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废水高速低温厌氧消化过程中的生物除磷

Biological Phosphorus Removal During High-Rate, Low-Temperature, Anaerobic Digestion of Wastewater.

作者信息

Keating Ciara, Chin Jason P, Hughes Dermot, Manesiotis Panagiotis, Cysneiros Denise, Mahony Therese, Smith Cindy J, McGrath John W, O'Flaherty Vincent

机构信息

Microbial Ecology Laboratory, Microbiology, School of Natural Sciences and Ryan Institute, National University of Ireland Galway Ireland.

School of Biological Sciences and the Institute for Global Food Security, The Queen's University of Belfast Belfast, UK.

出版信息

Front Microbiol. 2016 Mar 3;7:226. doi: 10.3389/fmicb.2016.00226. eCollection 2016.

DOI:10.3389/fmicb.2016.00226
PMID:26973608
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC4776080/
Abstract

We report, for the first time, extensive biologically mediated phosphate removal from wastewater during high-rate anaerobic digestion (AD). A hybrid sludge bed/fixed-film (packed pumice stone) reactor was employed for low-temperature (12°C) anaerobic treatment of synthetic sewage wastewater. Successful phosphate removal from the wastewater (up to 78% of influent phosphate) was observed, mediated by biofilms in the reactor. Scanning electron microscopy and energy dispersive X-ray analysis revealed the accumulation of elemental phosphorus (∼2%) within the sludge bed and fixed-film biofilms. 4', 6-diamidino-2-phenylindole (DAPI) staining indicated phosphorus accumulation was biological in nature and mediated through the formation of intracellular inorganic polyphosphate (polyP) granules within these biofilms. DAPI staining further indicated that polyP accumulation was rarely associated with free cells. Efficient and consistent chemical oxygen demand (COD) removal was recorded, throughout the 732-day trial, at applied organic loading rates between 0.4 and 1.5 kg COD m(-3) d(-1) and hydraulic retention times of 8-24 h, while phosphate removal efficiency ranged from 28 to 78% on average per phase. Analysis of protein hydrolysis kinetics and the methanogenic activity profiles of the biomass revealed the development, at 12°C, of active hydrolytic and methanogenic populations. Temporal microbial changes were monitored using Illumina MiSeq analysis of bacterial and archaeal 16S rRNA gene sequences. The dominant bacterial phyla present in the biomass at the conclusion of the trial were the Proteobacteria and Firmicutes and the dominant archaeal genus was Methanosaeta. Trichococcus and Flavobacterium populations, previously associated with low temperature protein degradation, developed in the reactor biomass. The presence of previously characterized polyphosphate accumulating organisms (PAOs) such as Rhodocyclus, Chromatiales, Actinobacter, and Acinetobacter was recorded at low numbers. However, it is unknown as yet if these were responsible for the luxury polyP uptake observed in this system. The possibility of efficient phosphate removal and recovery from wastewater during AD would represent a major advance in the scope for widespread application of anaerobic wastewater treatment technologies.

摘要

我们首次报道了在高速厌氧消化(AD)过程中,生物介导的从废水中大量去除磷的现象。采用混合污泥床/固定膜(填充浮石)反应器对合成污水进行低温(12°C)厌氧处理。观察到成功从废水中去除了磷(高达进水磷含量的78%),这是由反应器中的生物膜介导的。扫描电子显微镜和能量色散X射线分析显示,污泥床和固定膜生物膜中积累了元素磷(约2%)。4',6-二脒基-2-苯基吲哚(DAPI)染色表明,磷的积累本质上是生物性的,是通过在这些生物膜中形成细胞内无机多聚磷酸盐(polyP)颗粒介导的。DAPI染色进一步表明,polyP的积累很少与游离细胞相关。在整个732天的试验中,当有机负荷率在0.4至1.5 kg COD m(-3) d(-1)之间且水力停留时间为8至24小时时,记录到了高效且稳定的化学需氧量(COD)去除情况,而各阶段磷去除效率平均在28%至78%之间。对生物质的蛋白质水解动力学和产甲烷活性曲线的分析表明,在12°C时,活跃的水解和产甲烷菌群得以发展。使用Illumina MiSeq对细菌和古菌的16S rRNA基因序列进行分析,监测了微生物的时间变化。试验结束时,生物质中占主导地位的细菌门是变形菌门和厚壁菌门,占主导地位的古菌属是甲烷鬃菌属。之前与低温蛋白质降解相关的Trichococcus和黄杆菌种群在反应器生物质中得以发展。记录到了数量较少的先前已鉴定的聚磷菌(PAO),如红环菌属、色杆菌目、放线菌属和不动杆菌属。然而,目前尚不清楚这些是否是造成该系统中观察到的奢侈性polyP摄取的原因。在厌氧消化过程中从废水中高效去除和回收磷的可能性,将代表厌氧废水处理技术广泛应用范围的一项重大进展。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/d6e1/4776080/dadd0add0fe3/fmicb-07-00226-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/d6e1/4776080/c0984e0846c1/fmicb-07-00226-g001.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/d6e1/4776080/c0984e0846c1/fmicb-07-00226-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/d6e1/4776080/d1a7c761cdbd/fmicb-07-00226-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/d6e1/4776080/f6c56bda9876/fmicb-07-00226-g003.jpg
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