磷酸铵镁结晶法去除和回收猪场废水中氮磷
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
废水中高含量的氮、磷是引起湖泊和封闭近岸海域富营养化现象的重要因素,经济而有效地控制氮磷污染已成为当前亟待解决的环保问题。磷酸铵镁(Magnesium Ammonium Phosphate, MAP)结晶法是脱氮除磷的主要工艺之一,从猪场废水中去除和回收氮、磷营养元素,对该废水的污染控制和资源化利用具有重要意义。本文以模拟和实际猪场废水为处理对象,系统研究了MAP结晶法的工艺条件,以脱氮除磷效果为考察指标确定了三种最佳工艺参数;分别对猪场原污水和厌氧消化后出水进行三种工艺的小试及放大试验,并对其运行的经济成本进行了初步分析。
     首先以模拟废水为处理对象,以MgCl2·6H2O和Na2HPO4·12H2O为沉淀剂进行了MAP结晶小试,通过正交设计确定了各影响因素的主次水平及显著性,其中废水中的P:N摩尔比影响最大。处理该模拟废水的最佳工艺条件为:P:N摩尔比=0.9-1.0、pH=9.5-10.5、Mg:N摩尔比=1.0-1.1,此时可获得较高的氨氮去除率同时保证尽可能低的余磷浓度。该工艺中废水搅拌速度、反应时间、沉淀时间等对氮、磷去除影响不太明显,因此从节约能源及缩短处理时间角度出发,可分别选为100-200r·min-1、10-15min、15-30min。
     其次以实际猪场废水为研究对象,针对猪场废水中NH4+-N、Mg2+、PO43--P三种离子比例不平衡的问题,设计了三种工艺,并对其工艺条件进行了系统研究。结果表明:pH值调节工艺中,废水的最佳pH值调节范围为9.0-10.0;通过连续曝气60 min可提升废水pH值至8.91,氨氮、磷、总氮去除率分别为16.8%、78.4%、21.4%;曝气尤其适用于富含CO2的猪场厌氧消化出水;补加镁源工艺,可有效提高磷去除率,当废水pH=9.0-10.0,Mg:P摩尔比=1.6时,磷去除率高达95.4%,该工艺较适用于富磷猪场废水;补加镁源和磷源工艺,保证尽可能低的余磷浓度的同时可获得较高的氨氮去除率,当pH=9.5、P:N摩尔比=1.0、Mg:N摩尔比=1.1时,氨氮去除率高达87.4%,余磷浓度小于10mg·L-1.
     最后以实际猪场废水为处理对象,进行了MAP结晶法的放大试验。试验结果表明:只调节pH值工艺、补加镁源工艺都具有较高的除磷能力,较适用于富磷的猪场废水。猪场原污水宜选用同时补加镁源和磷源工艺(Mg:N摩尔比=1.2,P:N摩尔比=1.0),单位氨氮处理费用最低,为7.85元·(kgNH4+-N)-1,此时处理1t原污水的费用为4.52元;猪场废水经厌氧消化后的出水也宜选用同时补加镁源和磷源工艺(Mg:N摩尔比=1.1,P:N摩尔比=0.9),单位氨氮处理费用为4.08元·(kgNH4+-N)-1,处理1t厌氧消化出水的费用为0.69元。由此可见,MAP结晶法比较适用于处理猪场废水经厌氧消化后的出水,这样不仅脱氮除磷效果好,而且成本较低。
The accumulation of nitrogen and phosphorus compounds by discharge of wastewater is one of the main causes of eutrophication in lakes and close inshore waters. How to control nutrients pollution high-efficiencily and economically is the most important environmental issue which needs to be solved urgently at present. The removal and recovery of nitrogen and phosphorus from swine wastewater are very important for the pollution control and utilization of the wastewater, and the crystallization of magnesium ammonium phosphate is a main process for this purpose. In this thesis, the process conditions on the removal efficiencies of nitrogen and phosphate with MAP crystallization were investigated in synthetic and actual swine wastewater systems and the three optimum process parameters were obtained. Small-scale and enlargement experiments of three kinds of processes on swine raw sewage and anaerobic digester effluents were carried out respectively, and then running economic costs were analyzed.
