Department of Chemical and Environmental Engineering, University of Ovieo, C/ Julián Clavería s/n, E-33071 Oviedo, Spain.
Department of Chemical and Environmental Engineering, University of Ovieo, C/ Julián Clavería s/n, E-33071 Oviedo, Spain.
Water Res. 2016 Nov 15;105:282-290. doi: 10.1016/j.watres.2016.09.004. Epub 2016 Sep 7.
Thermal pre-treatments of activated sludge involve the release of a high amount of polymeric substances into the bulk medium. The molecular size of these polymers will largely define the subsequent biological treatment of the liquid effluent generated. In this work, the effects of wet oxidation treatment (WO) on the fingerprints of the polymeric substances which compose the activated sludge, were analysed. For a better understanding of these transformations, the sludge was separated into its main fractions: soluble microbial products (SMP), loosely bound extracellular polymeric substances (LB-EPS), tightly bound extracellular polymeric substances (TB-EPS) and naked cells, and then each one was subjected to WO separately (190 °C and 65 bar), determining the fingerprints evolution by size exclusion technique. Results revealed a fast degradation of larger molecules (over 500 kDa) during the first minutes of treatment (40 min). WO also increases the absorptive properties of proteins (especially for 30 kDa), which is possibly due to the hydroxylation of phenylalanine amino acids in their structure. WO of naked cells involved the formation of molecules between 23 and 190 kDa, which are related to the release of cytoplasmic polymers, and more hydrophobic polymers, probably from the cell membrane. The results allowed to establish a relationship between the location of polymeric material and its facility to become oxidised; thus, the more internal the polymeric material in the cell, the easier its oxidation. When working directly with the raw sludge, hydrolysis mechanisms played a key role during the starting period. Once a high degree of solubilisation was reached, the molecules were rapidly oxidised into other compounds with refractory characteristics. The final effluent after WO showed almost 90% of low molecular weight solubilised substances (0-35 kDa).
活性污泥的热预处理会将大量的聚合物质释放到主体介质中。这些聚合物的分子大小将在很大程度上决定随后对产生的液体废水的生物处理。在这项工作中,分析了湿式氧化处理(WO)对构成活性污泥的聚合物质指纹的影响。为了更好地理解这些转化,将污泥分离成其主要部分:可溶性微生物产物(SMP)、松散结合的胞外聚合物物质(LB-EPS)、紧密结合的胞外聚合物物质(TB-EPS)和裸露细胞,然后分别对它们进行 WO(190°C 和 65 巴),通过尺寸排阻技术确定指纹的演变。结果表明,在处理的最初几分钟内(40 分钟),较大分子(超过 500 kDa)迅速降解。WO 还增加了蛋白质的吸收特性(特别是对于 30 kDa 的蛋白质),这可能是由于其结构中的苯丙氨酸氨基酸的羟化。裸露细胞的 WO 涉及到 23 至 190 kDa 之间的分子的形成,这些分子与细胞质聚合物的释放以及更疏水的聚合物有关,可能来自细胞膜。结果建立了聚合材料的位置与其被氧化的能力之间的关系;因此,细胞内聚合材料的位置越内部,其氧化就越容易。当直接处理原始污泥时,水解机制在起始阶段起着关键作用。一旦达到高溶解度,分子就会迅速氧化成具有抗降解特性的其他化合物。WO 后的最终流出物几乎含有 90%的低分子量溶解物质(0-35 kDa)。