School of Environmental and Municipal Engineering, Qingdao University of Technology, Qingdao 266033, PR China.
School of Environmental and Municipal Engineering, Qingdao University of Technology, Qingdao 266033, PR China.
Waste Manag. 2017 Nov;69:242-249. doi: 10.1016/j.wasman.2017.08.022. Epub 2017 Aug 12.
The carbon-nitrogen ratio (COD/NH-N) is an important factor affecting nitrification and denitrification in wastewater treatment; this factor also influences nitrous oxide (NO) emissions. This study investigated two simulated intermittently aerated semi-aerobic aged refuse bioreactors (SAARB) filled with 8-year old aged refuse (AR). The research analyzed how differences in and the combination of influent COD and NH-N impact NO emissions in leachate treatment. Experimental results showed that NO emissions increased as the influent COD/NH-N decreased. The influent COD had a greater effect on NO emissions than NH-N at the same influent ratios of COD/NH-N (2.7 and 8.0, respectively). The maximum NO emission accounted for 8.82±2.65% of the total nitrogen removed from the influent leachate; the maximum level occurred when the COD was 2000mg/L. An analysis of differences in influent carbon sources at the same COD/NH-N ratios concluded that the availability of biodegradable carbon substrates (i.e. glucose) is an important factor affecting NO emissions. At a low influent COD/NH-N ratio (2.7), the NO conversion rate was greater when there were more biodegradable carbon substrates. Although the SAARB included the NO generation and reduction processes, NO reduction mainly occurred later in the process, after leachate recirculation. The maximum NO emission rate occurred in the first hour of single-period (24h) experiments, as leachate contacted the surface AR. In practical SAARB applications, NO emissions may be reduced by measures such as reducing the initial recirculation loading of NH-N substrates, adding a later supplement of biodegradable carbon substrates, and/or prolonging hydraulic retention time (HRT) of influent leachate.
碳氮比(COD/NH-N)是影响废水处理中硝化和反硝化的一个重要因素;这个因素也会影响氧化亚氮(NO)的排放。本研究调查了两个模拟间歇曝气半好氧老化垃圾生物反应器(SAARB),其中填充了 8 年的老化垃圾(AR)。研究分析了进水 COD 和 NH-N 的差异以及组合对渗滤液处理中 NO 排放的影响。实验结果表明,随着进水 COD/NH-N 的降低,NO 排放增加。在相同的进水 COD/NH-N 比(分别为 2.7 和 8.0)下,进水 COD 对 NO 排放的影响大于 NH-N。最大 NO 排放量占进水渗滤液中总氮去除量的 8.82±2.65%;当 COD 为 2000mg/L 时,NO 排放量最大。对相同 COD/NH-N 比下进水碳源差异的分析表明,可生物降解碳基质(如葡萄糖)的可用性是影响 NO 排放的一个重要因素。在低进水 COD/NH-N 比(2.7)下,当有更多可生物降解的碳基质时,NO 转化率更高。虽然 SAARB 包括了 NO 的产生和还原过程,但 NO 的还原主要发生在渗滤液再循环之后的过程中。在单周期(24h)实验的第一个小时,当渗滤液与表面 AR 接触时,NO 排放速率最大。在实际的 SAARB 应用中,可以通过减少初始 NH-N 基质再循环负荷、添加后期可生物降解碳基质的补充以及/或延长进水渗滤液的水力停留时间(HRT)等措施来减少 NO 排放。