印染废水活性污泥代谢状态光偏转快速检测法

张洛红, 李芮莹, 曹敏, 成晶晶, 王勋涛, 翟迎博, 熊鑫

中国环境科学 ›› 2021, Vol. 41 ›› Issue (9) : 4157-4166.

PDF(1229 KB)
PDF(1229 KB)
中国环境科学 ›› 2021, Vol. 41 ›› Issue (9) : 4157-4166.
水污染与控制

印染废水活性污泥代谢状态光偏转快速检测法

  • 张洛红, 李芮莹, 曹敏, 成晶晶, 王勋涛, 翟迎博, 熊鑫
作者信息 +

Study on rapid detection of beam deflection method for detecting metabolic status of activated sludge from printing and dyeing wastewater

  • ZHANG Luo-hong, LI Rui-ying, CAO Min, CHENG Jing-jing, WANG Xun-tao, ZHAI Ying-bo, XIONG Xin
Author information +
文章历史 +

摘要

针对现有活性污泥检测方法过程繁琐、耗时长、检测结果滞后的局限,提出了光偏转快速检测法.在污泥负荷为0.33KgCOD/(kg MLSS·d)、水力停留时间为15h的印染废水完全混合式活性污泥系统中,投放粒径4mm、具有20μm微孔结构的聚乙烯醇(PVA)凝胶小球以负载微生物,并在小球达到稳定状态后,对其表面处因外界溶液与微生物代谢产物交换产生的浓度梯度变化,借助光斑分析仪进行光偏转检测,同时测定与光偏转检测结果相对应的15h后的出水COD及COD去除率.连续10个月的检测发现,小球中富集的主要为细菌,当进水COD由91.95mg/L增至519.4mg/L时,小球的光偏转值从229.51μm增加至299.97μm,COD去除率从16.03%提高至66.99%;当DO浓度为1.5mg/L~5mg/L时,小球光偏转值在DO=4mg/L时增至最大为309.3mg/L,对应状态下COD去除率增至最大为61.18%;在pH值为6~9时,小球光偏转值在pH=7时增至最大为293.96μm,对应状态下COD去除率也达到最大值为64.83%;当重金属Cr3+浓度增至50mg/L时,微生物活性逐渐受到抑制,小球光偏转值在Cr3+浓度为20mg/L时降至269.7μm,随后随着Cr3+浓度的增加,微生物细胞受损,胞内物质溶出,小球光偏转值有所增大,对应状态下COD去除率从52.5%持续降低至25.73%.结果表明:该方法可快速获得活性污泥代谢状态变化信息,且依据特定条件下小球光偏转值变化能够预测随后印染废水COD的去除效果.利用三维荧光光谱初步探究了微生物代谢引发光偏转的机理,发现参与微生物代谢的主要有机物为酪氨酸、芳香类蛋白及色氨酸.

Abstract

Considering that limitation that cumbersome process, time-consuming and lagging detection of current activated sludge testing process, a rapid detection of beam deflection method were provided in this study. The polyvinyl alcohol gel beads with a particle size of 4mm and microporous structure of 20μm were put in the printing and dyeing wastewater complete mixed activated sludge treatment system with a sludge load of 0.33KgCOD/(kg MLSS·d) and a hydraulic retention time of 15h. The light spot analyzer was used to detecte light deflection which reflect the surface concentration gradient changes due to the exchange of external solutions and microbial metabolites after the beads reached a stable state. The corresponding COD of effluent after 15h were also measured, meanwhile the COD removal rate were calculated. After ten consecutive months of testing, it was found that the predominant microorganism is bacteria in the PVA-gel beads. The light deflection value of the beads increased from 229.51μm to 299.97μm when the influent COD increased from 91.95mg/L to 519.4mg/L, and The COD removal rate also increased from 16.03% to 66.99%. The light deflection of the beads increased with dissolved oxygen concentration and reached to the higest value 309.3μm at DO=4mg/L, meanwhile, the corresponding COD removal rate reached to the maximum which is 61.18%, when the dissolved oxygen concentration range from 1.5mg/L to 5mg/L. The light deflection of the beads increased with dissolved oxygen concentration and reached to the higest value 293.96μm at pH=7, meanwhile, the corresponding COD removal rate reached to the maximum which is 64.83%, when the pH range from 6to 9. The light deflection value of the beads decreased with the concentration of Cr3+ and reached to 269.7μm when the Cr3+ concentration at 20mg/L. The light deflection value increased with Cr3+ concentration continiued increased to 50mg/L, but the corresponding COD removal rate decreased form 52.5% to 25.73%, for the reason that the microbial cells are damaged and the intracellular substances are dissolved. The results show that the changes information of metabolic state in activated sludge can be quickly obtained by this method. And the changes of light deflection value of beads can be used to predict the subsequent COD concentration removal effect of printing and dyeing wastewater under specific conditions. Three-dimensional fluorescence spectroscopy were also used to explore the mechanism of microbial metabolism triggering light deflection. And the results showed that the main organic substances involved in microbial metabolism are tyrosine, aromatic proteins and tryptophan.

