CAILu,CHENJun,FENGHao.Discussion on Key Design Parameter of Municipal Sludge Aerobic Fermentation Project: Fermentation Cycle[J].China Water & Wastewater,2022,38(18):72-77.
城市污泥好氧发酵工程关键设计参数发酵周期探讨
- Title:
- Discussion on Key Design Parameter of Municipal Sludge Aerobic Fermentation Project: Fermentation Cycle
- Keywords:
- sludge; aerobic fermentation; composting; drying; fermentation cycle; maturity
- 摘要:
- 发酵周期是决定城市污泥好氧发酵工程能否达到预期运行效果的关键设计参数,也是影响工程占地面积和工程造价的重要参数。从脱水减量化、高温无害化、稳定腐熟化等角度,结合发酵产物用途、标准要求和工程实践,探讨适宜的好氧发酵周期,为工程设计提供借鉴。研究表明,至少15 d的主发酵周期才能达到脱水减量化和无害化部分指标要求。若产物用于焚烧,主发酵周期可设为15 d;若用于土地改良,主发酵周期至少设为20 d;若进行农林地利用,建议主发酵后接续后腐熟,全周期至少设为30 d。因此,在工程实践中,主发酵周期至少设为15 d,后腐熟时间可根据产物用途设为5~15 d或更长。
- Abstract:
- Fermentation cycle is a key design parameter that determines whether the municipal sludge aerobic fermentation project can achieve the expected performance, and also an important parameter that affects the project footprint area and construction investment. From the aspects of dehydration reduction, microbial inactivation and maturity, the suitable aerobic fermentation cycle was discussed based on the product applications, standard requirements and engineering practices, which aimed to provide reference for engineering design. The main fermentation cycle to meet part of the dehydration reduction and microbial inactivation index requirements should be at least 15 days. If the product was used for incineration, the main fermentation cycle could be set to 15 days, and at least 20 days for soil conditioner. If the product was used as fertilizer in farmland or forestland, it was recommended that the whole cycle of main fermentation and subsequent maturity should be at least 30 days. In engineering practice, the main fermentation cycle should be at least 15 days, and the maturity cycle could be set to 5-15 days or longer depending on the use of the product.
相似文献/References:
[1]刘常青,陈琬,曾艺芳,等.SARD与CSTR反应器半连续发酵产氢能力对比[J].中国给水排水,2018,34(21):7.
LIU Chang qing,CHEN Wan,ZENG Yi fang,et al.Hydrogen Production Capacity of Semi continuous Fermentation of SARD and CSTR Bio hydrogen Production Reactor[J].China Water & Wastewater,2018,34(18):7.
[2]颜莹莹,梁远,沙雪华,等.新冠肺炎疫情下关于减少污泥中病原体的思考[J].中国给水排水,2020,36(6):22.
[3]郭波,田瑜,范晨,等.绿色纳米铁/H2O2联用两性脱水剂调理污泥研究[J].中国给水排水,2020,36(13):62.
GUO Bo,TIAN Yu,FAN Chen,et al. Sludge Conditioning by Green Iron Nanoparticles/H2O2 Combined with Amphoteric Dewatering Agent [J].China Water & Wastewater,2020,36(18):62.
[4]许劲,范准,吕秋颖,等.山地城市污泥水热炭化产物特性研究[J].中国给水排水,2020,36(21):21.
XU Jin,FAN Zhun,L Qiu-ying,et al.Characteristics of Hydrothermal Carbonization Products of Municipal Sludge in Mountainous Cities[J].China Water & Wastewater,2020,36(18):21.
[5]李金河,张波涛,刘宝玉,等.污泥中温厌氧消化最佳温度及改善机理分析[J].中国给水排水,2021,37(3):9.
LI Jin-he,ZHANG Bo-tao,LIU Bao-yu,et al.Optimal Reaction Temperature in Mesophilic Anaerobic Digestion of Waste Activated Sludge and Its Promotion Mechanism[J].China Water & Wastewater,2021,37(18):9.
[6]王丽花,吕国钧,王飞,等.污泥干化焚烧系统的节能降耗研究[J].中国给水排水,2021,37(4):29.
WANG Li-hua,Lü Guo-jun,WANG Fei,et al.Research on Energy Saving and Consumption Reduction of Sludge Drying and Incineration System[J].China Water & Wastewater,2021,37(18):29.
[7]纪莎莎,黄瑾.污泥焚烧工程中的磷形态分布与磷迁移研究[J].中国给水排水,2021,37(5):26.
JI Sha-sha,HUANG Jin.Phosphorus Forms Distribution and Migration in Sludge Incineration Project[J].China Water & Wastewater,2021,37(18):26.
[8]马彩霞,刘蕾,李碧清,等.强化化学淋滤对污泥重金属溶出及磷释放的影响[J].中国给水排水,2021,37(5):66.
MA Cai-xia,LIU Lei,LI Bi-qing,et al.Effect of Enhanced Chemical Leaching on Heavy Metal Dissolution and Phosphorus Release from Sludge[J].China Water & Wastewater,2021,37(18):66.
[9]李伟,常菁,王佳伟,等.热水解高级厌氧消化系统的污泥消毒、减量与能量回收[J].中国给水排水,2021,37(16):19.
LI Wei,CHANG Jing,WANG Jia-wei,et al.Sludge Disinfection, Reduction and Energy Recovery by Anaerobic Digestion with Thermal Hydrolysis Pretreatment[J].China Water & Wastewater,2021,37(18):19.
[10]胡佩佩,侯锋,范莹,等.深度脱水污泥好氧发酵工艺研究[J].中国给水排水,2021,37(17):74.
HU Pei-pei,HOU Feng,FAN Ying,et al.Aerobic Fermentation Process of Deep Dewatering Sludge[J].China Water & Wastewater,2021,37(18):74.