利用逐级提高进料浓度的方法启动完全混合反应器处理鸡粪

裴梦富, 强虹, 杨祎楠, 刘晓佩, 宋梓梅. 利用逐级提高进料浓度的方法启动完全混合反应器处理鸡粪[J]. 环境工程学报, 2018, 12(6): 1825-1832. doi: 10.12030/j.cjee.201711113
引用本文: 裴梦富, 强虹, 杨祎楠, 刘晓佩, 宋梓梅. 利用逐级提高进料浓度的方法启动完全混合反应器处理鸡粪[J]. 环境工程学报, 2018, 12(6): 1825-1832. doi: 10.12030/j.cjee.201711113
PEI Mengfu, QIANG Hong, YANG Yinan, LIU Xiaopei, SONG Zimei. Start-up of continuous stirring tank reactor treating chicken manure by stepwise increasing influent solid concentration[J]. Chinese Journal of Environmental Engineering, 2018, 12(6): 1825-1832. doi: 10.12030/j.cjee.201711113
Citation: PEI Mengfu, QIANG Hong, YANG Yinan, LIU Xiaopei, SONG Zimei. Start-up of continuous stirring tank reactor treating chicken manure by stepwise increasing influent solid concentration[J]. Chinese Journal of Environmental Engineering, 2018, 12(6): 1825-1832. doi: 10.12030/j.cjee.201711113

利用逐级提高进料浓度的方法启动完全混合反应器处理鸡粪

  • 基金项目:

    国家自然科学基金资助项目(51308460)

Start-up of continuous stirring tank reactor treating chicken manure by stepwise increasing influent solid concentration

