畜禽粪便热堆肥过程中微生物群落生态演替的研究

X. Zhen, T. Dong, Jia Liu, Miao Luo, Shun-Jie Li
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摘要

摘要甘肃省畜禽工业固体废弃物的处理和资源化利用存在着各种环境问题。因此,本研究选择甘肃省兰州市兰州理工大学附近农场的牛粪、猪粪和鸡粪作为堆肥原料,以10%玉米秸秆为膨松剂进行好氧静态堆肥。研究了畜禽粪便堆肥过程中细菌、真菌和放线菌的群落演替及其微生物降解机制。结果表明,在畜禽粪便堆肥过程中,上述微生物数量均与堆肥堆温度呈正相关。在堆肥初期,微生物数量随着温度的升高而增加,在最高温度时达到峰值,之后随着温度的降低而减少。堆肥结束时,牛、猪、和鸡粪堆肥桩,细菌的数量分别为(3.1±1.0)·109 CFU·克−1 d.w。,(4.4±1.0)·109 CFU·克−1 d.w.和(6.7±1.8)·109 CFU·克−1 d.w。,分别的真菌(8.6±1.2)·104 CFU·g−1 d.w。(7.2±1.6)·104 CFU·克−1 d.w.和(8.0±2.8)·104 CFU·克−1 d.w。,分别,而放线菌106 CFU(8.8±2.2)··g−1 d.w。(9.5±2.1)·106 CFU·克−1 d.w.和(6.32±0.98)·106 CFU·克−1 d.w。,分别。
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Study on the Ecological Succession of Microbial Communities During Hot Composting of Livestock Manure
Abstract There have been various environmental issues in the treatment and resource utilisation of solid waste of livestock and poultry industry in Gansu Province. Thus, in this study, manure of cattle, pig, and chicken from farms near the Lanzhou University of Technology in Lanzhou City, Gansu Province were selected as raw materials for composting using 10 % corn stalk as a leavening agent for aerobic static composting. This study focused on bacterial, fungal, and actinomycetes community succession during livestock manure composting and the underlying microbial degradation mechanism. The results demonstrated that during livestock manure composting, the number of the above-mentioned types of microbes was all positively correlated with the temperature of the compost piles. In the initial stage of composting, the number of microbes increased as the temperature increased, and reached the peaks at the highest temperature, after which, their numbers decreased with the decrease in temperature. At the end of composting, in the cattle, pig, and chicken manure compost piles, the number of bacteria were respectively (3.1 ±1.0) · 109 CFU·g−1 d.w., (4.4 ±1.0) · 109 CFU·g−1 d.w. and (6.7 ±1.8) · 109 CFU·g−1 d.w., respectively, those of fungi were (8.6 ±1.2) · 104 CFU·g−1 d.w., (7.2 ±1.6) · 104 CFU·g−1 d.w. and (8.0 ±2.8) · 104 CFU·g−1 d.w., respectively, while those of actinomycetes were (8.8 ±2.2) · 106 CFU·g−1 d.w., (9.5 ±2.1) · 106 CFU·g−1 d.w. and (6.32 ±0.98) · 106 CFU·g−1 d.w., respectively.
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