Please wait a minute...
浙江大学学报(工学版)  2017, Vol. 51 Issue (10): 2055-2060    DOI: 10.3785/j.issn.1008-973X.2017.10.021
环境工程、化学工程     
基于微藻培养的养猪废水氨氮吹脱预处理
罗龙皂, 邵瑜, 田光明
浙江大学 环境与资源学院, 浙江 杭州 310058
Ammonia stripping of piggery wastewater for microalgae culturing
LUO Long-zao, SHAO Yu, TIAN Guang-ming
College of Environmental and Resource Sciences, Zhejiang University, Hangzhou 310058, China
 全文: PDF(1066 KB)   HTML
摘要:

针对养猪废水中氨氮质量浓度过高,会限制微藻生长这一问题,研究3种能源微藻对不同氨氮质量浓度养猪废水的适应性,探讨利用吹脱法对养猪废水中氨氮进行预处理的可行性,考察pH、曝气量和氨氮初始质量浓度对氨氮吹脱效果的影响.结果表明,当废水中氨氮质量浓度≤ 130 mg/L时,小球藻1068和近具刺链带藻CHX1能够很好地生长,葡萄藻765在氨氮质量浓度为90 mg/L的废水中生长良好.经吹脱预处理的养猪废水可以满足小球藻、葡萄藻和近具刺链带藻3种微藻生长,且吹脱去除氨氮过程符合一级动力学方程.提高pH和曝气量有助于提高氨氮吹脱去除效率.在综合考虑经济投入和氨氮去除效果2个因素后,确定满足小球藻1068和近具刺链带藻CHX1生长的养猪废水吹脱预处理工艺参数如下:曝气量为1.5 L/min、曝气时间为36 h;满足葡萄藻765生长的养猪废水吹脱预处理工艺参数为:曝气量>1.5 L/min、曝气时间为42 h,或曝气量为1.5 L/min、曝气时间>42 h.

Abstract:

The ammonium mass concentration is very high in piggery wastewater, which may inhibit the growth of microalgae. The inhibitory ammonia levels for three microalgae strains were analyzed in order to solve the problem. Then the ammonia stripping method was used to decrease the ammonia mass concentration in piggery wastewater. The effects of the pH, aeration rate, and the initial ammonia mass concentration of wastewater on the removal efficiency were analyzed. Results showed that the inhibitory ammonia level for Chlorella vulgaris 1068 and Desmodesmus sp.CHX1 was both 130 mg/L, and 90 mg/L for Botryococcus braunii 765. Microalgae can grow well in the wastewater pretreated by stripping, and the process of stripping conforms to the first-order kinetic equation. Increasing the pH, aeration or the initial ammonium mass concentration was helpful to increase the removal efficiency of ammonia nitrogen. Appropriate operating parameters were obtained by considering the economic inputs and ammonia nitrogen removal efficiency. The wastewater should be stripped at an aeration rate of 1.5 L/min for 36 h, so that Chlorella vulgaris 1068 and Desmodesmus sp.CHX1 can grow well. The wastewater should be stripped at an aeration rate of more than 1.5 L/min for 42 h, or at an aeration rate of 1.5 L/min for more than 42 h in order to meet the growth condition of Botryococcus braunii 765.

收稿日期: 2016-07-24 出版日期: 2017-09-27
CLC:  X703  
基金资助:

水体污染控制与治理科技重大专项资助项目(2014ZX07101-012).

通讯作者: 田光明,男,教授.ORCID:0000-0001-8109-7227.     E-mail: gmtian@zju.edu.cn
作者简介: 罗龙皂(1985-),男,博士生,从事废物资源化的研究.ORCID:0000-0002-1151-3587.E-mail:luolongzao@sina.com
服务  
把本文推荐给朋友
加入引用管理器
E-mail Alert
作者相关文章  

引用本文:

罗龙皂, 邵瑜, 田光明. 基于微藻培养的养猪废水氨氮吹脱预处理[J]. 浙江大学学报(工学版), 2017, 51(10): 2055-2060.

LUO Long-zao, SHAO Yu, TIAN Guang-ming. Ammonia stripping of piggery wastewater for microalgae culturing. JOURNAL OF ZHEJIANG UNIVERSITY (ENGINEERING SCIENCE), 2017, 51(10): 2055-2060.

链接本文:

http://www.zjujournals.com/eng/CN/10.3785/j.issn.1008-973X.2017.10.021        http://www.zjujournals.com/eng/CN/Y2017/V51/I10/2055

