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污泥中温热处理过程中有机物的命运:生物聚合物和水解活性释放的动力学及其对厌氧消化污泥减量的影响。

Fate of organic matter during moderate heat treatment of sludge: kinetics of biopolymer and hydrolytic activity release and impact on sludge reduction by anaerobic digestion.

机构信息

Université de Toulouse; UPS; LBAE; IUT A, 24 rue d'Embaquès, F-32000 Auch, France E-mail:

Université de Toulouse; INSA, UPS, INP, LISBP, 135 Avenue de Rangueil, F-31077 Toulouse - INRA, UMR792 F-31400 Toulouse - CNRS, UMR5504, F-31400 Toulouse, France.

出版信息

Water Sci Technol. 2014;69(9):1828-33. doi: 10.2166/wst.2014.083.

DOI:10.2166/wst.2014.083
PMID:24804656
Abstract

Temperature-phased anaerobic digestion with a 50-70 °C pre-treatment is widely proposed for sludge. Here, such a sludge pre-treatment (65 °C) was studied against the physical, enzymatic and biodegradation processes. The soluble and particulate fractions were analysed in terms of biochemical composition and hydrolytic enzymatic activities. Two kinetics of organic matter solubilisation were observed: a rapid transfer of the weak-linked biopolymers to the water phase, including sugars, proteins or humic acid-like substances, to the water phase, followed by a slow and long-term solubilisation of proteins and humic acid-like substances. In addition, during the heat treatment a significant pool of thermostable hydrolytic enzymes including proteases, lipases and glucosidases remains active. Consequently, a global impact on organic matter was the transfer of the biodegradable chemical oxygen demand (COD) from the particulate to the soluble fraction as evaluated by the biological methane potential test. However, the total biodegradable COD content of the treated sludge remained constant. The heat process improves the bio-accessibility of the biodegradable molecules but doesn't increase the inherent sludge biodegradability, suggesting that the chemistry of the refractory proteins and humic acids seems to be the real limit to sludge digestion.

摘要

温度分相厌氧消化与 50-70°C 的预处理广泛应用于污泥处理。在这里,研究了这种污泥预处理(65°C)对物理、酶和生物降解过程的影响。根据生化成分和水解酶活性分析了可溶和颗粒两部分。观察到两种有机物溶解动力学:一种是弱键生物聚合物快速转移到水相,包括糖、蛋白质或类腐殖质物质,随后是蛋白质和类腐殖质物质的缓慢和长期溶解。此外,在热处理过程中,包括蛋白酶、脂肪酶和糖苷酶在内的大量耐热水解酶仍然保持活性。因此,正如生物甲烷潜力测试所评估的,有机物质的整体影响是可生物降解化学需氧量(COD)从颗粒相向可溶相的转移。然而,处理后的污泥的总可生物降解 COD 含量保持不变。热过程提高了可生物降解分子的生物可利用性,但不会增加内在的污泥生物降解性,这表明难生物降解的蛋白质和腐殖酸的化学性质似乎是污泥消化的真正限制因素。

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