School of Infrastructure, Indian Institute of Technology Bhubaneswar, Odisha, India.
Environ Technol. 2023 Nov;44(25):3791-3802. doi: 10.1080/09593330.2022.2072238. Epub 2022 May 11.
In this study, simultaneous nitrification and denitrification-sequencing batch reactor (SND-SBR) process was investigated to treat greywater. The effect of three process parameters, including hydraulic retention time (HRT), volumetric exchange ratio (VER) and sludge retention time (SRT), was optimised using a 2 full factorial design. The statistic model was developed for two response variables, i.e. chemical oxygen demand (COD) and ammonia (NH-N) removal. The optimum conditions were 6.8 h HRT (anaerobic/aerobic/anoxic: 1.77 h/2.77 h/2.27 h), 0.7 VER and 7.94 d SRT, which resulted in 93.9% COD and 84.6% NH-N removal efficiency. SRT was the most significant factor, followed by HRT and VER for COD and NH-N removal. The interaction effect of VER and SRT was significant in COD removal. On the other hand, the interaction effects of HRT-VER and HRT-SRT were significant in NH-N removal. The removal efficiencies of 89.6 ± 1.1% and 83.7 ± 2.3% were observed for TKN and TN, respectively, in the optimised SND-SBR system. NH-N removal was obtained via nitrate pathway in the SND-SBR system. The PO-P removal of 74.2 ± 3.4% was obtained via aerobic phosphorus uptake and post anoxic denitrification at the optimal condition. To enhance PO-P removal, adsorption (using corn cob adsorbent) was integrated with SBR by adding the optimum adsorbent dose (0.5 g/L). The PO-P removal efficiency in the SBR-adsorption system was found to be 80 ± 1.5%. The biodegradation of emerging contaminants (ECs) was also carried out in the SND-SBR system, and the results showed removal rate of 58.9 ± 2.3% benzophenone-3 (BP) and 80.1 ± 2.2% anionic surfactant (AS).
在这项研究中,采用序批式间歇反应器(SBR)同步硝化反硝化(SND)工艺处理灰水。采用 2 因素完全实验设计优化了 3 个工艺参数,包括水力停留时间(HRT)、体积交换比(VER)和污泥停留时间(SRT)。建立了两个响应变量,即化学需氧量(COD)和氨氮(NH-N)去除率的统计模型。最佳条件为 HRT 6.8 h(厌氧/好氧/缺氧:1.77 h/2.77 h/2.27 h)、VER 0.7 和 SRT 7.94 d,COD 和 NH-N 的去除率分别为 93.9%和 84.6%。SRT 是 COD 和 NH-N 去除的最主要因素,其次是 HRT 和 VER。在 COD 去除方面,VER 和 SRT 的交互作用显著。另一方面,在 NH-N 去除方面,HRT-VER 和 HRT-SRT 的交互作用显著。在优化的 SND-SBR 系统中,TKN 和 TN 的去除率分别为 89.6±1.1%和 83.7±2.3%。NH-N 的去除是通过 SND-SBR 系统中的硝酸盐途径实现的。在最佳条件下,通过好氧吸磷和缺氧后反硝化,可获得 74.2±3.4%的 PO-P 去除率。为了提高 PO-P 的去除率,通过向 SBR 中添加最佳吸附剂剂量(0.5 g/L),将吸附(使用玉米芯吸附剂)与 SBR 集成。在 SBR-吸附系统中,PO-P 的去除率为 80±1.5%。在 SND-SBR 系统中也进行了新兴污染物(ECs)的生物降解实验,结果表明,BP 的去除率为 58.9±2.3%,AS 的去除率为 80.1±2.2%。