     Firstly, with synthetic wastewater, small-scale batch experiments of MAP crystallization were carried out, adopting MgCl2·6H2O and Na2HPO4·12H2O as precipitants. And by orthogonal experiments the paper drew the sequence of actors and significance level. The effect of P:N molar ratio was the most significant. The optimal reaction condition was obtained by single factor experiments. It showed that P:N molar ratio of 0.9-1.0, pH of 9.5-10.5, Mg:N molar ratio of 1.0-1.1, were found to be beneficial for the higher removal of NH4+-N and the lower residual concentration of phosphate. However, the influences of stirring speed, reaction time and settling time were not significant. From saving energy and reducing the process time perspective,100-200 r·min-1,10-15 min,15-30min could be chosen, respectively.
     Secondly, in connection with the imbalance of NH4+-N, Mg2+, PO43--P three ions ratio of actual swine wastewater, a systematic study was performed to investigate three types of process conditions to realize the removal of nitrogen and phosphorus from actual swine wastewater. It showed that only by adjusting pH of the wastewater, the optimum pH value was in the range of 9.0-10.0. The pH of the wastewater was raised to 8.91 with continuous aeration standing 60min, and the ammonium-nitrogen, phosphorus and total nitrogen removal efficiencies were 16.8%, 78.4% and 21.4%, respectively. Aeration was especially suitable for swine anaerobic effluents rich in CO2. Adding magnesium source could increase the phosphorus removal efficiency obviously, which was above 95.4%, when the optimum Mg:P molar ratio was 1.6 and the optimum pH value was in the range of 9.0-10.0. The high ammonium-nitrogen removal efficiency could be achieved by adding magnesium and phosphate soures simultaneously, which could reach 87.4% and the residual phosphorous was less than 10mg·L-1 in the solution with the optimum pH 9.5, P:N molar ratio 1.0 and Mg:N molar ratio 1.1.
     Lastly, with actual swine wastewater, the enlargement experiments of MAP crystallization were carried out. It showed that only adjusting pH of the wastewater and adding magnesium source, capable of phosphorous removal, were suitable for phosphate-rich swine wastewater. Swine raw sewage treated by adding magnesium and phosphate sources simultaneously (Mg:N=1.2, P:N=1.0) had the lowest ammonium-nitrogen removal cost, which was 7.85 yuan·(kgNH4+-N)-1 and the treatment cost of one ton swine raw sewage was 4.52 yuan. Adding magnesium and phosphate sources simultaneously (Mg:N=1.1, P:N=0.9) was suitable for swine anaerobic digester effluents. The treatment cost of one ton swine anaerobic digester effluents was 0.69 yuan and the ammonium-nitrogen removal cost was 4.08 yuan·(kgNH4+-N)-1. Thus it can be seen that the processes should be used after anaerobic treatment not only in removing ability of both nitrogen and phosphorus but also in low cost.
引文
[1]刘延华.对活性污泥过剩摄磷发生条件的新认识[J].给水排水,1997,23(10):18-20
    [2]段妮娜,董滨,何群彪,等.规模化养猪废水处理模式现状和发展趋势[J].净水技术,2008,27(4):9-15
    [3]袁鹏,宋永会,袁芳,彭剑峰.磷酸铵镁结晶法去除和回收养猪废水中营养元素的实验研究[J].环境科学学报,2007,27(7):1127-1133
    [4]邓良伟.规模化畜禽养殖废水处理技术现状探析[J].中国生态农业学报,2006,14(2):23-25
    [5]刘小澜,王继徽,黄稳水,等.磷酸铵镁法处理焦化厂高浓度氨氮废水[J].环境污染治理技术与设备,2005,6(3):65-66
    [6]汤琪,罗固源.磷酸铵镁沉淀法处理磷酸盐工业废水[J].化工进展,2008,27(4):558-563
    [7]赵庆良;李湘中.化学沉淀法去除垃圾渗滤液中的氨氮[J].环境科学,1999,20(5):90-92
    [8]Zhang T, Ding L L, Ren H Q. Pretreatment of ammonium removal from landfill leachate by chemical precipitation[J]. Journal of Hazardous Materials,2009,166(2/3):911-915
