Influence of the filler addition method on characteristics of operation stability and membrane fouling in MBR
FAN Jiawen1,, YANG Yongzhe1,,, YANG Hongbo2, LI Yaguo2 1.School of Environment and Municipal Engineering, Xi'an University of Architecture and Technology, Xi'an 710055, China 2.Shaanxi Microbe Biotechnology Co. Ltd., Weinan 714000, China
Abstract:To improve MBR removal performance and alleviate membrane fouling, the hybrid suspended biofilm enhanced-membrane bioreactor (HSBE-MBR) was employed for biopharmaceutical wastewater treatment. The aim of the study was to explore the effect of the filler addition method on the removal characteristics of typical pollutants, operation stability and membrane fouling and to determine the membrane fouling mechanism. Results showed that the average removal efficiencies of TCOD, ${\rm{NH}}_4^ + $-N and TN were 91.61%, 97.08% and 79.40%, respectively when the fillers were added in the anoxic and oxic zone (condition 1). The average removal efficiencies of TCOD, ${\rm{NH}}_4^ + $-N and TN were 91.09%, 97.24% and 83.66%, respectively when the fillers were added in the anoxic, oxic and membrane zone (condition 2). Under above two conditions, HSBE-MBR had good performance on TCOD, ${\rm{NH}}_4^ + $-N and TN removal, and maintained the good operation stability, TN removal efficiency increased by 4.26% under condition 2. HSBE-MBR operation time increased from 0.02~8.17 d (condition 1) to 0.26~138 d (condition 2). Cake formation was identified as the main membrane fouling mechanism under conditions 1 and 2, and their cake resistance ratios were 94.7% and 90.1%, respectively. The fillers added in membrane zone could effectively mitigate the cake formation on the membrane surface, and reduce the cake resistance by 8.07%. Meanwhile, the concentrations of soluble microbial product (SMP), loosely bound-EPS (LB-EPS) and tightly bound-EPS (TB-EPS) in the sludge mixed liquor were reduced from (63.70±12.95), (13.97±2.03) and (153.82±12.64) mg·g?1 (condition 1) to (31.77±3.17), (9.11±0.40) and (78.12±18.92) mg·g?1 (condition 2), respectively. The result of particle size distribution showed that the average particle size of the sludge increased from 31.35 μm (condition 1) to 34.71 μm (condition 2) when adding the fillers in the membrane zone. According to the characteristics of pollutants removal and membrane fouling, the optimal method of the fillers addition is to add them in the anoxic, oxic and membrane zone. This provides the reference for further improvement of the operation stability and membrane fouling alleviation of MBR. Key words:hybrid suspended biofilm enhanced-membrane bioreactor(HSBE-MBR)/ biopharmaceutical wastewater/ method of filler addition/ membrane fouling/ characteristic of mixed liquor.
图1HSBE-MBR实验装置图 Figure1.Schematic diagram of the HSBE-MBR
KAYA Y, ERSAN G, VERGILI I, et al. The treatment of pharmaceutical wastewater using in a submerged membrane bioreactor under different sludge retention times[J]. Journal of Membrane Science, 2013, 442(9): 72-82.
JIN L, ONG S L, NG H Y. Fouling control mechanism by suspended biofilm carriers addition in submerged ceramic membrane bioreactors[J]. Journal of Membrane Science, 2013, 427: 250-258. doi: 10.1016/j.memsci.2012.09.016
[4]
BAGHERI M, MIRBAGHERI S A. Critical review of fouling mitigation strategies in membrane bioreactors treating water and wastewater[J]. Bioresource Technology, 2018, 258: 318-334. doi: 10.1016/j.biortech.2018.03.026
[5]
HAZRATI H, SHAYEGAN J. Influence of suspended carrier on membrane fouling and biological removal of styrene and ethylbenzene in MBR[J]. Journal of the Taiwan Institute of Chemical Engineers, 2016, 64: 59-68. doi: 10.1016/j.jtice.2015.12.002
[6]
RAFIEI B, NAEIMPOOR F, MOHAMMADI T. Bio-film and bio-entrapped hybrid membrane bioreactors in wastewater treatment: Comparison of membrane fouling and removal efficiency[J]. Desalination, 2014, 337(1): 16-22.
