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Integrated biological treatment of swine waste for nitrogen removal and energy recovery.

机译:猪废物的综合生物处理,用于脱氮和能量回收。

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摘要

Nitrogen emissions associated with swine waste management have been identified as sources of several adverse public health and environmental effects, including: contamination of drinking water, respiratory diseases, production of ground level ozone, depletion of stratospheric ozone, release of greenhouse gases, and acidification of soils and watersheds. These adverse effects make the technologically and economically feasible removal of nitrogen highly desirable. To understand the technological feasibility of nitrogen removal from swine waste, two biological systems were designed and operated: a traditional, pilot-scale, Modified Ludzack-Ettinger (MLE) process; and a lab-scale, single-reactor, nitritation/anaerobic ammonium oxidation (anammox) process.;The MLE process removed ~98% influent ammonium-N and ∼83% influent total-N. Approximately 75% of the chemical oxygen demand (COD) was oxidized; the majority of COD was utilized as a source of electron equivalents for denitrification. The concentration of COD varied seasonally and full-scale N removal is expected to vary seasonally as well. There was only enough COD for complete denitrification in winter months. Alkalinity in the waste is insufficient to meet the demand associated with nitrification, although the extent of external alkalinity addition is expected to vary seasonally. Of the removed nitrogen, ~8% was released as nitrous oxide, primarily as a side-product of nitrification.;The single-reactor nitritation/anammox process removed up to 96% of influent ammonium-N and up to 90% influent total-N. Several observations indicated anammox as the primary N removal pathway though the relative contribution of denitrification is unknown. This system required at least 49% less oxygen than a conventional nitrogen removal system and required no external alkalinity which should minimize the cost associated with nitrogen removal. Of the removed N, 11% was converted to nitrous oxide.;The microbial community associated with nitritation/anammox was examined by quantitative PCR and bar-coded amplicon sequencing. The microbes known to perform anammox were found to comprise a small fraction of the total biomass. A significant shift in the dominant anammox bacteria was observed, from a seed culture dominated by Candidatus Brocadia to Candidatus Kuenenia dominating in the reactor biomass. An uncharacterized Planctomycete was identified as a dominant member of the community, though it is unknown if this microbe performs anammox.
机译:与猪废物管理有关的氮排放已被确定为造成若干不利的公共健康和环境影响的源头,包括:饮用水污染,呼吸系统疾病,地面臭氧的产生,平流层臭氧的消耗,温室气体的释放以及酸的酸化。土壤和流域。这些不利影响使得在技术上和经济上可行的氮去除成为高度期望的。为了了解从猪粪中脱氮的技术可行性,设计并运行了两个生物系统:传统的中试规模改良Ludzack-Ettinger(MLE)工艺;实验室规模的单反应器硝化/厌氧铵氧化(anammox)工艺。MLE工艺去除了约98%的进水铵态氮和约83%的进水总氮。大约75%的化学需氧量(COD)被氧化; COD的大部分被用作反硝化电子当量的来源。 COD的浓度随季节变化,并且预期的全氮去除率也会随季节变化。在冬季,只有足够的COD才能完全脱氮。废物中的碱度不足以满足硝化相关的需求,尽管外部碱度的添加量预计会随季节变化。在除去的氮中,约有8%的氮氧化物以一氧化二氮的形式释放出来,主要是作为硝化的副产物。单反应器硝化/厌氧氨氧化工艺除去了高达96%的流入的N-铵和高达90%的流入的总氮。 N.尽管反硝化的相对贡献尚不清楚,但有几项观察表明厌氧氨氧化是主要的氮去除途径。与传统的脱氮系统相比,该系统所需的氧气至少少49%,并且不需要外部碱度,这应将与脱氮相关的成本降至最低。去除的氮中有11%转化为一氧化二氮。通过定量PCR和条形码扩增子测序检查了与硝化/氨氧化有关的微生物群落。发现已知执行厌氧氨氧化的微生物仅占总生物量的一小部分。观察到优势厌氧菌发生了显着变化,从以Brocadia念珠菌为主导的种子培养物转变为以反应器生物质为主的Kuednia念珠菌。尽管尚不清楚这种微生物是否会表现出厌氧菌作用,但未鉴定出的浮游菌被认为是该群落的主要成员。

著录项

  • 作者

    Staunton, Eric Timothy.;

  • 作者单位

    The University of North Carolina at Chapel Hill.;

  • 授予单位 The University of North Carolina at Chapel Hill.;
  • 学科 Environmental engineering.;Microbiology.
  • 学位 Ph.D.
  • 年度 2015
  • 页码 200 p.
  • 总页数 200
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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