摘要
为探讨经济实用的高浓度奶牛场污水预处理方法,该研究开展了絮凝预处理对膜生物反应器(Membrane Bioreactor,MBR)膜污染的影响试验,试验采用高浓度奶牛场污水原水和絮凝出水作为MBR进水依次运行,对比分析了不同进水的膜污染规律及其原因。结果表明,絮凝出水作为MBR进水时膜污染速率较污水原水降低47%且膜组件的维护性清洗时间间隔由10 d延长至16 d;MBR处理污水原水的膜池混合液中胞外聚合物(Extracellular Polymeric Substances,EPS)和溶解性微生物产物(Soluble Microbial Products,SMP)浓度分别为4.76和3.94 g/L,而处理絮凝出水时的EPS和SMP浓度值分别为3.97和2.23 g/L。两阶段MBR膜池混合液各粒径值总体上均呈现先增大后减小的趋势,第1和第2阶段的最大粒径体积百分比分别出现在第16天和第23天,第1阶段EPS浓度和SMP浓度均随着颗粒粒径的增大而减小,第2阶段EPS浓度随着颗粒粒径的增大而增大但SMP浓度与颗粒物粒径之间无变化规律;MBR处理污水原水的膜池混合液颗粒粒径的峰值较分散,且16 d后峰值向小粒径方向移动,而处理絮凝出水的峰值粒径相对稳定,且峰值粒径对应的最大体积百分比从3.57%增加至5.95%。MBR对2种进水的化学需氧量(Chemical Oxygen Demand,COD)去除率均可达90%以上,氨氮(Ammonia Nitrogen,NH3-N)去除率均接近90%,对絮凝出水的总磷(Total Phosphorus,TP)处理效果高于污水原水。絮凝预处理使膜池混合液的EPS和SMP浓度降低且SMP蛋白质浓度显著降低(P<0.05)、膜池混合液颗粒粒径显著增加(P<0.05),有效减缓了MBR的膜污染,絮凝预处理与MBR组合可望为高浓度奶牛场污水处理提供可靠的技术途径。
A cost-effective pretreatment method is highly demanding for the high-strength wastewater from dairy cattle farms in modern agricultural industry.In this study,a pilot test was conducted to investigate the effects of the flocculation on the membrane fouling of submerged membrane bioreactor(MBR).Normally,the wastewater from dairy cattle farm cannot be directly used as the influent of MBR,due to it contains high organic matters.Therefore,the flocculated and diluted raw wastewater can serve as the influent of MBR,where the chemical oxygen demand(COD)contents were similar.Two specific stages can be selected to operate sequentially in membrane fouling.The mechanism was also proposed in terms of transmembrane pressure,particle size,extracellular polymeric substances,and soluble microbial products inside MBR process tank during the two stages.The results showed that the transmembrane pressure in the first stage increased rapidly with time,when the flocculated effluent was used in the second stage,the membrane fouling rate decreased by 47%and the maintenance cleaning interval was 16 d in comparison with the interval of 10 d in the first stage.The concentration of extracellular polymeric substances(EPS)and soluble microbial products(SMP)of MBR in treating raw wastewater in the first stage were(4.76±1.67)g/L and(3.94±1.41)g/L,while the corresponding values of EPS and SMP in treating flocculated effluent were(3.97±1.58)g/L and(2.23±1.12)g/L,respectively.The SMP concentration in the first stage increased rapidly after the operation of the membrane bioreactor,but the SMP concentration in the second stage increased first and then decreased with time,and basically returned to its initial concentration level on the 30th day into the experiment.During both operation stages of MBR,the EPS concentration gradually increased with the running time.The peak volume percentages of the maximum particle size(MPS)in both stages increased first and then declined,and the maximum values in the first and second stage appeared on 16 d and 23 d,respectively.Both EPS concentration and SMP concentration decreased with the increase of particle size in the first stage,while in the second stage,EPS concentration increased with the increase of particle size,but there was no change rule between SMP concentration and particle size.Dispersed distribution of MPS in the first stage was observed and MPS turned to decrease after 16 days,while the MPS in the second stage remained relatively stable,and the maximum volume percentage of MPS increased from 3.57%to 5.95%.The COD removal rate of two influent waters by MBR can reach more than 90%,and the NH3-N(ammonia nitrogen)removal rate was close to 90%.The TP(total phosphorus)treatment effect of flocculated effluent was higher than that of raw sewage.The concentration of NPAM residue in flocculating effluent was analyzed,and the concentration ranged from 2 to 6 mg/L.When the flocculated effluent entered the process tank as MBR influent,the residual flocculant was not easy to permeate through the membrane module,and subsequently accumulated in the MBR process tank,where the macromolecule NPAM can combine the soluble constituents with the activated sludge flocs to form floc particles larger than the membrane pores,indicating effective to inhibit the clogging of membrane pores and the forming of gel layer,thereby to mitigate the membrane fouling.In Flocculation pretreatment,the EPS and SMP concentrations of liquid inside MBR process tank decreased with the concentration of SMP protein decreased significantly(P<0.05),but the particle size of liquid inside MBR process tank increased significantly(P<0.05),indicating beneficial for MBR fouling mitigation.The cost of dairy wastewater flocculation was estimated to be 0.08 Yuan/m^3.The combination of flocculation and MBR can be expected to be a promising technology for high-strength wastewater treatment in dairy cattle farms.
作者
宋建超
尚斌
陶秀萍
董红敏
王俊
郭江鹏
Song Jianchao;Shang Bin;Tao Xiuping;Dong Hongmin;Wang Jun;Guo Jiangpeng(Key Laboratory of Energy Conservation and Waste Management in Agricultural Structures,Ministry of Agriculture and Rural Affairs,Institute of Environment and Sustainable Development in Agriculture,Chinese Academy of Agricultural Sciences,Beijing 100081,China;Beijing General Station of Animal Husbandry,Beijing 100107,China)
出处
《农业工程学报》
EI
CAS
CSCD
北大核心
2020年第20期34-41,共8页
Transactions of the Chinese Society of Agricultural Engineering
基金
国家重点研发计划项目(2016YFD0501410)
北京市奶牛产业创新团队项目(BAIC06-2020)
中国农业科学院科技创新工程协同创新任务(CAAS-XTCX2016011-01)。
关键词
污水
絮凝
膜
膜生物反应器
奶牛场
污染
wastewater
flocculation
films
membrane bioreactor
dairy cattle farm
fouling