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Assessing the Impacts of Silver Nanoparticles on the Growth, Diversity, and Function of Wastewater Bacteria.

机译:评估银纳米颗粒对废水细菌的生长,多样性和功能的影响。

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The objectives of this dissertation were to: 1) characterize the effect of several different silver nanoparticles (AgNPs) on the ammonia oxidizing bacterium (AOB) Nitrosomonas europaea and investigate possible mechanisms for toxicity, 2) test the effects of consumer product AgNPs on a wide range of heterotrophic bacteria, 3) evaluate the effects of AgNPs on bench scale wastewater sequencing batch reactors, and lastly 4) assess the impacts on microbial communities that are applied with AgNP spiked wastewater biosolids.;First, Nitrosomonas europaea was selected because wastewater nitrifying microorganisms carry out the first step in nitrification and are known to be sensitive to a wide range of toxicants [4].The antimicrobial effects of AgNPs on the AOB N. europaea were measured by comparing nitrite production rates in a dose response assay and analyzing cell viability using the LIVE/DEADRTM fluorescent staining assay. AgNP toxicity to N. europaea appeared to be largely nanoparticle coating dependent. While PVP coated AgNPs have shown reductions up to 15% in nitrite production at 20 ppm, other AgNPs such as gum arabic (GA) coated showed the same level of inhibition at concentrations of 2 ppm. The first mechanism of inhibition appears to be a post-transcriptional interference of AMO/HAO by either dissolved Ag or ROS, in treatments where membranes are not completely disrupted but nitrite production decreased (2 ppm GA AgNP and 2 ppm PVP AgNP treatments). The disruption of nitrification is dependent on AgNP characteristics, such as zeta potential and coating, which will dictate how fast the AgNP will release Ag+ and ROS production. Finally, total membrane loss and release of internal cellular matter occur.;In order to test the effects of AgNP products available to consumers, simple bacterial toxicity tests were carried out on well-studied heterotrophic bacteria. A model gram-positive and gram-negative bacterium (B. subtilis and E. coli, respectively) was selected to assess any differences in sensitivity that may occur with the exposure to AgNPs. A third model gram-negative bacterium (P. aeruginosa) was chosen for its biofilm forming capabilities. In addition to testing pure nanoparticles, three silver supplements meant for ingestion, were randomly chosen to test with these three bacteria. Growth curve assays and LIVE/DEAD staining indicate that the consumer product AgNPs had the most significant inhibition on growth rates, but not membrane integrity. Overall, P. aeruginosa was most negatively affected by all AgNPs with nearly 100% growth inhibition for all 2 ppm AgNP treatments. TEM imaging also confirmed cell wall separation in P. aeruginosa and internal density differences for E. coli. The effects on B. subtilis, a gram-positive bacterium, were not as severe but toxicity was observed for several AgNPs at concentrations greater than 2 ppm. Citrate AgNPs appeared to have the most impact on membrane integrity, while other mechanisms such as internal thiol binding might have been at work for other AgNPs.;The effects of varying concentrations of pure AgNPs on complex microbial wastewater reactors are currently being tested. Eight bench-scale sequencing batch reactors were set up to follow the typical "fill, react, settle, decant, idle" method with an 8 hour hydraulic retention time and constant aeration. Reactors were fed synthetic wastewater and treatment efficiency is measured by monitoring effluent concentrations of COD, NH4+, and NO3-. The reactors were seeded with 500 mL of activated sludge from a local wastewater treatment plant. After reaching steady state, the reactors were spiked with 0.2 ppm gum arabic and citrate coated AgNPs. Treatment efficiency was monitored and results showed significant spikes and ammonia and COD immediately following the first spike, but the microbial community appeared to adapt for future AgNP spikes. Microbial community analysis (terminal restriction fragment length polymorphism) showed confirmed this hypothesis. (Abstract shortened by UMI.).
机译:本文的目的是:1)表征几种不同的银纳米颗粒(AgNPs)对氨氧化细菌(Nitrosomonas europaea)的影响,并研究可能的毒性机理; 2)测试消费类产品AgNPs在广泛的环境中的作用。 3)评估AgNPs对台式规模废水定序批处理反应器的影响,最后4)评估掺有AgNP的废水生物固体对微生物群落的影响。首先,选择Nitrosomonas europaea是因为废水硝化微生物进行硝化的第一步,已知对多种毒物敏感[4]。通过在剂量反应分析中比较亚硝酸盐的产生速率并分析细胞活力,可测量AgNP对欧洲AOB猪的抗菌作用。使用LIVE / DEADRTM荧光染色测定法。 AgNP对欧洲猪笼草的毒性似乎很大程度上取决于纳米颗粒涂层的依赖性。尽管PVP涂层的AgNP在20 ppm时显示出最多可减少15%的亚硝酸盐生成,但是其他AgNP(例如阿拉伯胶(GA)涂层)在2 ppm的浓度下显示出相同的抑制水平。抑制的第一个机制似乎是溶解的Ag或ROS对AMO / HAO的转录后干扰,在膜未完全破坏但亚硝酸盐生成减少的处理中(2 ppm GA AgNP和2 ppm PVP AgNP处理)。硝化作用的中断取决于AgNP特性,例如Zeta电位和涂层,这将决定AgNP释放Ag +和ROS的释放速度。最后,发生了总的膜损失和内部细胞物质的释放。;为了测试可用于消费者的AgNP产品的效果,对经过充分研究的异养细菌进行了简单的细菌毒性测试。选择模型革兰氏阳性和革兰氏阴性细菌(分别为枯草芽孢杆菌和大肠杆菌)以评估暴露于AgNP时可能出现的敏感性差异。选择了第三种革兰氏阴性细菌(铜绿假单胞菌),因为它具有生物膜形成能力。除了测试纯纳米颗粒外,还随机选择了三种用于摄取的银补充剂来测试这三种细菌。生长曲线分析和LIVE / DEAD染色表明,消费品AgNPs对生长速率的抑制作用最大,但对膜的完整性没有抑制作用。总体而言,铜绿假单胞菌受所有AgNP的负面影响最大,所有2 ppm AgNP处理的生长抑制率均接近100%。 TEM成像还证实了铜绿假单胞菌的细胞壁分离和大肠杆菌的内部密度差异。对革兰氏阳性细菌枯草芽孢杆菌的影响不那么严重,但是在浓度大于2 ppm的几种AgNP中观察到了毒性。柠檬酸盐AgNP对膜的完整性影响最大,而其他机制(例如内部硫醇结合)可能对其他AgNP起作用。;目前正在测试不同浓度的纯AgNP对复杂微生物废水反应器的影响。设置了八个台式规模的间歇反应器,以遵循典型的“填充,反应,沉降,倾析,空转”方法,液压停留时间为8小时,恒定通气。向反应器中注入合成废水,并通过监测COD,NH4 +和NO3-的废水浓度来测量处理效率。向反应堆中注入来自当地废水处理厂的500 mL活性污泥。达到稳态后,向反应器中加入0.2 ppm阿拉伯胶和柠檬酸盐包覆的AgNP。监测治疗效率,结果显示在首次加标后立即出现明显的加标以及氨和COD,但微生物群落似乎适应了未来的AgNP加标。微生物群落分析(末端限制性片段长度多态性)表明了这一假设。 (摘要由UMI缩短。)。

著录项

  • 作者

    Arnaout, Christina Lee.;

  • 作者单位

    Duke University.;

  • 授予单位 Duke University.;
  • 学科 Engineering Environmental.;Nanotechnology.
  • 学位 Ph.D.
  • 年度 2012
  • 页码 156 p.
  • 总页数 156
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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