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Landfill leachate treatment with a novel process: Anaerobic ammonium oxidation (Anammox) combined with soil infiltration system

机译:新型工艺处理垃圾渗滤液:厌氧铵氧化(Anammox)结合土壤入渗系统

摘要

A novel combined process was proposed to treat municipal landfill leachate with high concentrations of ammonium and organics. This process consisted of a partial nitritation reactor (PNR), an anaerobic ammonium oxidation (Anammox) reactor (AR) and two underground soil infiltration systems (USIS-1 and USIS-2). Based on the optimum operating conditions obtained from batch tests of individual unit, the combined process was continuously operated on a bench scale for 166 days. Partial nitritation was performed in a fixed bio-film reactor (PNR, working volume= 12 L). Ammonium nitrogen-loading rate (Nv) and DO were combined to monitor partial nitritation, and at T = 30 +/- 1 degrees C, Nv = 0.27-1.2 kg/(m(3).d), DO = 0.8-2.3 mg/L, the ratios of nitrite nitrogen (NO2--N) to ammonium nitrogen (NH4+-N) were successfully kept close to 1.0-1.3 in the effluent. Nitrate nitrogen (NO3--N) less than 43 mg/L was observed. The effluent of PNR was ideally suited as influent of AR. Sixty-nine percent CODcr from the raw leachate was degraded in the PNR. Anammox was carried out in a fixed bio-film reactor (AR, working volume= 36 L). At T = 30 +/- 1 degrees C. Nv = 0.06-0.11 kg/(m(3).d), about 60% NH4+-N and 64% NO2--N in the influent of AR were simultaneously removed. Inhibition of high-strength NO2--N (up to 1011 mg/L) should be responsible for the low removal rate of nitrogen. About 35% aquatic humic substance (AHS) was degraded in the AR. With the same working volume (200 L), USIS-1 and USIS-2 were alternately performed to treat the effluent from AR at one cycle of about 30 days. At hydraulic loading rate (HLR) = 0.02-0.04 m(3)/m(3).d, pollutant loading rates (PLR) = NH4+-N = 14 g/m(3).d, TN = 25 g/m(3).d, and CODcr = 13 g/m(3).d, average removal efficiencies of 88% NH4+-N, 67% TN and 55% CODcr were obtained. Overall, raw leachate with 1430-2720 mg NH4+-N/L, 1524-2912 mg TN/L and 1165-2599 mg CODcr/L, was treated by the process and the effluent with 22-58 mg NH4+-N/L, 108-300 mg TN/L and 32-250 mg CODcr/L was obtained with average removal efficiencies of 97% NH4+-N, 87% TN and 89% CODcr. The test results indicated that the combined system could work stably over a long period under the operating conditions, and that the process was feasible for the leachate treatment. AR should be the key to the performance of the combined process. (c) 2007 Elsevier B.V. All rights reserved.
机译:提出了一种新颖的联合工艺来处理含高浓度铵和有机物的市政垃圾渗滤液。该过程由部分硝化反应器(PNR),厌氧铵氧化(Anammox)反应器(AR)和两个地下土壤入渗系统(USIS-1和USIS-2)组成。根据从单个单元的批处理测试获得的最佳操作条件,组合过程在台式规模上连续运行166天。在固定的生物膜反应器(PNR,工作体积= 12 L)中进行部分硝化。氨氮负荷率(Nv)和DO结合起来以监测部分硝化作用,在T = 30 +/- 1摄氏度时,Nv = 0.27-1.2 kg /(m(3).d),DO = 0.8-2.3以mg / L为单位,废水中亚硝酸盐氮(NO2--N)与铵态氮(NH4 + -N)的比率已成功保持接近1.0-1.3。硝酸盐氮(NO3--N)低于43 mg / L。 PNR的废水非常适合用作AR的废水。在PNR中,来自原始渗滤液的69%的CODcr被降解。厌氧氨氧化在固定的生物膜反应器(AR,工作体积= 36 L)中进行。在T = 30 +/- 1摄氏度。Nv= 0.06-0.11 kg /(m(3).d)时,AR进水中的约60%NH4 + -N和64%NO2--N被同时去除。抑制高强度NO2--N(最高1011 mg / L)应该是氮去除率低的原因。 AR中降解了约35%的水生腐殖质(AHS)。在相同的工作量(200升)下,以大约30天的一个周期交替进行USIS-1和USIS-2处理AR的废水。在水力负荷率(HLR)= 0.02-0.04 m(3)/ m(3).d时,污染物负荷率(PLR)= NH4 + -N <= 14 g / m(3).d,TN <= 25 g /m(3).d和CODcr <= 13 g / m(3).d,平均去除效率为88%NH4 + -N,67%TN和55%CODcr。总体而言,通过该工艺处理含1430-2720 mg NH4 + -N / L,1524-2912 mg TN / L和1165-2599 mg CODcr / L的原渗滤液,并采用22-58 mg NH4 + -N / L处理废水,获得108-300 mg TN / L和32-250 mg CODcr / L,平均去除效率为97%NH4 + -N,87%TN和89%CODcr。试验结果表明,该组合系统在工况下可以长期稳定运行,该工艺可行。 AR应该是组合过程执行的关键。 (c)2007 Elsevier B.V.保留所有权利。

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    Liang Zhu; Liu Junxin;

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  • 年度 2008
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