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不同接种程序对土壤中 ZnO 纳米颗粒分布和毒性的影响。

Effect of different spiking procedures on the distribution and toxicity of ZnO nanoparticles in soil.

机构信息

Department of Animal Ecology, Faculty of Earth and Life Sciences, VU University, De Boelelaan 1085, 1081 HV, Amsterdam, The Netherlands.

出版信息

Ecotoxicology. 2012 Oct;21(7):1797-804. doi: 10.1007/s10646-012-0914-3. Epub 2012 May 3.

Abstract

Due to the difficulty in dispersing some engineered nanomaterials in exposure media, realizing homogeneous distributions of nanoparticles (NP) in soil may pose major challenges. The present study investigated the distribution of zinc oxide (ZnO) NP (30 nm) and non-nano ZnO (200 nm) in natural soil using two different spiking procedures, i.e. as dry powder and as suspension in soil extract. Both spiking procedures showed a good recovery (>85 %) of zinc and based on total zinc concentrations no difference was found between the two spiking methods. Both spiking procedures resulted in a fairly homogeneous distribution of the ZnO particles in soil, as evidenced by the low variation in total zinc concentration between replicate samples (<12 % in most cases). Survival of Folsomia candida in soil spiked at concentrations up to 6,400 mg Zn kg(-1) d.w. was not affected for both compounds. Reproduction was reduced in a concentration-dependent manner with EC50 values of 3,159 and 2,914 mg Zn kg(-1) d.w. for 30 and 200 nm ZnO spiked as dry powder and 3,593 and 5,633 mg Zn kg(-1) d.w. introduced as suspension. Toxicity of ZnO at 30 and 200 nm did not differ. We conclude that the ZnO particle toxicity is not size related and that the spiking of the soil with ZnO as dry powder or as a suspension in soil extract does not affect its toxicity to F. candida.

摘要

由于一些工程纳米材料在暴露介质中难以分散,因此实现纳米颗粒(NP)在土壤中的均匀分布可能会带来重大挑战。本研究采用两种不同的添加程序,即作为干粉和土壤提取物中的悬浮液,研究了氧化锌(ZnO)NP(30nm)和非纳米 ZnO(200nm)在天然土壤中的分布。两种添加程序均显示锌的回收率良好(>85%),并且基于总锌浓度,两种添加方法之间没有发现差异。两种添加程序均导致 ZnO 颗粒在土壤中分布相当均匀,这可以从重复样品之间总锌浓度的低变化(大多数情况下<12%)得到证明。在高达 6400mg Zn kg(-1)d.w.的浓度下,两种化合物对 Folsomia candida 在土壤中的生存都没有影响。繁殖呈浓度依赖性降低,30nm 和 200nm ZnO 以干粉形式添加时的 EC50 值分别为 3159mg Zn kg(-1)d.w.和 2914mg Zn kg(-1)d.w.,以悬浮液形式添加时的 EC50 值分别为 3593mg Zn kg(-1)d.w.和 5633mg Zn kg(-1)d.w.。ZnO 的毒性与粒径无关。我们得出结论,ZnO 颗粒的毒性与粒径无关,并且将 ZnO 以干粉或土壤提取物中的悬浮液形式添加到土壤中不会影响其对 F. candida 的毒性。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/8b5d/3431463/09a9dd65a43f/10646_2012_914_Fig1_HTML.jpg

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