的剂量依赖性增加,因此,系统地暴露于后者会导致明显更高的生物量浓度。此外,当比较相似的暴露浓度时,CeO2 ENPs的表观植物摄取似乎高于Ag ENPs。这些发现表明,与加拿大大肠埃希菌的结合可能受到颗粒特征如大小,组成,表面电荷或表面涂层的影响。此外,悬浮液/溶液中ENP或离子的稳定性可能是影响植物暴露和吸收的另一个重要方面。纳米粒子或离子与加拿大大肠埃希菌的缔合受水样的理化特性影响。发现银生物质浓度与Ag ENPs的电导率(EC),干渣(DR)和Cl-,K,Na和Mg含量显着相关,或者与EC,无机碳(IC)和Cl显着相关-,NO3(-),Na和Mg含量(对于Ag +离子而言),而铈生物量浓度与EC,DR,IC和Ca含量或pH,EC,DR,IC和Cl-,Ca含量之间存在显着关系分别获得了CeO2 ENPs或Ce3 +离子的Mg和Mg含量。结果还表明,Ag ENP和Ag +离子可能对加拿大大肠埃希菌有毒,而对于CeO2 ENPs或Ce3 +离子则没有发现植物毒性的证据。

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