The influence of aeration rate on intermittent forced-aeration composting of biogas residue
QIU Shan1, ZHAO Long-bin1, MA Fang1,2, SUN Ying3
1. School of Municipal and Environmental Engineering, Harbin Institute of Technology, Harbin 150090, China;
2. State Key Laboratory of Urban water Resource and Environment, Harbin Institute of Technology, Harbin 150090, China;
3. Environmental management college of China, Qinhuangdao 066102, China
An experiment was conducted to study the effect of aeration rates of 0.2, 0.5, 0.8L/(min·kg OM) on intermittent forced-aeration composting of biogas residue. Characteristics of physics, chemistry and maturity were determined during the composting. The results were manifested that the higher aeration rate of 0.8 L/(min·kg OM) did not maintain a longer thermophilic phase. The decomposition rate of OM were 28.2%, 32.9% and 30.5%, respectively. The aeration rate had little influence on the final pH and EC, all composts had reached acceptable optimum values and EC had not exceeded 4mS/cm. The final ammonia nitrogen content in pile of aeration rates of 0.2L/(min·kg OM) did not meet the limit value of 400 mg/kg, and the nitrate nitrogen was 2545, 3146 and 2735 mg/kg, respectively. The final C/N was 16.5, 14.1 and 15.6, and the final germination index (GI) was 92.2%, 96.6% and 82.7%, respectively. The pile of middle aeration rates of 0.5L/(min·kg OM) had the highest humification because E465/E665 (E4/E6) of it reduced the largest range. Overall, aeration rates of 0.5L/(min·kg OM) can be chosen for composting.
邱珊, 赵龙彬, 马放, 孙颖. 通风速率对厌氧残余物沼渣堆肥的影响[J]. 中国环境科学, 2016, 36(8): 2402-2408.
QIU Shan, ZHAO Long-bin, MA Fang, SUN Ying. The influence of aeration rate on intermittent forced-aeration composting of biogas residue. CHINA ENVIRONMENTAL SCIENCECE, 2016, 36(8): 2402-2408.
Govasmark E,Stäb J, Holen B., et al.Chemical and microbiological hazards associated with recycling of anaerobic digested residue intended for agricultural use[J]. Waste Management, 2011,31(12):2577-2583.
Do T, Scherer H. Compost and biogas residues as basic materials for potting substrates[J]. Plant Soil Environ, 2012,58:459-464.
[6]
Svensson K, Odlare M, Pell M. The fertilizing effect of compost and biogas residues from source separated household waste[J]. The Journal of Agricultural Science, 2004,142(4):461-467.
Do T C V, Scherer H W. Compost and biogas residues as basic materials for potting substrates[J]. Plant Soil and Environment, 2012,58(10):459-464.
[9]
Kuter G, Hoitink H, Rossman L. Effects of aeration and temperature on composting of municipal sludge in a full-scale vessel system[J]. Journal (Water Pollution Control Federation), 1985:309-315.
[10]
Hu Z, Liu Y, Chen G, et al. Characterization of organic matter degradation during composting of manure-straw mixtures spiked with tetracyclines[J]. Bioresource Technology, 2011,102(15): 7329-7334.
[11]
Gao M, Li B, Yu A, et al. The effect of aeration rate on forced-aeration composting of chicken manure and sawdust[J]. Bioresource Technology, 2010,101(6):1899-1903.
Guo R., Li G., Jiang T, et al. Effect of aeration rate, C/N ratio and moisture content on the stability and maturity of compost[J]. Bioresource Technology, 2012,112:171-178.
[14]
Chen Z, Zhang S, Wen Q, et al. Effect of aeration rate on composting of penicillin mycelial dreg[J]. Journal of Environmental Sciences, 2015,37:172-178.
Wong J, Li S, Wong M. Coal fly ash as a composting material for sewage sludge: effects on microbial activities[J]. Environmental technology, 1995,16(6):527-537.
[22]
Wong J, Mak K., Chan N, et al. Co-composting of soybean residues and leaves in Hong Kong[J]. Bioresource Technology, 2001,76(2):99-106.
[23]
Lin C. A negative-pressure aeration system for composting food wastes[J]. Bioresource Technology, 2008,99(16):7651-7656.
[24]
Fang M., Wong J, Ma K., et al. Co-composting of sewage sludge and coal fly ash: nutrient transformations[J]. Bioresource Technology, 1999,67(1):19-24.
[25]
Garcia C, Hernandez T, Costa F, et al. Evaluation of the maturity of municipal waste compost using simple chemical parameters[J]. Communications in Soil Science & Plant Analysis, 1992, 23(13/14):1501-1512.
[26]
Mahimairaja S, Bolan N, Hedley M, et al. Losses and transformation of nitrogen during composting of poultry manure with different amendments: an incubation experiment[J]. Bioresource Technology, 1994,47(3):265-273.
[27]
Cáceres R, Flotats X, Marfà O. Changes in the chemical and physicochemical properties of the solid fraction of cattle slurry during composting using different aeration strategies[J]. Waste Management, 2006,26(10):1081-1091.
[28]
Morel J, Colin F, Germon J, et al. Methods for the evaluation of the maturity of municipal refuse compost[J]. Composting of agricultural and other wastes/edited by JKR Gasser, 1985:
Korshin G V., Li C.-W, Benjamin M. M. Monitoring the properties of natural organic matter through UV spectroscopy: a consistent theory[J]. Water Research, 1997,31(7):1787-1795.
[31]
Liu W, Zhang Z, Yang X., et al. Effects of UV irradiation and UV/chlorine co-exposure on natural organic matter in water[J]. Science of theTotal Environment, 2012,414:576-584.
[32]
Wong M. Phytotoxicity of refuse compost during the process of maturation[J]. Environmental Pollution Series A, Ecological and Biological, 1985,37(2):159-174.