Biofouling and Biofilm Processes Section, WSCD, Chemistry Group, Bhabha Atomic Research Centre, Kalpakkam, 603102, India; Homi Bhabha National Institute, Anushakti Nagar, Mumbai, 400 094, India.
Biofouling and Biofilm Processes Section, WSCD, Chemistry Group, Bhabha Atomic Research Centre, Kalpakkam, 603102, India; Homi Bhabha National Institute, Anushakti Nagar, Mumbai, 400 094, India.
Environ Res. 2023 May 1;224:115500. doi: 10.1016/j.envres.2023.115500. Epub 2023 Feb 14.
Long start-up periods for granulating activated sludge and concerns on granular stability are the bottlenecks reported during implementation of novel aerobic granular sludge (AGS) technology in municipal wastewater treatment plants. Here, de novo granulation of sewage-borne microorganisms without using activated sludge (AS) inoculum was investigated in bench-scale sequencing batch reactors (SBR). Data showed that formation of AGS from sewage-borne microorganisms was rapid and first granules appeared within one week. Granulation was indicated by appearance of biomass particles (size >0.12 mm), high biomass levels (∼8 g/L) and superior settling properties (SVI: 30 mL/g). Granulation process involved distinct stages like formation of aggregates, retention of aggregates, and growth of millimetre sized granules. Simultaneous COD, nitrogen and phosphorous removal was established within 10 days of start-up in the SBR without using AS inoculum. However, phosphorus removal became stable after 50 days of start-up. Total nitrogen (TN) and total phosphorus (TP) removals of 92% and 70%, respectively, were achieved from real domestic wastewater. Furthermore, addition of granular activated carbon (GAC) had improved both granulation and biological nutrient removals. Interestingly, phosphorus removal became quite stable within 10 days of start-up in the SBR operated with GAC particles. TN and TP removals were found to be higher at >98% and >94%, respectively, in GAC-augmented SBR. Removal of ammonia and phosphorus were mediated by nitritation-denitritation and enhanced biological phosphorus removal (EBPR) pathways, respectively. The bacterial diversity of AGS was lower than that of sewage. Quantitative PCR indicated enrichment of ammonia oxidizing bacteria, denitrifying bacteria and polyphosphate accumulating organisms during granulation. De novo granulation of sewage-borne microorganisms is a promising approach for rapidly cultivating AGS and establishing biological nutrient removal in sewage treatment plants.
新型好氧颗粒污泥 (AGS) 技术在城市污水处理厂的应用存在启动时间长和颗粒稳定性等问题。本研究在序批式间歇反应器 (SBR) 中,利用污水中原生微生物,在不接种活性污泥 (AS) 的情况下,启动颗粒污泥。结果表明,污水中原生微生物可快速启动并形成 AGS,第 1 周内即可出现颗粒。颗粒形成的标志是生物量颗粒(粒径>0.12mm)的出现、高生物量水平(∼8g/L)和良好的沉降性能(SVI:30mL/g)。颗粒化过程涉及多个阶段,包括聚集物的形成、聚集物的保留和毫米级颗粒的生长。在不接种 AS 的情况下,SBR 在启动后 10 天内即可同时去除 COD、氮和磷。然而,磷的去除在启动后 50 天才稳定。从实际生活污水中,分别实现了 92%和 70%的总氮 (TN) 和总磷 (TP) 去除率。此外,添加颗粒活性炭 (GAC) 不仅提高了颗粒化和生物脱氮除磷效果。有趣的是,在含有 GAC 颗粒的 SBR 中,启动后 10 天内磷的去除就相当稳定。在 GAC 强化 SBR 中,TN 和 TP 的去除率分别高达 98%和 94%以上。氨氮和磷的去除分别通过亚硝化-反硝化和增强型生物除磷 (EBPR) 途径进行。AGS 的细菌多样性低于污水。定量 PCR 结果表明,在颗粒化过程中氨氧化菌、反硝化菌和聚磷菌得到了富集。利用污水中原生微生物,不经接种即可快速启动颗粒污泥,为污水处理厂建立生物脱氮除磷提供了一种有前景的方法。