    [9]Gunay A, Karadag D, Tosun I, et al. Use of magnesit as a magnesium source for ammonium removal from leachate[J]. Journal of Hazardous Materials,2008,156(1/2/3):619-623
    [10]Sibel U D, Maazuza O. Removal of ammonium and phosphate from the supernatant of anaerobically digested waste activated sludge by chemical precipitation[J]. Bioresource Technology,2009,100(13):3236-3244
    [11]Liu Z G, Zhao Q L, Wang K, et al. Urea hydrolysis and recovery of nitrogen and phosphorous as MAP from stale human urine[J]. Journal of Environmental Sciences,2008, 20(8):1018-1024
    [12]Song Y H, Yuan P, Zheng B H, et al. Nutrients removal and recovery by crystallization of magnesiu ammonium phosphate from synthetic swine wastewater[J]. Chemosphere,2007, 69(2):319-324
    [13]许国强,曾光明,等.氨氮废水处理技术现状及发展[J].湖南有色金属,2002,(2):29-33
    [14]高廷耀,顾国维.水污染控制工程下册(第二版)[M].北京:高等教育出版社,1999
    [15]孙锦宜.含氮废水处理技术与应用[M].北京:化学工业出版社,2003.130-181
    [16]张庆东,赵东风,赵朝成.吸附法脱氮现状及常用吸附剂介绍[J].新疆环境保护,2002,24(2):43-46
    [17]Jung J Y, Chung Y C, Shin H S, et al. Enhanced ammonia nitrogen removal using consistent biological regeneration and ammonium exchange of zeolite in modified SBR process[J]. Water Research,2004,38(2):347-354
    [18]吴海林,杨开,王弘宇,等.废水除磷技术的研究与发展[J].环境污染治理技术与设 备,2003,4(1):53-57
    [19]赵桂瑜,周琪.沸石吸附去除污水中磷的研究[J].水处理技术,2007,33(2):34-37
    [20]赵庆良,李湘中.垃圾渗滤液中的氨氮对微生物活性的抑制作用[J].环境污染与防治,1998,20(6):1-4
    [21]何岩,赵由才,周恭明.高浓度氨氮废水脱氮技术研究进展[J].工业水处理,2008,28(1):1-4
    [22]Khin T, Annachhatre A P. Novel microbial nitrogen removal processes[J]. Biotechnology Advances,2004,22(7):519-532
    [23]Van Kempen R, Mulder J W, Uijterllnde C A, et al. Overview:full scale experience of the SHARON process for treatment of rejection water of digested sludge dewatering [J]. Water Science and Technology,2001,44(1):145-152
    [24]何岩,周恭明.HRT对亚硝酸型硝化反应器处理“中老龄”垃圾渗滤液的影响研究[J].广州环境科学,2005,20(2):8-11
    [25]李春杰,耿琰,周琪,等.SMSBR处理焦化废水中的短程硝化反硝化[J].中国给水排水,2001,17(11):50-54
    [26]方士,李筱焕.高氨氮味精废水的亚硝化/反亚硝化脱氮研究[J].环境科学学报,2001,21(1):79-83
    [27]王欢,李旭东,曾抗美.猪场废水厌氧氨氧化脱氮的短程硝化反硝化预处理研究[J].环境科学,2009,30(1):114-119
    [28]Jetten M S M, Wagner M, Fuerst J. Microbiology and application of the anaerobic ammonium oxidation (anammox) process[J]. Current Opinion in Biotechnology,2001, 12(3):283-288
    [29]Fux C, Boehler M, Huber P, et al. Biological treatment of ammonium-rich wastewater by partial nitritation and subsequent anaerobic ammonium oxidation (anammox) in a pilot plant [J]. Journal of Biotechnology,2002,99(3):295-306
    [30]Mino T, Van Loosdrecht M C M, Heijnen J J. Microbiology and biochemistry of the enhanced biological phosphate removal process[J]. Water Research,1998,32(11): 3193-3207
    [31]郝晓地,汪慧贞,钱易,等.欧洲城市污水处理技术新概念-可持续生物除磷脱氮工艺(上)[J].给水排水,2002,28(6):6-11
    [32]王晓莲,彭永臻,王淑莹,等.城市可持续污水生物处理技术[J].水处理技术,2004,30(2):106-109
    [33]李军,杨秀山,彭永臻.微生物与水处理工程[M].北京:化学工业出版社,2002
    [34]卢峰,杨殿海.反硝化除磷工艺的研究开发进展[J].中国给水排水,2003,19(9):32-34
    [35]李贤胜,王琳,施永生.生物法同步脱氮除磷主要工艺及问题探讨[J].净水技术,2005,24(6):30-33
    [36]Doyle J D, Parsons S A. Struvite formation, control and recovery[J]. Water Research,2002, 36(16):3925-3940
    [37]马世昌.化学物质辞典[M].西安:陕西科学技术出版社,2003
    [38]秋山尧(日).复合肥料中的成盐反应[M].于文洲,吴维江译.北京:化学工业出版社,1986
    [39]曾之平,李玉,李喜红.新型复合肥-磷酸铵镁生成条件的研究[J].河南化工,1995,12:8-10
    [40]Van Rensburg P, Musvoto E V, Wentzel M C, et al. Modelling multiple mineral precipitation in anaerobic digester liquor[J]. Water Research,2003,37(13):3087-3097