  • Fund Project:
  • 摘要: 为了改进完全混合反应器(continuous stirring tank reactor, CSTR)厌氧消化处理鸡粪的启动效果,通过逐级提高进料鸡粪浓度的方法在CSTR中进行中温(36 °C)厌氧消化的启动实验,实验分为2个步骤:污泥适应性驯化和消化能力提升,即通过间歇添加2%浓度鸡粪的方法驯化活性污泥;利用逐级提高进料鸡粪浓度(2.1%、3.2%和5.2%)的方法提高污泥消化能力。结果表明:通过逐级提升进料鸡粪浓度的方法能够驯化出处理一定浓度鸡粪的活性污泥,当进料鸡粪浓度达到5. 2%时,CSTR进料有机负荷(organic loading rate, OLR)、总固体含量(total solid, TS)去除率和产沼气量分别达到1.5 g·(L·d)-1、60%和1 L·(L·d)-1,甲烷体积分数稳定在(65±3)%左右,总氨氮浓度最高达到1 200 mg·L-1,没有出现氨抑制的现象,污泥活性随进料鸡粪浓度提升而逐步得到驯化,从而成功启动反应器正常运行。为CSTR厌氧消化处理高氮基质启动提供了新的方法,具有重要的理论和实践意义。
  • 加载中
  • [1] 田宜水.中国规模化养殖场畜禽粪便资源沼气生产潜力评价[J]. 农业工程学报,2012,28(8):230-234
    [2] POSCHL M, WARD S, OWENDE P, Evaluation of energy efficiency of various biogas production and utilization pathways[J].Applied Energy,2010,87(11):3305-3321
    [3] 潘君廷,马俊怡,郜天磊,等.膨润土改善鸡粪厌氧消化产酸产甲烷特性[J]. 农业工程学报,2016,32(8):246-252 10.11975/j.issn.1002-6819.2016.08.035
    [4] ABOUELENIEN F, NAMBA Y,KOSSEVR M R, et al.Enhancement of methane production from co-digestion of chicken manure with agricultural wastes[J].Bioresource Technology,2014,159(6):80-87 10.1016/j.biortech.2014.02.050
    [5] 马俊怡,潘君廷,郜天磊,等.膨润土对鸡粪序批式厌氧消化特性的影响[J]. 环境科学研究,2016,29(3):442-448
    [6] CHEN S, CAO W, BANKS C J, et al.Biogas production from undiluted chicken manure and maize silage: A study of ammonia inhibition in high solids anaerobic digestion[J].Bioresource Technology,2016,218:1215-1223 10.1016/j.biortech.2016.07.082
    [7] WU S, NI P, LI J, et al.Integrated approach to sustain biogas production in anaerobic digestion of chicken manure under recycled utilization of liquid digestate:Dynamics of ammonium accumulation and mitigation control [J].Bioresource Technology,2016,205(1):172-178 10.1016/j.biortech.2016.01.021
    [8] 何秋阳,李润东,冯磊,等.CSTR反应器鸡粪厌氧消化中试启动研究[J].可再生能源,2012(4):89-92
    [9] 梅冰,彭绪亚,王璐,等.CSTR反应器厌氧消化餐厨垃圾启动过程的监控[J].中国给水排水,2013,29(11):18-21
    [10] 李荣平,李秀金,陈淑琳.用于牛粪液厌氧消化的推流式和完全混合式反应器性能研究[J].农业工程学报,2007,23(9):186-190
    [11] JANKE L, LEITE A F, NIKOLAUSAN M, et al.Comparison of start-up strategies and process performance during semi continuous anaerobic digestion of sugarcane filter cake co-digested with bagasse[J].Waste Management,2016,48:199-208 10.1016/j.wasman.2015.11.007
    [12] APHA.Standard Methods for the Examination of Water and Waste water[M].Washington D C: American Public Health Association (APHA),2005
    [13] HANSEN K H, ANGELIDAKI I, AHRING B K.Anaerobic digestion of swine manure: Inhibition by ammox[J].1998,32(1):5-12 10.1016/S0043-1354(97)00201-7
    [14] 孙晓.高含固率污泥厌氧消化系统的启动方案与试验[J]. 净水技术,2012,31(3):78-82
    [15] 马磊,王德汉,杨文杰,等.餐厨垃圾高温厌氧消化接种物的驯化研究[J]. 农业工程学报,2007,23(6):203-207
    [16] 张威, 赵庆良,胡凯.搅拌时间对污泥厌氧消化效能的影响研究[J]. 黑龙江大学自然科学学报,2011,28(3):383-387
    [17] NIU Q, KUBOTA K, QIAO W, et al.Effect of ammonia inhibition on microbial community dynamic and process functional resilience in mesophilic methane fermentation of chicken manure[J].Journal of Chemical Technology & Biotechnology,2015,90(12):65-85 10.1002/jctb.4527
    [18] NIU Q, WEI Q, HONG Q, et al.Mesophilic methane fermentation of chicken manure at a wide range of ammonia concentration:Stability,inhibition and recovery[J].Bioresource Technology,2013,137(11):358-367 10.1016/j.biortech.2013.03.080
    [19] MICHAUD S,BERNET N,BUFFIERE P.Methane yield as a monitoring parameter for the start-up of anaerobic fixed film reactors[J].Water Research,2002,36(5):1385-1391 10.1016/S0043-1354(01)003 38-4
    [20] TONG Z, YANG Y, LIU L, et al.Improved biogas production from chicken manure anaerobic digestion using cereal residues as co-substrates [J].Energy & Fuels, 2014, 28(4):2490-2495 10.1021/ef500262m
    [21] CHEN Y, CHENG J J, CREAMER K S.Inhibition of anaerobic digestion process: A review[J].Bioresource Technology,2008,99(10):4044-4064 10.1016/j.biortech.2007.01.057
    [22] ZEEMAN G,WIEGANT W M,KOSTERTREFFERS M E, et al.The influence of the total-ammonia concentration on the thermophilic digestion of cow manure[J].Agricultural Wastes,1985,14(1):19-35 10.1016/S0141-4607(85)80014-7
    [23] HASHIMOTO A G.Ammonia inhibition of methanogenesis from cattle wastes[J].Agricultural Wastes,1986,17(4):241-261 10.1016/0141-4607(86)90133-2
    [24] DUAN N, DONG B, WU B, et al.High-solid anaerobic digestion of sewage sludge under mesophilic conditions:feasibility study[J].Bioresource Technology,2012,104:150-156 10.1016/j.biortech.2011. 10. 090
    [25] NIU Q, WEI Q, HONG Q, et al.Microbial community shifts and biogas conversion computation during steady,inhibited and recovered stages of thermophilic methane fermentation on chicken manure with a wide variation of ammonia[J].Bioresource Technology,2013,146(10):223-233 10.1016/j.biortech.2013.07.038
  • 加载中
计量
  • 文章访问数:  2578
  • HTML全文浏览数:  2255
  • PDF下载数:  342
  • 施引文献:  0
出版历程
  • 刊出日期:  2018-06-18

利用逐级提高进料浓度的方法启动完全混合反应器处理鸡粪

  • 1. 西北农林科技大学机械与电子工程学院,杨凌 712100
  • 2. 西北农林科技大学资源环境学院,杨凌 712100
基金项目:

国家自然科学基金资助项目(51308460)

摘要: 为了改进完全混合反应器(continuous stirring tank reactor, CSTR)厌氧消化处理鸡粪的启动效果,通过逐级提高进料鸡粪浓度的方法在CSTR中进行中温(36 °C)厌氧消化的启动实验,实验分为2个步骤:污泥适应性驯化和消化能力提升,即通过间歇添加2%浓度鸡粪的方法驯化活性污泥;利用逐级提高进料鸡粪浓度(2.1%、3.2%和5.2%)的方法提高污泥消化能力。结果表明:通过逐级提升进料鸡粪浓度的方法能够驯化出处理一定浓度鸡粪的活性污泥,当进料鸡粪浓度达到5. 2%时,CSTR进料有机负荷(organic loading rate, OLR)、总固体含量(total solid, TS)去除率和产沼气量分别达到1.5 g·(L·d)-1、60%和1 L·(L·d)-1,甲烷体积分数稳定在(65±3)%左右,总氨氮浓度最高达到1 200 mg·L-1,没有出现氨抑制的现象,污泥活性随进料鸡粪浓度提升而逐步得到驯化,从而成功启动反应器正常运行。为CSTR厌氧消化处理高氮基质启动提供了新的方法,具有重要的理论和实践意义。

English Abstract

参考文献 (25)

目录

/

返回文章
返回