Eskicioglu Cigdem, Prorot Audrey, Marin Juan, Droste Ronald L, Kennedy Kevin J
School of Engineering, University of British Columbia Okanagan, Kelowna, BC, Canada.
Water Res. 2008 Nov;42(18):4674-82. doi: 10.1016/j.watres.2008.08.010. Epub 2008 Aug 19.
A microwave-enhanced advanced hydrogen peroxide oxidation process (MW/H(2)O(2)-AOP) was studied in order to investigate the synergetic effects of MW irradiation on H(2)O(2) treated waste activated sludges (WAS) in terms of mineralization (permanent stabilization), sludge disintegration/solubilization, and subsequent anaerobic biodegradation as well as dewaterability after digestion. Thickened WAS sample pretreated with 1gH(2)O(2)/g total solids (TS) lost 11-34% of its TS, total chemical oxygen demand (COD) and total biopolymers (humic acids, proteins and sugars) via advanced oxidation. In a temperature range of 60-120 degrees C, elevated MW temperatures (>80 degrees C) further increased the decomposition of H(2)O(2) into OH* radicals and enhanced both oxidation of COD and solubilization of particulate COD (>0.45 micron) of WAS indicating that a synergetic effect was observed when both H(2)O(2) and MW treatments were combined. However, at all temperatures tested, MW/H(2)O(2) treated samples had lower first-order mesophilic (33+/-2 degrees C) biodegradation rate constants and ultimate (after 32 days of digestion) methane yields (mL per gram sample) compared to control and MW irradiated WAS samples, indicating that synergistically (MW/H(2)O(2)-AOP) generated soluble organics were slower to biodegrade or more refractory than those generated during MW irradiation.
为了研究微波辐照对过氧化氢处理过的废弃活性污泥(WAS)在矿化(永久稳定化)、污泥解体/溶解、随后的厌氧生物降解以及消化后脱水性能方面的协同效应,对一种微波增强的高级过氧化氢氧化工艺(MW/H₂O₂ - AOP)进行了研究。用1gH₂O₂/g总固体(TS)预处理的浓缩WAS样品,通过高级氧化损失了其TS、总化学需氧量(COD)和总生物聚合物(腐殖酸、蛋白质和糖类)的11 - 34%。在60 - 120℃的温度范围内,升高的微波温度(>80℃)进一步促进了H₂O₂分解为OH*自由基,并增强了WAS的COD氧化和颗粒状COD(>0.45微米)的溶解,这表明当H₂O₂和微波处理相结合时观察到了协同效应。然而,在所有测试温度下,与对照和微波辐照的WAS样品相比,MW/H₂O₂处理的样品具有更低的一级中温(33±2℃)生物降解速率常数和最终(消化32天后)甲烷产量(每克样品毫升数),这表明协同产生的可溶性有机物比微波辐照过程中产生的那些有机物更难生物降解或更具难降解性。