关键词

COD去除率 / 光偏转快速检测法 / 活性污泥法 / 聚乙烯醇(PVA)凝胶小球 / 微生物代谢状态

Key words

activated sludge method / COD removal rate / microbial metabolism status / polyvinyl alcohol (PVA) -gel beads / rapid detection of beam deflection method

引用本文

导出引用
张洛红, 李芮莹, 曹敏, 成晶晶, 王勋涛, 翟迎博, 熊鑫. 印染废水活性污泥代谢状态光偏转快速检测法[J]. 中国环境科学. 2021, 41(9): 4157-4166
ZHANG Luo-hong, LI Rui-ying, CAO Min, CHENG Jing-jing, WANG Xun-tao, ZHAI Ying-bo, XIONG Xin. Study on rapid detection of beam deflection method for detecting metabolic status of activated sludge from printing and dyeing wastewater[J]. China Environmental Science. 2021, 41(9): 4157-4166
中图分类号: X703.1   

参考文献

[1] Carmen S D R, Luis M M, Rui A R B. Decontamination of an industrial cotton dyeing wastewater by chemical and biological processes[J]. Industrial & Engineering Chemistry Research, 2014, 53(6):2412-2421.
[2] 端正花,潘留明,陈晓欧,等.低温下活性污泥膨胀的微生物群落结构研究[J]. 环境科学, 2016,37(3):1070-1074.Duan Z H, Pan L M, Chen X O, et al. Changes of microbial community structure in activated sludge bulking at low temperature[J]. Environmental Science, 2016,37(3):1070-1074.
[3] 周律,彭标.微量元素对工业废水好氧生物处理的促进[J]. 清华大学学报(自然科学版), 2015,55(6):653-659.Zhou L, Pen B. Effect of trace elements for improving the aerobic biological treatment of industrial wastewater[J]. Journal of Tsinghua University (Science and Technology), 2015,55(6):653-659.
[4] 郝思宇,张艾,刘亚男.臭氧与过氧化钙协同降解甲基红废水[J]. 中国环境科学, 2019,39(2):591-597.Hao S Y, Zhang A, Liu Y N. Removal of methyl red in aqueous by O3/CaO2treatment:influencing factors and synergetic effects[J]. China Environmental Science, 2019,39(2):591-597.
[5] 唐嘉丽,岳秀,吉世明,等.好氧生化法处理印染废水原水的工艺优化研究[J]. 环境工程, 2016,34(S1):123-125,158.Tang J L, Yue X, Ji S M, et al. Optimizatio research on process of aerobic biological treatment for raw dyeing wastewater[J]. Environmental Engineering, 2016,34(S1):123-125,158.
[6] El Gohary F, Tawfik A. Decolorization and COD reduction of disperse and reactive dyes wastewater using chemical-coagulation followed by sequential batch reactor (SBR) process[J]. Desalination, 2009,249(3):1159-1164.
[7] 章志元,张莉,刘新,等.活性污泥培养初期溶解氧(DO)的控制[J]. 环境工程, 2008,26(S1):163-164.Zhang Z Y, Zhang L, Liu X, et al. Dissolved oxygen (DO) controlling in initial period of raising activated sludge[J]. Environmental Engineering, 2008,26(S1):163-164.
[8] Jochen H, Barbara S, Martin W. Floc volume effects in suspensions and its relevance for wastewater engineering[J]. Environmental Science & Technology, 2011,45(20):8788-8793.
[9] 张日霞,王社平,谢纯德,等.SVI在Orbal氧化沟运行管理中的指导作用[J]. 中国给水排水, 2010,26(6):52-54.Zhang R X, Wang S P, Xie C D, et al. Guiding role of SVI in actual operation and management of Orbal oxidation ditch process[J]. China Water & Wastewater, 2010,26(6):52-54.
[10] 张洛红,李冰清,李兴.ATP法和TTC法表征印染污泥性质的适用性[J]. 西安工程大学学报, 2013,27(6):764-767.Zhang L H, Li B Q, Li X. The applicability for describing the printing and dyeing sludge properties with ATP and TTC[J]. Journal of Xi'an Polytechnic University, 2013,27(6):764-767.
[11] Wang X F, Jia Y G, Li D. The relationship between SOUR and some pocess parameters in activated sludge system[J]. Advanced Materials Research, 2012,462:169-172.
[12] 刘宝宝,汪洋,易立,等.细菌生物被膜检测与分析方法[J]. 微生物学通报, 2018,45(10):2263-2270.Liu B B, Wang Y, Yi L, et al. Detection and analysis methods of bacterial biofilm[J]. Microbiology China, 2018,45(10):2263-2270.
