S. Zhaparova, Z. Bayazitova, A. Kurmanbayeva, A. Kakabayev, Z. Bekpergenova
{"title":"Thermophilic fermentation of household food waste","authors":"S. Zhaparova, Z. Bayazitova, A. Kurmanbayeva, A. Kakabayev, Z. Bekpergenova","doi":"10.31489/2022bmg3/56-66","DOIUrl":null,"url":null,"abstract":"In mesophilic conditions, anaerobic digestion is the most common in the world. However, thermophilic fermentation has several advantages due to the growth rate of microorganisms and the reactions they produce, as well as the degradation of deep organic matter due to an increase in the solubility of organic compounds. Increasing the temperature of the process makes it possible to neutralize the remnants of pathogenic organisms (viruses, bacteria, helminth eggs), which are necessary for the further use of fermented biomass as a biofertilizer. An effective inoculum is selected for the process of anaerobic co-fermentation of food waste and excess activated sludge. The optimal ratio of inoculate and substrate is determined to start the process of anaerobic digestion. Experiments with flasks and laboratory biogas reactors demonstrate that fermentation of OSV with food waste can significantly increase the rate and consumption of biogas. The optimal ratio of OSV and food waste in a mixture of coenzymes is 50/50, depending on the total content of organic substances in the mixture. The maximum rate of methanogenesis is observed in mixtures of I/C 70/30 and I/C 55/45 (after 18 days) and 156 ml of CH4 and 178 ml of CH4, respectively. This indicates the stability of the anaerobic process. It is shown that after pretreatment and activation of the landfill, the organic part of solid household waste, food waste and wastewater can be used to start the process of anaerobic digestion in anaerobic reactors.","PeriodicalId":9377,"journal":{"name":"Bulletin of the Karaganda University. “Biology, medicine, geography Series”","volume":"136 1","pages":""},"PeriodicalIF":0.0000,"publicationDate":"2022-09-30","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Bulletin of the Karaganda University. “Biology, medicine, geography Series”","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.31489/2022bmg3/56-66","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 0
Abstract
In mesophilic conditions, anaerobic digestion is the most common in the world. However, thermophilic fermentation has several advantages due to the growth rate of microorganisms and the reactions they produce, as well as the degradation of deep organic matter due to an increase in the solubility of organic compounds. Increasing the temperature of the process makes it possible to neutralize the remnants of pathogenic organisms (viruses, bacteria, helminth eggs), which are necessary for the further use of fermented biomass as a biofertilizer. An effective inoculum is selected for the process of anaerobic co-fermentation of food waste and excess activated sludge. The optimal ratio of inoculate and substrate is determined to start the process of anaerobic digestion. Experiments with flasks and laboratory biogas reactors demonstrate that fermentation of OSV with food waste can significantly increase the rate and consumption of biogas. The optimal ratio of OSV and food waste in a mixture of coenzymes is 50/50, depending on the total content of organic substances in the mixture. The maximum rate of methanogenesis is observed in mixtures of I/C 70/30 and I/C 55/45 (after 18 days) and 156 ml of CH4 and 178 ml of CH4, respectively. This indicates the stability of the anaerobic process. It is shown that after pretreatment and activation of the landfill, the organic part of solid household waste, food waste and wastewater can be used to start the process of anaerobic digestion in anaerobic reactors.
在中温环境中,厌氧消化是世界上最常见的。然而,由于微生物的生长速度和它们产生的反应,以及由于有机化合物的溶解度增加而对深层有机物的降解,嗜热发酵具有几个优点。提高该过程的温度可以中和致病生物(病毒、细菌、蠕虫卵)的残余,这是进一步利用发酵生物质作为生物肥料所必需的。选择了一种有效的接种菌,对食物垃圾和剩余活性污泥进行厌氧共发酵。确定接种物与底物的最佳配比,启动厌氧消化过程。用烧瓶和实验室沼气反应器进行的实验表明,用食物垃圾发酵OSV可以显著提高沼气的利用率和消耗量。根据混合物中有机物的总含量,辅酶混合物中OSV和食物垃圾的最佳比例为50/50。在I/C 70/30和I/C 55/45(18天后)和156 ml CH4和178 ml CH4的混合条件下,产甲烷率最高。这表明厌氧过程的稳定性。结果表明,垃圾填埋场经过预处理和活化后,可以利用生活垃圾、食物垃圾和废水中的有机部分在厌氧反应器中启动厌氧消化过程。