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淡水生物膜形成过程(从定植到成熟)对锐钛矿和金红石 TiO2 纳米颗粒的响应:纳米颗粒老化和转化的影响。

Responses of freshwater biofilm formation processes (from colonization to maturity) to anatase and rutile TiO nanoparticles: Effects of nanoparticles aging and transformation.

机构信息

Key Laboratory of Integrated Regulation and Resource Development on Shallow Lakes, Ministry of Education, Hohai University, Nanjing, 210098, PR China; College of Environment, Hohai University, Nanjing, 210098, PR China.

Key Laboratory of Integrated Regulation and Resource Development on Shallow Lakes, Ministry of Education, Hohai University, Nanjing, 210098, PR China; College of Environment, Hohai University, Nanjing, 210098, PR China.

出版信息

Water Res. 2020 Sep 1;182:115953. doi: 10.1016/j.watres.2020.115953. Epub 2020 Jun 9.

Abstract

Most of the current studies on the toxicology of pristine nanoparticles (NPs) are environmentally irrelevant, because their ''aging'' process accompanied by the physicochemical transformation is inevitable in the environment. Considering aging phenomenon will gain a better understanding of the toxicity and fate of NPs in the environment. Here, we focused on the physicochemical transformation of anatase-NPs (TiO-A) and rutile-NPs (TiO-R) after 90 days of aging and investigated the responses of freshwater biofilm formation to the stress changes of naturally aged TiO-NPs (aTiO-NPs). We found that after aging, the TiO-NPs underwent sophisticated physicochemical transformations in the original morphology and microstructure owing to organic and crystal salts inclusions, such as energy band changes and the formation of Ti on the NPs surfaces. These comprehensive transformations increased the stability of NPs in the exposed suspension. However, the physicochemical transformations were crystal-forms-dependent, and aging did not change the crystal structure and crystallinity. Interestingly, compared to pristine NPs, aTiO-NPs showed much lower cytotoxicity and had the weaker ability to promote or inhibit the biofilm formation (p < 0.05) owing to the passivation of photoactivity caused by the comprehensive effect of the inclusions, especially for aTiO-A. Regardless of aging or not of crystal forms, responses of biofilm formation were exposure-concentration-dependent, namely low concentration promotion (0.1 mg/L) and high concentration inhibition (10 mg/L), e.g., role transition of the pioneers (algae or bacteria) in initial colonization, extracellular polymeric substances (EPS) secretion and compositions of development stages with polysaccharide (PS)-rich and protein (PRO)-rich stages, and biomass and cell activity at different depths of mature biofilms. The reactive oxygen species (ROS) induced by TiO-NPs showed typical hormesis. The changing trends of the autoinducers (c-di-GMP and quorum sensing signals including AHL and AI-2) were highly consistent with the growth stages of biofilms and were stimulated or suppressed by TiO-NPs. The NPs crystal-dependently changed the microorganism community structures, while the UPGMA clustering of bacteria was based on the growth stages of the biofilms. The toxic mechanisms revealed that photoactivity and nanoscale retention of particles are the main reasons for the differences in the ecological stress capacity of four kinds of TiO-NPs. Aging reduced characteristic differences of two pristine NPs and even reversed their relative stresses levels (p > 0.05). However, the toxicity of high-concentration aTiO-NPs (10 mg/L) remained serious in a water environment. This study provides a better understanding for the water environmental risks evaluation and policy control of nanoparticles, that is, the effect of time aging has to be considered.

摘要

目前大多数关于原始纳米颗粒(NPs)毒理学的研究都与环境无关,因为它们在环境中不可避免地会经历“老化”过程,伴随着物理化学的转变。考虑到老化现象,我们将能更好地理解 NPs 在环境中的毒性和归宿。在这里,我们重点研究了锐钛矿型 NPs(TiO-A)和金红石型 NPs(TiO-R)在 90 天老化后的物理化学转变,并调查了天然老化的 TiO-NPs(aTiO-NPs)对淡水生物膜形成的应激变化的响应。我们发现,老化后,由于有机和晶体盐的包含物,如能带变化和 NPs 表面上 Ti 的形成,TiO-NPs 在原始形态和微观结构上经历了复杂的物理化学转变。这些综合转变增加了 NPs 在暴露悬浮液中的稳定性。然而,物理化学转变取决于晶体形态,老化并没有改变晶体结构和结晶度。有趣的是,与原始 NPs 相比,由于包含物的综合影响导致光活性钝化,aTiO-NPs 表现出较低的细胞毒性和较弱的促进或抑制生物膜形成的能力(p<0.05),尤其是对于 aTiO-A。无论是否老化,生物膜形成的响应都与暴露浓度有关,即低浓度促进(0.1mg/L)和高浓度抑制(10mg/L),例如,在初始定植时先驱生物(藻类或细菌)的作用转变、细胞外聚合物物质(EPS)的分泌以及多糖(PS)丰富和蛋白质(PRO)丰富阶段的发展阶段的组成,以及成熟生物膜不同深度处的生物量和细胞活性。TiO-NPs 诱导的活性氧(ROS)表现出典型的激素作用。自诱导物(c-di-GMP 和群体感应信号,包括 AHL 和 AI-2)的变化趋势与生物膜的生长阶段高度一致,并受到 TiO-NPs 的刺激或抑制。NPs 晶体依赖性地改变了微生物群落结构,而细菌的 UPGMA 聚类则基于生物膜的生长阶段。毒性机制表明,光活性和颗粒的纳米级保留是四种 TiO-NPs 生态应激能力差异的主要原因。老化降低了两种原始 NPs 的特征差异,甚至逆转了它们的相对应激水平(p>0.05)。然而,高浓度 aTiO-NPs(10mg/L)在水环境中的毒性仍然很严重。本研究为纳米颗粒的水环境风险评估和政策控制提供了更好的理解,即必须考虑时间老化的影响。

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