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序批式反应器中开发好氧颗粒污泥和光颗粒的启动策略。

Start-up strategies to develop aerobic granular sludge and photogranules in sequential batch reactors.

机构信息

Federal University of Pernambuco, Department of Civil and Environmental Engineering, Laboratory of Environmental Sanitation. Av. Academico Helio Ramos, s/n. Cidade Universitária, CEP 50740-530 Recife, PE, Brazil.

Federal University of Pernambuco, Department of Civil and Environmental Engineering, Laboratory of Environmental Sanitation. Av. Academico Helio Ramos, s/n. Cidade Universitária, CEP 50740-530 Recife, PE, Brazil.

出版信息

Sci Total Environ. 2022 Jul 1;828:154402. doi: 10.1016/j.scitotenv.2022.154402. Epub 2022 Mar 8.

DOI:10.1016/j.scitotenv.2022.154402
PMID:35276148
Abstract

In this study, start-up strategies to develop conventional aerobic granular sludge (AGS) and algal aerobic granular sludge (AAGS) (photogranules), were investigated. The granulation experiment was conducted in four sequencing batch reactors (SBR), of which two were conventional SBRs (RC1, RC2) used as control, and two were photo-SBRs (R1, R2). R1 and RC1 were operated with a 40-min feeding during the reactors´ anaerobic cycle period, whereas R2 and RC2 with a 60-min feeding. All the reactors were operated in two phases with a C:N = 4:1 in Phase I and 8:1 in Phase II. In Phase I, AGS in RC1 and RC2 was formed 15 days before the AAGS development in R1 and R2. However, the AAGS generally presented better stability and higher diameter. On the other hand, AGS presented greater abundance of extracellular polymeric substances producing organisms, such as Xanthomonadacea and Rhodocyclaceae. Chemical oxygen demand (COD) and NH-N removal efficiencies were similar in all the four reactors of approximately 70% and 60%, respectively. In this phase, despite the good biomass structure, the reactors were not able to completely oxidize the high influent concentration of NH-N (100 mg.L) and COD (400 mg.L). This can be associated to the short time of the aerobic phase and low biomass content. In Phase II in all the reactors, a good increase in COD and NH-N removal efficiencies to values above 95% and 93%, respectively, was achieved under a higher C:N ratio of 8 with lower influent concentration of NH-N (50 mg.L). The 60-min anaerobic feeding period in R2 and RC2 resulted in greater removal efficiency of nitrogen, confirming that small variation on cycle periods can affect the biomass composition; the biomass presented more compact granules and larger diameters under 60 min-feeding when compared with those obtained with 40 min-feeding in Phase I.

摘要

本研究旨在探索开发传统好氧颗粒污泥(AGS)和藻好氧颗粒污泥(AAGS)(光颗粒)的启动策略。该颗粒化实验在四个序批式反应器(SBR)中进行,其中两个为传统 SBR(RC1、RC2)作为对照,两个为光 SBR(R1、R2)。R1 和 RC1 在反应器厌氧循环期间的 40 分钟给料期间进行操作,而 R2 和 RC2 则进行 60 分钟给料。所有反应器均在两个阶段运行,第一阶段 C:N 为 4:1,第二阶段 C:N 为 8:1。在第一阶段,RC1 和 RC2 中的 AGS 在 R1 和 R2 中 AAGS 开发前 15 天形成。然而,AAGS 通常表现出更好的稳定性和更高的直径。另一方面,AGS 产生更多的胞外聚合物物质产生的生物体,如黄单胞菌科和红环菌科。所有四个反应器的化学需氧量(COD)和 NH-N 去除效率相似,分别约为 70%和 60%。在这个阶段,尽管生物量结构良好,但反应器无法完全氧化高进水浓度的 NH-N(100mg.L)和 COD(400mg.L)。这可能与好氧阶段时间短和生物量含量低有关。在第二阶段,所有反应器的 COD 和 NH-N 去除效率均有较好的提高,分别达到 95%以上和 93%以上,进水 NH-N 浓度(50mg.L)较低,C:N 比为 8。R2 和 RC2 中 60 分钟的厌氧给料时间导致氮的去除效率更高,证实周期时间的微小变化会影响生物量组成;与第一阶段 40 分钟给料相比,60 分钟给料时生物量呈现出更紧凑的颗粒和更大的直径。

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