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Process kinetics of inoculation composting of municipal solid waste

机译:城市生活垃圾接种堆肥的过程动力学

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A method was used to improve the composting efficiency by seeding with Inoculum A (a blend of Bacillus azotofimms, Bacillus megaterium and Bacillus mucilaginosus), Inoculum B (a blend of effective cellulolytic strains, i.e. Trichoderma koningii, Streptomyces cellulosae, and White-rot fungi), and Inoculum C (a mixture of Inoculum A and Inoculum B). There were four runs: the control run (not inoculated), Run A, Run B and Run C. During the runs, parameters such as temperature, O_2, CO_2 and H_2S emissions, and microbial concentration were investigated to study the efficiencies of inoculation composting. The maximum oxygen uptake rates in the control run, Run A, Run B and Run C were calculated as 0.22, 0.32; 0.28 and 0.34 mol/hkg while the corresponding total O_2 quantities accumulated were 511.18, 684.57, 659.74 and 778.47 g/h kg, respectively. In addition, odorous gases were highly reduced by inoculation. In order to understand the mechanisms of inoculation composting process, two stages kinetics equations were developed from the viewpoint of microbial kinetics. These equations showed that, in the first stage, microbial concentration was the main limiting factor of the degradation rate. The degradation rates in control, Run A, Run B and Run C were 10.5,13.61,13.08, and 15.671 g/kg h, respectively. In the second stage, the degradation rate was mainly affected by substrate concentration. Although the degradation rates were at almost the same level for both with and without inoculation, inoculation could reduce the half velocity coefficient K_m and in turn stabilize the composting products efficiently. Therefore, inoculation could improve the efficiency of the composting process.
机译:一种方法是通过接种接种物A(偶氮芽孢杆菌,巨大芽孢杆菌和粘液芽孢杆菌的混合物),接种物B(有效的纤维素分解菌株,即康氏木霉,链霉菌和白腐真菌的混合物)来提高堆肥效率。 )和接种物C(接种物A和接种物B的混合物)。共有四个运行:对照运行(未接种),运行A,运行B和运行C。在运行过程中,研究了温度,O_2,CO_2和H_2S排放量以及微生物浓度等参数,以研究接种堆肥的效率。在对照试验,试验A,试验B和试验C中的最大摄氧率经计算为0.22、0.32;在试验A,试验B和试验C中的最大摄氧率被计算为0.22、0.32。 0.28和0.34 mol / hkg,而相应的累积O_2总量分别为511.18、684.57、659.74和778.47 g / h kg。另外,通过接种可以大大减少恶臭气体。为了理解接种堆肥的机理,从微生物动力学的角度出发,建立了两个阶段的动力学方程。这些方程表明,在第一阶段,微生物浓度是降解速率的主要限制因素。对照,试验A,试验B和试验C的降解速率分别为10.5、13.61、13.08和15.671g / kg·h。在第二阶段,降解速率主要受底物浓度影响。尽管在有和没有接种的情况下降解速率都几乎处于同一水平,但是接种可以降低半速系数K_m,从而有效地稳定堆肥产品。因此,接种可以提高堆肥过程的效率。

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