暗发酵过程中接种源和预处理对生物制氢的影响

Marlena Domińska, K. Paździor, R. Ślężak, Stanisław Ledakowicz
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摘要

通过暗发酵(DF)从食物垃圾(FW)中生产生物氢是一项很有商业前景的技术,因为它既是一种清洁燃料,也是一种可持续废物管理的合适手段。所述实验比较了使用两种不同来源的接种物后所获得的生物氢产量:罗兹市污水处理厂(WWTP)的消化污泥和乳制品工业废水(DIW)(非浓缩和双浓缩)厌氧处理污泥。此外,还测试了接种物预处理的不同温度(70、90 和 121°C)对 DF 中生物产氢的影响。该过程在 37°C 下分批进行。在 70°C 下对接种物进行预处理后,产氢量最高。此外,使用污水处理厂的污泥作为接种物(96 cm3 H2/g TVSFW)比使用去离子水厂的未浓缩污泥(85 cm 3 H 2/g TVSFW)能获得更多的氢。然而,在对乳制品工业污泥进行浓缩并同时平衡两种污泥的干物质后,两种污泥的产氢潜力相当(污水处理厂污泥为 96 立方厘米 H2/克 TVSFW,工业污水处理厂污泥为 93 立方厘米 H2/克 TVSFW)。制氢动力学用修正的贡培兹方程来描述,该方程与实验数据的拟合度很高(确定系数 R2 在 0.909 和 0.999 之间)。
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The influence of inoculum source and pretreatment on the biohydrogen production in the dark fermentation process
The production of biohydrogen from food waste (FW) by dark fermentation (DF) is a promising technology for commercialisation, as it is both a clean fuel and a suitable means of sustainable waste management. The described experiments compared the biohydrogen production yields obtained after the use of inoculum from two different sources: digested sludge from the wastewater treatment plant (WWTP) in Lodz and sludge from the anaerobic treatment of dairy industry wastewater (DIW) (unconcentrated and double-concentrated). In addition, the effect of different temperatures (70, 90 and 121°C) of inoculum pretreatment on the biohydrogen production in DF was tested. The process was carried out batchwise at 37°C. The highest yield of hydrogen production was obtained after the inoculum pretreatment at 70°C. In addition, a higher amount of hydrogen could be obtained by using sludge from the WWTP as the inoculum (96 cm3 H2/gTVSFW) than unthickened sludge from the DIW (85 cm 3 H 2/g TVSFW). However, after thickening the sludge from the dairy industry, and at the same time balancing the dry matter of both sludges, the hydrogen production potential was comparable for bothsludges (for the WWTP sludge – 96 and for the DIW sludge – 93 cm 3 H 2/g TVSFW). The kinetics of hydrogen production was described by modified Gompertz equation, which showed a good fit (determination coefficient R2 between 0.909 and 0.999) to the experimental data.
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