    [41]Battistoni P, Pavan P, Prisciandaro M, et al. Struvite crystallization:A feasible and reliable way to fix phosphorus in anaerobic supernatants[J]. Water Research,2000,34(11): 3033-3041
    [42]Nelson N O, Mikkelsen R L, Hesterberg D L. Struvite precipitation in anaerobic swine lagoon liquid:effect of pH and Mg:P ratio and determination of rate constant[J]. Bioresource Technology,2003,89(3):229-236
    [43]Suzuki K, Tanaka Y, Osada T, et al. Removal of phosphate, magnesium and calcium from swine wastewater through crystallization enhanced by aeration[J]. Water Research,2002, 36(12):2991-2998
    [44]邹安华,孙体昌,邢奕,等.pH对MAP沉淀法去除废水中氨氮的影响[J].环境科学动态,2005(4):4-6
    [45]Jaffer Y, Clark T A, Pearce P, et al. Potential phosphorus recovery by struvite formation[J]. Water Res.,2002,36(7):1834-1842
    [46]Zhang T, Ding L L, Ren H Q. Pretreatment of ammonium removal from landfill leachate by chemical precipitation[J]. Journal of Hazardous Materials,2009,166(2/3):911-915
    [47]闵敏,黄种买.化学沉淀法去除养猪场废水中氨氮的试验研究[J].化学与生物工程,2005,(5):27-29
    [48]Stratful I, Scrimshaw M D, Lester J N. Conditions influencing the precipitation of magnesium ammonium phosphate[J]. Water Res.,2001,35(17):4191-4199
    [49]Anton Perera P W, Wu W X, Chen Y X, et al. Struvite recovery from swine waste biogas digester effluent through a stainless steel device under constant pH conditions[J]. Biomedical and Environmental Sciences,2009,22(3):201-209
    [50]Bonurophoulos N C, Koutsoukos P G. Spontaneous precipitation of struvite from aqueous solutions[J]. Journal of Crystal Growth,2000,213:381-388
    [51]霍守亮,席北斗,刘鸿亮,等.磷酸铵镁沉淀法去除与回收废水中氮磷的应用研究进展[J].化工进展,2007,26(3):371-374
    [52]Battistoni P, Pavan P, Cecchi F, et al. Phosphate removal in real anaerobic supernatants: modeling and performance of a fluidized bed reactor[J]. Water Sci. Tech.,1998,38(1): 275-283
    [53]Imtiaj Ali M d, Philip A S. A fed-batch design approach of struvite system in controlled supersaturation[J]. Chemical Engineering Science,2006,61(12):3951-3961
    [54]Ohlinger K N, Young T M, Schroeder E D. Kinetics effects on preferential struvite accumulation in wastewater[J]. J. Environ. Eng.,1999,125(8):730-737
    [55]Borgerding J. Phosphate deposits in digestion systems[J]. Water Pollution Control Federation,1972,44(5):813-819
    [56]Williams S. Struvite precipitation in the sludge stream at Slough wastewater treatment plant and opportunities for phosphorus recovery[J]. Environmental Technology,1999,20(7): 743-747
    [57]毕学军,王振江,于澎学,等.各污泥处理单元废液的磷含量控制问题[J].中国给水排水,2003,19(1):98-99
    [58]Jaffer Y, Clark T A, Pearce P, Parsons S A. Assessing the potential of full scale phosphorus recovery by struvite formation[C]. Second International Conference on Recovery of phosphates from Sewage and Animal Wastes. Noordwijkerhout, Holland,2001,3:12-14
    [59]Luz E de-Bashan, Yoav Bashan. Recent advances in removing phosphorus from wastewater and its future use as fertilizer (1997-2003)[J]. Water Research,2004,38(19):4222-4246
    [60]程芳琴,贺春宝.磷酸镁铵的性质、制备方法及应用[J].磷肥与复肥,2004,19(4):53-54
    [61]El Diwani G, El Rafiea S, El Ibiari N N, et al. Recovery of ammonia nitrogen from industrial wastewater treatment as struvite slow releasing fertilizer[J]. Desalination,2007, 214(1/2/3):200-214
    [62]Sugiyama S, Yokoyama M, Ishizuka H, et al. Removal of aqueous ammonium with magnesium phosphates obtained from the ammonium-elimination of magnesium ammonium phosphate[J]. Journal of Colloid and Interface Science,2005,292(1):133-138
