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The investigation of microbial denitrification processes for the removal of nitrate from water using bio-electrochemical methods and carbon nano-materials

机译:利用生物电化学方法和碳纳米材料研究微生物反硝化工艺去除水中硝酸盐的方法

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摘要

With ever increasing regulation of the quality of drinking water and wastewater treatment, there is a need to develop methods to remove nitrogenous compounds from water. These processes are mediated by a variety of micro-organisms that can oxidise ammonia to nitrate, and then reduced to gaseous nitrogen by another set of organisms. This two stage process involves the relatively slow oxidation of ammonia to nitrate followed a relatively fast reduction of nitrate to nitrogen. Nitrate reduction normally requires anaerobic environments and the addition of organic matter to provide reducing power (electrons) for nitrate reduction. In practical situations the nitrate reduction can be problematic in those precise quantities of organic matter to ensure that the process occurs while not leaving residual organic matter. The aim of this study was to investigate microbial denitrification using electrochemical sources to replace organic matter as a redactant. The work also involved developing a system that could be optimised for nitrate removal in applied situations such as water processing in fish farming or drinking water, where high nitrate levels represent a potential health problem. Consequently, the study examined a range of developments for the removal of nitrate from water based on the development of electrochemical biotransformation systems for nitrate removal. This also offers considerable scope for the potential application of these systems in broader bio-nanotechnology based processes (particularly in bioremediation). The first stage of the study was to investigate the complex interactions between medium parameters and their effects on the bacterial growth rates. The results proved that acetate is a good carbon source for bacterial growth, and therefore it was used as an organic substrate for the biological process. High nitrate removal rate of almost 87% was successfully achieved by using a microbial fuel cell (MFC) enriched with soil inocula with the cathodes cells fed with nitrate and the anode fed with acetate. The maximum power density obtained was 1.26 mW/m2 at a current density of 10.23 mA/m2. The effects of acetate, nitrate and external resistance on current generation and denitrification activity were investigated, and the results demonstrated that nitrate removal was greatly dependent on the magnitude of current production within the MFC. Increase of acetate (anode) and nitrate (cathode) concentrations improved the process, while increasing external resistance reduced the activity. Furthermore, for a clear understanding of the nitrate reduction process, the analysis of the associated bacteria was performed through biochemical tests and examination of morphological characteristics. A diversity of nitrate reducing bacteria was observed; however a few were able to deliver complete denitrification. Pure cultures in MFC were examined and the voltage output achieved was about 36% of that obtained by mixed cultures. The nitrate removal gained was 56.2%, and this is almost 31% lower than that obtained by the mixed bacterial experiment. In an attempt to improve the MFC, modifications to the electrochemical properties of the electrode were investigated through the use of a cyclic voltammetry using carbon nanomaterials to coat the graphite felts electrodes. Among all the nanomaterials used in this study, graphitised carbon nanofibres (GCNFs) was selected for further investigation as it offered the best electrochemical performance and was thought to provide the largest active surface area. The performance of the MFC system coupled with the GCNFs modified electrodes was evaluated and significant improvements were observed. The highest voltage output achieved was about 41 mV with over 95% nitrate removal. The work is discussed in the context of improved MFC performance, potential analytic applications and further innovations using a bio-nanotechnology approach to analyse cell-electrode interactions.
机译:随着对饮用水和废水处理质量的日益提高的监管,需要开发从水中去除含氮化合物的方法。这些过程由多种微生物介导,这些微生物可以将氨氧化为硝酸盐,然后被另一组生物还原为气态氮。这两个阶段的过程涉及相对缓慢地将氨氧化为硝酸盐,然后相对快速地将硝酸盐还原为氮气。硝酸盐还原通常需要在厌氧环境中进行,并添加有机物以提供还原力(电子)来还原硝酸盐。在实际情况下,硝酸盐的还原对于那些精确数量的有机物而言可能是成问题的,以确保在不残留有机物的情况下进行该过程。这项研究的目的是研究使用电化学来源代替有机物作为增白剂的微生物反硝化作用。这项工作还涉及开发一种系统,该系统可以针对诸如鱼场或饮用水中的高硝酸盐含量代表潜在健康问题的应用情况中的硝酸盐去除进行优化。因此,该研究基于用于去除硝酸盐的电化学生物转化系统的发展,研究了从水中去除硝酸盐的一系列进展。这也为这些系统在更广泛的基于生物纳米技术的过程(尤其是生物修复)中的潜在应用提供了很大的空间。研究的第一阶段是研究培养基参数之间的复杂相互作用及其对细菌生长速率的影响。结果证明乙酸盐是细菌生长的良好碳源,因此被用作生物过程的有机底物。通过使用富含土壤接种物的微生物燃料电池(MFC),其中阴极电池供有硝酸盐,阳极电池供有乙酸盐,成功实现了近87%的高硝酸盐去除率。在10.23 mA / m2的电流密度下,获得的最大功率密度为1.26 mW / m2。研究了乙酸盐,硝酸盐和外部电阻对电流产生和反硝化活性的影响,结果表明硝酸盐的去除很大程度上取决于MFC中电流产生的大小。乙酸盐(阳极)和硝酸盐(阴极)浓度的增加改善了该过程,而外部电阻的增加则降低了活性。此外,为了清楚地了解硝酸盐的还原过程,通过生化测试和形态特征检查对相关细菌进行了分析。观察到硝酸盐还原菌的多样性。但是,有一些能够提供完全的反硝化作用。检查了MFC中的纯培养物,获得的电压输出约为混合培养物的36%。获得的硝酸盐去除率为56.2%,这几乎比通过混合细菌实验获得的硝酸盐去除率低31%。为了改善MFC,通过使用碳纳米材料涂覆石墨毡电极的循环伏安法研究了对电极电化学性能的改性。在这项研究中使用的所有纳米材料中,石墨化碳纳米纤维(GCNFs)被选作进一步研究,因为它提供了最佳的电化学性能,并被认为提供了最大的活性表面积。评估了MFC系统与GCNF修饰电极的性能,并观察到了显着的改进。获得的最高电压输出约为41 mV,其中硝酸盐去除率超过95%。在改进的MFC性能,潜在的分析应用以及使用生物纳米技术方法分析细胞-电极相互作用的进一步创新的背景下讨论了这项工作。

著录项

  • 作者

    Alharbi, Njud Saleh F.;

  • 作者单位

    Swansea University (United Kingdom).;

  • 授予单位 Swansea University (United Kingdom).;
  • 学科 Chemical engineering.;Bioengineering.
  • 学位 Ph.D.
  • 年度 2012
  • 页码 223 p.
  • 总页数 223
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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