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食品废物厌氧消化中产 HS 的特性和机制。

Characteristics and mechanisms of HS production in anaerobic digestion of food waste.

机构信息

Environmental Simulation and Pollution Control State Key Joint Laboratory, School of Environment, Tsinghua University, Beijing 100084, China.

Environmental Simulation and Pollution Control State Key Joint Laboratory, School of Environment, Tsinghua University, Beijing 100084, China; State Environmental Protection Key Laboratory of Microorganism Application and Risk Control (SMARC), Graduate School at Shenzhen, Tsinghua University, Shenzhen 518055, China.

出版信息

Sci Total Environ. 2020 Jul 1;724:137977. doi: 10.1016/j.scitotenv.2020.137977. Epub 2020 Mar 16.

Abstract

The biogas produced in food waste anaerobic digestion (FWAD) contains HS which can lead to corrosion, bad smell and poisoning accident. To control HS pollution, the characteristics and mechanisms of HS production in FWAD should be known. In this study, a lab-scale FWAD batch test was applied for 20 days under 35 °C. The production potential and average concentration of HS were 765 ± 163 g/t (TS) and 1065 ± 267 ppm, respectively. 76% of total HS was produced within 6 h on the first day of fermentation, acidification and gas production were key reasons for high HS production at this time. Compared to HS peak production time, that of methane was long (4 days) and after that of HS. Sulfides were found to be the dominant form of sulfur (accounting for 20-70% of total sulfur) in the mixed fermentation liquor in fermentation batch. These sulfides were from protein, which could be decomposed slowly to sulfide by protein-using bacteria and methanogen at the time of methane production peak, and sulfate, which could be converted to sulfide by Sulfate reducing bacteria (SRB) during the first two days of fermentation. Protein would be the main contributor to sulfide/HS for the continuous feeding FWAD system in long term operation, due to its presence as the main form of sulfur in food waste.

摘要

在食物垃圾厌氧消化(FWAD)中产生的沼气中含有 H2S,这可能导致腐蚀、恶臭和中毒事故。为了控制 H2S 污染,应该了解 FWAD 中 H2S 的产生特性和机制。在这项研究中,应用了一个实验室规模的 FWAD 批处理测试,在 35°C 下进行了 20 天。HS 的产生潜力和平均浓度分别为 765±163g/t(TS)和 1065±267ppm。在发酵的第一天,76%的总 HS 在 6 小时内产生,酸化和产气是此时 HS 产生量高的关键原因。与 HS 峰值生产时间相比,甲烷的生产时间较长(4 天),且 HS 之后。在发酵批中,混合发酵液中硫的主要形式是硫化物(占总硫的 20-70%)。这些硫化物来自蛋白质,在甲烷产生高峰期,蛋白质可以被产甲烷菌和蛋白质利用菌缓慢分解为硫化物,硫酸盐可以在发酵的前两天由硫酸盐还原菌(SRB)转化为硫化物。在长期运行的连续进料 FWAD 系统中,由于蛋白质是食物垃圾中硫的主要存在形式,因此它将是硫化物/HS 的主要来源。

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