Laboratory of Microbial Ecology and Technology (LabMET), Ghent University, Gent, Belgium.
Water Res. 2013 Jul 1;47(11):3732-41. doi: 10.1016/j.watres.2013.04.020. Epub 2013 Apr 23.
Anaerobic digestion is a key technology in the bio-based economy and can be applied to convert a wide range of organic substrates into CH4 and CO2. Kitchen waste is a valuable substrate for anaerobic digestion, since it is an abundant source of organic matter. Yet, digestion of single kitchen waste often results in process failure. High-rate activated sludge or A-sludge is produced during the highly loaded first stage of the two-phase 'Adsorptions-Belebungsverfahren' or A/B activated sludge system for municipal wastewater treatment. In this specific case, the A-sludge was amended with FeSO4 to enhance phosphorous removal and coagulation during the water treatment step. This study therefore evaluated whether this Fe-rich A-sludge could be used to obtain stable methanation and higher methane production values during co-digestion with kitchen waste. It was revealed that Fe-rich A-sludge can be a suitable co-substrate for kitchen waste; i.e. methane production rate values of 1.15 ± 0.22 and 1.12 ± 0.28 L L(-1) d(-1) were obtained during mesophilic and thermophilic co-digestion respectively of a feed-mixture consisting of 15% KW and 85% A-sludge. The thermophilic process led to higher residual VFA concentrations, up to 2070 mg COD L(-1), and can therefore be considered less stable. Addition of micro- and macronutrients provided a more stable digestion of single kitchen waste, i.e. a methane production of 0.45 L L(-1) d(-1) was obtained in the micronutrient treatment compared to 0.30 L L(-1) d(-1) in the control treatment on day 61. Yet, methane production during single kitchen waste digestion still decreased toward the end of the experiment, despite the addition of micronutrients. Methane production rates were clearly influenced by the total numbers of archaea in the different reactors. This study showed that Fe-rich A-sludge and kitchen waste are suitable for co-digestion.
厌氧消化是生物基经济中的一项关键技术,可应用于将广泛的有机底物转化为 CH4 和 CO2。厨余垃圾是厌氧消化的一种有价值的底物,因为它是有机物的丰富来源。然而,单一厨余垃圾的消化往往会导致工艺失败。在用于城市污水处理的两相“吸附-生物降解法”或 A/B 活性污泥系统的高负荷第一阶段,会产生高浓度的活性污泥或 A 污泥。在这种特殊情况下,A 污泥中添加了 FeSO4,以在水处理步骤中增强磷的去除和混凝。因此,本研究评估了富含铁的 A 污泥是否可用于与厨余垃圾共消化时获得稳定的甲烷化和更高的甲烷产率。结果表明,富含铁的 A 污泥可以作为厨余垃圾的合适共底物;即在中温和高温共消化由 15%厨余垃圾和 85%A 污泥组成的进料混合物时,分别获得了 1.15±0.22 和 1.12±0.28 L L(-1) d(-1)的甲烷产率值。高温过程导致更高的残留 VFA 浓度,高达 2070 mg COD L(-1),因此可以认为其稳定性较差。添加微量和大量营养素可更稳定地消化单一厨余垃圾,即在微量营养素处理中获得了 0.45 L L(-1) d(-1)的甲烷产率,而在对照处理中则在第 61 天获得了 0.30 L L(-1) d(-1)的甲烷产率。然而,尽管添加了微量营养素,单一厨余垃圾消化过程中的甲烷产率仍在实验结束时下降。甲烷产率明显受到不同反应器中古菌总数的影响。本研究表明,富含铁的 A 污泥和厨余垃圾适合共消化。