    [63]Shu L, Schneider P, Jegatheesan V, et al. An economic evaluation of phosphorus recovery as struvite from digester supernatant[J]. Bioresource Technology,2006,97(17):2211-2216
    [64]Liu Z G, Zhao Q L, Lee D J, et al. Enhancing phosphorus recovery by a new internal recycle seeding MAP reactor[J]. Bioresource Technology,2008,99(14):6488-6493
    [65]Uludag-Demirer S, Demirer G N, Chen S. Ammonia removal from anaerobically digested dairy manure by struvite precipitation[J]. Process Biochemistry,2005,40(12):3667-3674
    [66]Elisabeth, Muench V, Barrm K. Controlled struvite crystallisation for removing ohosphorus from anaerobic digester sidetreams[J]. Research,2001,35(1):151-159
    [67]Battistoni P, De Angelis A, Prisciandaro M, et al. P removal from anaerobic supernatants by struvite crystallization:long term validation and process modeling[J]. Research,2002,36(8): 1927-1938
    [68]Suzuki K, Tanaka Y, Kuroda K, et al. Recovery of phosphorous from swine wastewater through crystallization[J]. Bioresource Technology,2005,96(14):1544-1550
    [69]Suzuki K, Tanaka Y, Kuroda K, et al. Removal and recovery of phosphorous from swine wastewater by demonstration crystallization reactor and struvite accumulation device[J]. Bioresource Technology,2007,98(8):1573-1578
    [70]Gunay A, Karadag D, Tosun I, et al. Use of magnesit as a magnesium source for ammonium removal from leachate[J]. Journal of Hazardous Materials,2008,156(1/2/3):619-623
    [71]Chimenos J M, Fernandez A I, Villalba G, et al. Removal of ammonium and phosphates from wastewater resulting from the process of cochineal extraction using MgO-containing by-product[J]. Research,2003,37(7):1601-1607
    [72]Lee S I, Weon S Y, Lee C W, et al. Removal of nitrogen and phosphate from wastewater by addition of bittern[J]. Chemosphere,2003,51(4):265-271
    [73]He S I, Zhang Y, Yang M. Repeated use of MAP decomposition residues for the removal of high ammonium concentration from landfill leachate[J]. Chemosphere,2007,66(11): 2233-2238
    [74]Turker M, Celen I. Removal of ammonia as struvite from anaerobic digester effluents and recycling of magnesium and phosphate[J]. Bioresource Technology,2007,98(8):1529-1534
    [75]贾玉鹤,李晶,刘洪波,等.磷酸铵镁沉淀法去除垃圾渗滤液中氨氮的实验研究[J].环境工程学报,2007,1(8):57
    [76]国家环境保护总局《水和废水监测分析方法》编委会.水和废水监测分析方法(第4版)[M].北京:中国环境科学出版社,2002
    [77]湖南化工研究所编.钙镁磷肥生产分析方法[M].北京:石油化学工业出版社,1976
    [78]Uludag-Demirer S, Othman M. Removal of ammonium and phosphate from the supernatant of anaerobically digested waste activated sludge by chemical precipitation[J]. Bioresource Technology,2009,100(13):3236-3244
    [79]Warmadewanthi, Liu J C. Recovery of phosphate and ammonium as struvite from semiconductor wastewater[J]. Separation and Purification Technology,2009,64(3):368-373
    [80]邹安华.不同水质中磷酸铵镁的结晶形态及回收研究.北京科技大学博士学位论文[D],2006
    [81]王建森,宋永会,袁鹏,等.基于PHREEQC程序的磷酸铵镁结晶法污水处理工艺模型化研究[J].环境科学学报,2006,26(2):208-213
    [82]邹安华,孙体昌,宋存义,等.化学沉淀法从氨氮废水中回收磷酸铵镁[J].北京科技大学学报,2007,29(6):562-568.
    [83]Deng L, Zheng P, Chen Z, et al. Improvement in post-treatment of digested swine wastewater[J]. Bioresource Technology,2008,99(8):3136-3145
    [84]Jardin N, Popel H J. Refixation of phosphates released during bio-P sludge handling as struvite or aluminum phosphate[J]. Environmental Technology,2001,22(11):1253-1262
NGLC 2004-2010.National Geological Library of China All Rights Reserved.
Add:29 Xueyuan Rd,Haidian District,Beijing,PRC. Mail Add: 8324 mailbox 100083
For exchange or info please contact us via email.