[13] Szilvia T S, József O, Magdolna M, et al. Comparison of different granular solids as biofilm carriers[J]. Microchemical Journal, 2013, 107:101-107.
[14] Zheng Y K, Hu Z B, Tu X J, et al. In-situ determination of the observed yield coefficient of aerobic activated sludge by headspace gas chromatography[J]. Journal of Chromatography A, 2020,1610.
[15] Jiang X T, Ye L, Ju F, et al. Toward an intensive longitudinal understanding of activated sludge bacterial assembly and dynamics[J]. Environmental Science & Technology, 2018,52(15):8224-8232.
[16] Ni B J, Fang F, Xie W M, et al. Formation of distinct soluble microbial products by activated sludge:Kinetic analysis and quantitative determination[J]. Environmental Science & Technology, 2012,46(3):1667-1674.
[17] 李冰清.光偏转检测活性污泥生长状态新方法研究[D]. 西安:西安工程大学, 2014.Li B Q. The study of new method for detecting the activated sludge metabolic state by light deflection[J]. China:Xi'an Polytechnic University, 2014.
[18] 王利娜,刘永红,闫爱军,等.生活污水PVA生物处理工艺[J]. 环境工程学报, 2016,10(4):1688-1692.Wang L N, Liu Y H, Yan A J, et al. Treatment of domestic sewage by PVA biological process[J]. Chinese Journal of Environmental Engineering, 2016,10(4):1688-1692.
[19] 曹敏,张洛红,成晶晶,等.聚乙烯醇载体在序批式高校生活污水处理中的应用[J]. 西安工程大学学报, 2018,32(3):285-290.Cao M, Zhang L H, Cheng J J, et al. Application of PVA carrier in SBR treatment of domestic sewage at university campus[J]. Journal of Xi'an Polytechnic University, 2018,32(3):285-290.
[20] Khanh D P. Studies on COD removal using poly (vinyl alcohol)-gel beads as biomass carrier in UASB reactor[D]. Japan:Kumamoto University, 2012.
[21] Bai X, Ye Z F, Li Y F, et al. Preparation ofcrosslinked macroporous PVA foam carrier for immobiliza-tion of microorganisms[J]. Process Biochemistry, 2010,45(1):60-66.
[22] 康小虎,冷艳,曾小英,等.污水处理活性污泥微生物群落研究进展[J]. 环境科学与技术, 2020,43(5):49-54.Kang X H, Len Y, Zeng X Y, et al. Review on activated sludge microbial community in sewage treatment[J]. Environmental Science & Technology, 2020,43(5):49-54.
[23] 鞠峰,张彤.活性污泥微生物群落宏组学研究进展[J]. 微生物学通报, 2019,46(8):2038-2052.Ju F, Zhang T. Advances in metaomics research on activated sludge microbial community[J]. Microbiology China, 2019,46(8):2038-2052.
[24] Chao Y, Wei Z, Liu R H, et al. Phylogenetic diversity and metabolic potential of activated sludge microbial communities in full-scale wastewater treatment plants[J]. Environmental Science & Technology, 2011,45(17):7408-7415.
[25] Nie L J, Kuboda M, Inoue T, et al. Effect of acid solutions on plants studied by the optical beam deflection method[J]. Journal of Environmental Sciences, 2013,25(1):93-96.
[26] 罗茜,马宏瑞,朱超,等.外源和内源呼吸模式下好氧活性污泥的微生物群落演替及生物活性特征[J]. 生态环境学报, 2013,22(12):1887-1892.Luo Q, Ma H R, Zhu C, et al. Bacterial community and metabolic characteristics during endogenous and exogenous periods in activated sludge[J]. Ecology and Environmental Sciences, 2013,22(12):1887-1892.
[27] 金宝丹,王淑莹,邢立群,等.基质投加方式对污泥碱性发酵性能的影响[J]. 中国环境科学, 2015,35(10):3010-3017.Jin B D, Wang S Y, Xing L Q, et al. The effect of substrate adding method on performance of sludge alkaline fermentation[J]. China Environmental Science, 2015,35(10):3010-3017.
[28] Gulde R, Helbling D E, Scheidegger A, et al. pH-dependent biotransformation of ionizable organic micro-pollutants in activated sludge[J]. Environmental Science & Technology, 2014,48(23):13760-8.
