腐熟蓝藻与厌氧污泥混合厌氧发酵特性

许丽娟, 朱光灿, 吕锡武, 赵晋伟. 腐熟蓝藻与厌氧污泥混合厌氧发酵特性[J]. 环境工程学报, 2013, 7(9): 3345-3350.
引用本文: 许丽娟, 朱光灿, 吕锡武, 赵晋伟. 腐熟蓝藻与厌氧污泥混合厌氧发酵特性[J]. 环境工程学报, 2013, 7(9): 3345-3350.
Xu Lijuan, Zhu Guangcan, Lü Xiwu, Zhao Jinwei. Biogas production through anaerobic digestion from the mixture of decomposed cyanobacteria and anaerobic sludge[J]. Chinese Journal of Environmental Engineering, 2013, 7(9): 3345-3350.
Citation: Xu Lijuan, Zhu Guangcan, Lü Xiwu, Zhao Jinwei. Biogas production through anaerobic digestion from the mixture of decomposed cyanobacteria and anaerobic sludge[J]. Chinese Journal of Environmental Engineering, 2013, 7(9): 3345-3350.

腐熟蓝藻与厌氧污泥混合厌氧发酵特性

  • 基金项目:

    国家"水体污染控制与治理"科技重大专项(2009ZX07101-011)

  • 中图分类号: X524

Biogas production through anaerobic digestion from the mixture of decomposed cyanobacteria and anaerobic sludge

  • Fund Project:
  • 摘要: 采用批次小试实验对不同腐熟程度的蓝藻进行厌氧发酵产沼气实验研究。结果表明,新鲜蓝藻在30~35℃时腐熟7 d后,可在35℃的厌氧温度下获得最高的产气速率和246 mL/g COD的产气量,产气潜力为354 mL/g (VS)。厌氧反应15 d后,累计产气量、COD和VFA浓度趋于稳定。淀粉酶和脱氢酶的活性在厌氧反应初期受到抑制,蛋白酶活性和辅酶F420浓度在厌氧系统中逐渐增加,分别在第6天达到27.66 μmol/(g VS·min)和第15天达到0.62 μmol/g(VS)。15~18 d是腐熟蓝藻适宜的中温厌氧发酵时间,少于以新鲜蓝藻为基质的厌氧消化时间。蓝藻腐熟过程促进了厌氧反应,腐熟7 d的蓝藻厌氧系统具有更高的微生物活性和产甲烷能力。
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    [4] Xu Rui,Gao Tianrong. Biochemical methane potential of blue-green algae in biogas fermentation progress. Journal of Yunnan Normal University,2007, 27(5):35-38
    [5] 董诗旭,董锦艳,宋洪川,等. 滇池蓝藻发酵产沼气的研究.可再生能源,2006,126(2):16-18 Dong Shixu,Dong Jinyan,Song Hongchuan. Study on the biogas fermentation with blue algae from Dianchi Lake. Renewable Energy,2006,126(2):16-18(in Chinese)
    [6] Yen H. W.,Brune D. E.Anaerobic co-digestion of algal sludge and waste paper to produce methane.Bioresource Technology,2007,98:130-134
    [7] 骆文忠.蓝藻在秋莴苣上的应用试验. 上海蔬菜,2008,(5):105 Luo Wenzhong. Application test of cyanobacteria on lettuce. Shanghai Vegetables,2008,(5):105(in Chinese)
    [8] 吴忠明,言建良,邹晴中,等.腐熟蓝藻在青菜上应用效果初探.上海农业科技,2007(1):87-88 Wu Zhongming,Yan Jianliang,Zhou Qingzhong,et al. Application of decomposed cyanobacteria on the effect of vegetable. Shanghai Agricultural Science and Technology,2007(1):87-88(in Chinese)
    [9] Bernfeld P. Amylase α and β. Methods in Enzymology,1955,1:149-151
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    [11] 吴唯民,胡纪萃,顾夏声. 厌氧污泥中的辅酶F420及其紫外-可见光分光光度法测定.中国环境科学,1986,6(1): 65-69 Wu Weimin,Hu Jicui,Gu Xiasheng. Coenzyme F420 in the anaerobic sludge and UV-visible spectrophotometric determination. China Environmental Science,1986,6(1): 65-69(in Chinese)
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出版历程
  • 收稿日期:  2012-08-10
  • 刊出日期:  2013-09-15

腐熟蓝藻与厌氧污泥混合厌氧发酵特性

  • 1.  东南大学能源与环境学院, 南京 210096
  • 2.  东南大学无锡太湖水环境工程研究中心, 无锡 214135
基金项目:

国家"水体污染控制与治理"科技重大专项(2009ZX07101-011)

摘要: 采用批次小试实验对不同腐熟程度的蓝藻进行厌氧发酵产沼气实验研究。结果表明,新鲜蓝藻在30~35℃时腐熟7 d后,可在35℃的厌氧温度下获得最高的产气速率和246 mL/g COD的产气量,产气潜力为354 mL/g (VS)。厌氧反应15 d后,累计产气量、COD和VFA浓度趋于稳定。淀粉酶和脱氢酶的活性在厌氧反应初期受到抑制,蛋白酶活性和辅酶F420浓度在厌氧系统中逐渐增加,分别在第6天达到27.66 μmol/(g VS·min)和第15天达到0.62 μmol/g(VS)。15~18 d是腐熟蓝藻适宜的中温厌氧发酵时间,少于以新鲜蓝藻为基质的厌氧消化时间。蓝藻腐熟过程促进了厌氧反应,腐熟7 d的蓝藻厌氧系统具有更高的微生物活性和产甲烷能力。

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