[1] PARK J, JIN H F, LIM B R, et al. Ammonia removal from anaerobic digestion effluent of livestock wasteusing green alga Scenedesmus sp[J]. Bioresource Technology, 2010, 101(22):8649-8657.
[2] TAM N F, WONG Y S. Effect of ammonia concentrations on growth of Chlorella vulgaris and nitrogenremoval from media[J]. Bioresource Technology, 1996, 57(1):45-50.
[3] ZHANG L, LEE Y W, JAHNG D. Ammonia stripping for enhanced biomethanization of piggery wastewater[J]. Journal of Hazardous Materials, 2012, 199-200(2):36-42.
[4] LIMOLI A, LANGONE M, ANDREOTTOLA G. Ammonia removal from raw manure digestate by means of a turbulent mixing stripping process[J]. Journal of Environmental Management, 2016, 176:1-10.
[5] HUANG W W, ZHAO Z W, YUAN T, et al. Effective ammonia recovery from swine excreta through dry anaerobic digestion followed by ammonia stripping at high total solids content[J]. Biomass and Bioenergy, 2016, 90:139-147.
[6] ZHANG L, LEE Y W, JAHNG D. Ammonia stripping for enhanced biomethanization of piggery wastewater[J]. Journal of Hazardous Materials, 2012, 199-200(2):36-42.
[7] SONG Y H, QIU G L, YUAN P, et al. Nutrients removal and recovery from anaerobically digested swine wastewater by struvite crystallization without chemical additions[J]. Journal of Hazardous Materials, 2011, 190(1-3):140-149.
[8] HUANG X, LIU C X, GAO C F, et al. Comparison of nutrient removal and bacterial communities between natural zeolite-based and volcanic rock-based vertical flow constructed wetlands treating piggery wastewater[J]. Desalination and Water Treatment, 2013, 51(22-24):4379-4389.
[9] WAKI M, TOKUTOMI T, YOKOYAMA H, et al. Nitrogen removal from animal waste treatment water by anammox enrichment[J]. Bioresource Technology, 2007, 98(14):2775-2780.
[10] OZTURK I, ALTINBAS M, KOYUNCU I, et al. Advanced physico-chemical treatment experiences on young municipal landfill leachates[J]. Waste Management, 2003, 23(5):441-446.
[11] QUAN X J, WANG F P, ZHAO Q H, et al. Air stripping of ammonia in a water-sparged aerocyclone reactor[J]. Journal of Hazardous Materials, 2009,170(2/3):983-988.
[12] 熊鸿斌,谷良平,张正.UASB-FEO-氨吹脱-CASS工艺在垃圾渗滤液处理中的应用[J].环境工程学报,2010,4(1):39-43. XIONG Hong-bin, GU Liang-ping, ZHANG Zheng. Application of UASB-FEO-ammonia stripping-CASS process in treatment of landfill leachate[J]. Chinese Journal of Environmental Engineering, 2010, 4(1):39-43.
[13] BONMATI A, FLOTATS X. Air stripping of ammonia from pig slurry:characterization and feasibility as a pre-or post-treatment to mesophilic anaerobic digestion[J]. Waste Management, 2003, 23(3):261-272.
[14] CHENG H X, TIAN G M. Identification of a newlyisolated microalga from a local pond and evaluation of its growth and nutrients removal potential in swine breeding effluent[J]. Desalination and Water Treatment, 2013, 51(13-15):2768-2775.
[15] CHENG H X, TIAN G M, LIU J Z. Enhancement of biomass productivity and nutrients removal from pretreated piggery wastewater by mixotrophic cultivation of Desmodesmus sp. CHX1[J]. Desalination and Water Treatment, 2013, 51(37-39):7004-7011.
[16] 黄美玲,何庆,黄建荣,等.小球藻生物量的快速测定技术研究[J].河北渔业,2010, 196(4):1-3. HUANG Mei-ling, HE Qing, HUANG Jian-rong, et al. A rapid determination of chlorella biomass[J]. Hebei Fisheries, 2010, 196(4):1-3.
[17] METZGER P, LARGEAU C. Botryococcus braunii:a rich source for hydrocarbons and related ether lipids[J]. Applied Microbiology and Biotechnology, 2005, 66(5):486-496.
[18] GUŠTIN S, MARINŠEK-LOGAR R. Effect of pH, temperature and air flow rate on the continuous ammonia stripping of the anaerobic digestion effluent[J]. Process Safety and Environmental Protection, 2011,89(1):61-66.
[19] 彭人勇,陈康康,李艳琳.超声吹脱去除氨氮的机理和动力学研究[J].环境工程学报,2010,4(12):2811-2814. PENG Ren-yong, CHEN Kang-kang, LI Yan-lin. Study on mechanism and kinetics of ammonia nitrogen removal by ultrasound stripping[J]. Chinese Journal of Environmental Engineering, 2010, 4(12):2811-2814.
[20] 刘丽.超声吹脱法去除养猪场废水中氨氮的试验研究[D].长沙:湖南农业大学, 2011. LIU Li. Study on removal of ammonia nitrogen in piggery wastewater by ultrasound stripping[D]. Changsha:Hunan Agricultural University, 2011.
[21] 姚玉英.化工原理(下册)[M].天津:天津科学技术出版社,2005.
[22] 孙华,申哲民.吹脱法去除氨氮的模型研究[J].环境科学与技术,2009,32(8):84-87. SUN Hua, SHEN Zhe-min. Model of air stripping of ammonia nitrogen[J]. Environmental Science and Technology, 2009, 32(8):84-87.
[23] LIAO P H, CHEN A, LO K V. Removal of nitrogen from swine manure wastewaters by ammonia stripping[J]. Bioresource Technology, 1995, 54(1):17-20.
[24] 隋倩雯. 氨吹脱与膜生物反应器组合工艺处理猪场厌氧消化液研究[D]. 北京:中国农业科学院, 2014. SUI Qian-wen. Combined of ammonia stripping and membrane bioreactor processes for anaerobically digested swine wastewater treatment[D]. Beijing:Chinese Academy of Agricultural Sciences, 2014.

[1] 杨海燕, 叶桂洪, 陈义华, 李翼. UV/NaClO高级氧化法降解再生水中磺胺甲恶唑[J]. 浙江大学学报(工学版), 2019, 53(1): 186-192.