[29] 李兴.印染废水生物处理系统活性污泥性质的检测方法比较研究[D]. 西安:西安工程大学, 2011.Li X. Comparative study on detection methods of activated sludge on printing dyeing wastewater biological treatment system[J]. Xi'an:Xi'an Polytechnic University, 2011.
[30] Wang L L, Wang L F, Ren X M, et al. pH dependence of structure and surface properties of microbial EPS[J]. Environmental science & technology, 2012,46(2):737-44.
[31] 朱哲,李涛,王东升,等.pH对活性污泥表面特性和形态结构的影响[J]. 环境工程学报, 2008,(12):1599-1604.Zhu Z, Li T, Wang D S, et al. Effect of pH on surface properties and Physical structure of activated sludge flocs[J]. Chinese Journal of Environmental Engineering, 2008,(12):1599-1604.
[32] 管斌斌,李庆,陈灵辉,等.基于锆-有机骨架的印染废水中Cr(Ⅵ)的荧光检测[J]. 纺织学报, 2021,42(2):122-128.Guan B B, Li Q, Chen L H, et al. Fluorescence detection of Cr(VI) from printing and dyeing wastewater by zirconium-organic framework[J]. Journal of Textile Research, 2021,42(2):122-128.
[33] He T, Zhang Y Z, Kong X J, et al. Zr(IV)-based metal organic framework with T-shaped ligand:unique structure, high stability, selective detection, and rapid adsorption of Cr2O72-in water[J]. ACS Applied Materials & Interfaces, 2018,10(19):16650-16659.
[34] 赵长坤,于娜玲,马丙瑞,等.二价钴离子对序批式反应器性能;微生物活性及其微生物群落的影响[J]. 中国海洋大学学报(自然科学版), 2020,50(6):101-108.Zhao C K, Yu N L, Ma B R, et al. Effects of divalent cobalt (co(Ⅱ)) on the performance microbial activity and microbial community of sequencing batch reactor[J]. Periodical of Ocean University of China, 2020,50(6):101-108.
[35] Jaiswal D, Pandey J. Impact of heavy metal on activity of some microbial enzymes in the riverbed sediments:Ecotoxicological implications in the ganga river(India)[J]. Ecotoxicology and Environmental Safety, 2018,46(3):104-115.
[36] Zeeshan M, Murugadas A, Ghaskadbi S, et al. Ecotoxicological assessment of cobalt using Hydra model:ROS, oxidative stress, DNA damage, cell cycle arrest, and apoptosis as mechanisms of toxicity[J]. Environmental pollution, 2017,224:54-69.
[37] Plaper A, Jenko-Brinovec S, Premzl A, et al. Genotoxicity of trivalent chromium in bacterial cells. Possible effects on DNA topology[J]. Chemical Research in Toxicology, 2002,15(7):943-9.
[38] 杨金强,赵南京,殷高方,等.城市生活污水处理过程三维荧光光谱在线监测分析方法[J]. 光谱学与光谱分析, 2020,40(7):1993-1997.Yang J Q, Zhao N J, Yin G F, et al. On-line monitoring and analysis method of three-dimensional fluorescence spectrum in urban domestic sewage treatment process[J]. Spectroscopy and Spectral Analysis, 2020,40(7):1993-1997.
[39] 王士峰,吴静,程澄,等.某印染废水的水质指纹特征[J]. 光谱学与光谱分析, 2015,35(12):3440-3443.Wang S F, Wu J, Cheng C, et al. Aqueous fingerprint of printing and dyeing wastewater[J]. Spectroscopy and Spectral Analysis, 2015,35(12):3440-3443.
[40] Li W W, Zhang H L, Sheng G P, et al. Roles of extracellular polymeric substances in enhanced biological phosphorus removal process[J]. Water Research, 2015,86:85-95.
[41] Wei L L, An X Y, Wang S, et al. Effect of hydraulic retention time on deterioration/restarting of sludge anaerobic digestion:Extracellular polymeric substances and microbial response[J]. Bioresource Technology, 2017,244:261-269.

基金

陕西省重点研发计划项目(2018KW-036);西安市科技计划项目(2019217114GXRC007CG008-GXYD7.10)

PDF(1229 KB)

Accesses

Citation

Detail

段落导航
相关文章

/