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生物质好氧发酵热生产与回收利用研究进展
引用本文:于艳玲,曹永娜,贺巍,周宁,邹泽华,朱宇航,郭超,秦江.生物质好氧发酵热生产与回收利用研究进展[J].农业工程学报,2024,40(5):25-37.
作者姓名:于艳玲  曹永娜  贺巍  周宁  邹泽华  朱宇航  郭超  秦江
作者单位:哈尔滨工业大学化工与化学学院,哈尔滨 150001;哈工大郑州研究院,郑州 450003;黑龙江省建设投资集团有限公司碳中和研究院,哈尔滨 150001;哈尔滨工业大学能源科学与工程学院,哈尔滨 150001
基金项目:黑龙江省重点研发计划项目(SC2023ZXC010081);生物质资源化-哈工大郑州研究院成果产业化项目(ZRI-RZ-2022-013)
摘    要:好氧发酵是目前有机固体废弃物处理的一种有效手段。人们对于好氧发酵的研究主要集中在高效有机肥的获取上,但发酵过程产生的热能不容忽视。发酵热作为一种“零碳”能源,可代替传统化石能源应用于加温供暖、生物干化等领域,助力实现“碳达峰、碳中和”。为将生物质能高效转化为热能利用,人们对发酵热回收利用进行了研究,但是没有将热生产、热回收和热利用三个阶段进行系统联系,导致热回收工艺效率不高。该文主要阐述了好氧发酵产热原理,并从菌剂、原料理化性质和发酵工艺三个方面对发酵热生产的影响进行了探讨,总结了现有热回收利用系统,最后对生物质好氧发酵热生产与回收利用系统的发展方向进行展望,以期为生物质发酵热能利用提供支持。

关 键 词:生物质  好氧发酵  发酵产热  能量回收  废热利用
收稿时间:2023/11/4 0:00:00
修稿时间:2024/3/1 0:00:00

Research progress on biomass aerobic fermentation heat production and recycling
YU Yanling,CAO Yongn,HE Wei,ZHOU Ning,ZOU Zehu,ZHU Yuhang,GUO Chao,QIN Jiang.Research progress on biomass aerobic fermentation heat production and recycling[J].Transactions of the Chinese Society of Agricultural Engineering,2024,40(5):25-37.
Authors:YU Yanling  CAO Yongn  HE Wei  ZHOU Ning  ZOU Zehu  ZHU Yuhang  GUO Chao  QIN Jiang
Institution:School of Chemical Engineering and Chemistry, Harbin Institute of Technology, Harbin 150001, China;Zhengzhou Research Institute, Harbin Institute of Technology, Zhengzhou 450003, China;Institute for Carbon Neutrality, Heilongjiang Construction Group Co., Ltd., Harbin 150001, China; School of Energy Science and Engineering, Harbin Institute of Technology, Harbin 150001, China
Abstract:Energy demand is ever-increasing with the rapid development of society. Chemical energy has also resulted in a variety of atmospheric pollutants in traditional energy reserves, such as coal, oil, and natural gas. Biomass energy is a promising renewable energy to convert solar into chemical energy and then store it inside biomass. The available biomass resources in the world are as high as 170 billion tons at present. But there is a low utilization rate of biomass resources. The rest is burned or abandoned as waste, leading to the waste of resources, as well as serious air, water, and soil pollution. Among them, aerobic fermentation is an effective treatment for organic solid wastes. Both heat energy and organic fertilizer can be produced in a simple process without size restrictions. The fermentation heat energy can be recycled and then used to heat rural winter residential houses, vegetable greenhouses, farms, and processing plants. Organic fertilizers are used to replenish the soil fertility in the field. As a result, the heat-fertilizer combination production using aerobic fermentation is an environmentally friendly energy consumption suitable for rural areas. Although highly effective organic fertilizers have been the primary goal of aerobic fermentation, it is important to consider the heat produced during fermentation. Fermentation heat can serve as a kind of "zero-carbon" energy to replace the traditional fossil energy in heating and bio-drying, particularly for carbon peaking and carbon neutrality. Three stages are also included in the production of and recovering heat through aerobic fermentation: heat production, recovery, and usage. These stages interact with the heat acting as a medium. Some research has focused on the recycling of fermentation heat, but it is still lacking in heat recovery. This study aims to clarify the systematic relationship among the three stages of heat production, recovery, and utilization. The principle of heat production was described in biomass aerobic fermentation, the influencing factors of heat production, recovery, and utilization. The aerobic fermentation of biomass was attributed to the oxidative decomposition of organic matter under the microorganisms and the continuous release of heat. The completely oxidized substances were transformed into carbon dioxide and water, while the partially oxidized microorganisms were oxidized into humus. A systematic investigation was carried out to explore the effects of three factors on the heat production of biomass aerobic fermentation, including bacteriological agents, physicochemical properties of raw materials (particle size, pH, carbon to nitrogen ratio, and moisture), and fermentation (temperature and oxygen content). Furthermore, the current systems were summarized for heat recovery and utilization. Three types were categorized into direct utilization, sensible heat recovery, and exhaust gas heat recovery. Currently, fermentation heat recovery has been explored at lab- and pilot-scale, and commercial systems, where the heat recovery rate varied from 13.4% to 73.0%. The heat recovery rate of the fermentation system depended on the type and scale of fermentation feedstock, the type and mode of heat recovery, the fermentation, and the ambient temperature. In general, the larger the fermentation heat production was, the higher the heat recovery rate was. The average recovery rate for lab-scale systems was 1.90 MJ/h (1.16 MJ/kg DM), for pilot-scale systems 20.04 MJ/h (4.30 MJ/kg DM), for commercial-scale systems 204.91 MJ/h (7.08 MJ/kg DM). The direct utilization of fermentation heat is inexpensive and suitable for self-consumption on farms. The recovering internal heat from the fermentation system with the buried pipe is simple to operate and suitable for domestic use. The heat recovery system for exhaust heat recovery is highly efficient and suitable for commercial environments. Finally, the research direction was also given to provide support for the heat utilization of biomass aerobic fermentation.
Keywords:biomass  aerobic fermentation  fermentation heat production  energy recovery  waste heat utilization
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