CHENG D L, NGO H H, GUO W S, et al. Anaerobic membrane bioreactors for antibiotic wastewater treatment: Performance and membrane fouling issues[J]. Bioresource Technology, 2018, 267: 714-724. doi: 10.1016/j.biortech.2018.07.133
HU J, REN H Q, XU K, et al. Effect of carriers on sludge characteristics and mitigation of membrane fouling in attached-growth membrane bioreactor[J]. Bioresource Technology, 2012, 122(5): 35-41.
[11]
KURITA T, MOG T, KIMURA K. Influence of different biofilm carriers on the operation and membrane fouling of submerged membrane bioreactors[J]. Separation & Purification Technology, 2016, 169: 43-49.
[12]
国家环境保护总局. 水和废水监测分析方法[M]. 4版. 北京: 中国环境科学出版社, 2002.
[13]
ZHOU L J, ZHANG Z Q, JIANG W, et al. Effects of low-concentration Cr(VI) on the performance and the membrane fouling of a submerged membrane bioreactor in the treatment of municipal wastewater[J]. Biofouling, 2014, 30(1): 105-114. doi: 10.1080/08927014.2013.847925
[14]
LOWRY O H, ROSEBROUGH N J, FARR A L, et al. Protein measurement with the Folin phenol reagent[J]. Journal of Biological Chemistry, 1951, 193(1): 265-275.
[15]
GAUDY A F. Calorimetric determination of protein and carbohydrate[J]. Indian Water Wastes., 1962, 7: 17-22.
[16]
CHOO K H, LEE C H. Membrane fouling mechanisms in the membrane-coupled anaerobic bioreactor[J]. Water Research, 1996, 30(8): 1771-1780. doi: 10.1016/0043-1354(96)00053-X
[17]
KHAN S.J, IIYAS S, JAVID S, et al Performance of suspended and attached growth MBR systems in treating high strength synthetic wastewater[J]. Bioresource Technology, 2011, 102(9): 5331-5336. doi: 10.1016/j.biortech.2010.09.100
NGUYEN T T, BUI X T, LUU V P, et al. Removal of antibiotics in sponge membrane bioreactors treating hospital wastewater: Comparison between hollow fiber and flat sheet membrane systems[J]. Bioresource Technology, 2017, 240: 42-49. doi: 10.1016/j.biortech.2017.02.118
[20]
IVANOVIC I, LEIKNES T O. The biofilm membrane bioreactor (BF-MBR): A review[J]. Desalination & Water Treatment, 2012, 37(1/2/3): 288-295.
[21]
HUANG X, WEI C H, YU K C. Mechanism of membrane fouling control by suspended carriers in a submerged membrane bioreactor[J]. Journal of Membrane Science, 2008, 309(1): 7-16.
[22]
LEE S, KIM M H. Fouling characteristics in pure oxygen MBR process according to MLSS concentrations and COD loadings[J]. Journal of Membrane Science, 2013, 428(2): 323-330.
[23]
SATYAWALI Y, BALAKRISHNAN M. Effect of PAC addition on sludge properties in an MBR treating high strength wastewater[J]. Water Research, 2009, 43(6): 1577-1588. doi: 10.1016/j.watres.2009.01.003
[24]
HAN F, YE W, WEI D, et al. Simultaneous nitrification-denitrification and membrane fouling alleviation in a submerged biofilm membrane bioreactor with coupling of sponge and biodegradable PBS carrier[J]. Bioresource Technology, 2018, 270: 156-165. doi: 10.1016/j.biortech.2018.09.026
[25]
FLEMMING H C, WINGENDER J, SZEWZYK U, et al. Biofilms: An emergent form of bacterial life[J]. Nature Reviews Microbiology, 2016, 14(9): 563-575. doi: 10.1038/nrmicro.2016.94
[26]
ZHENG Y, TANG B, YE J, et al. A crucial factor towards a sustainable process for municipal wastewater treatment: Fouling effects of different statuses of biomass in the membrane bioreactors with no sludge discharge[J]. Journal of Cleaner Production, 2018, 192: 877-886. doi: 10.1016/j.jclepro.2018.05.048
[27]
DOMíNGUEZ CHABALINá L, RODRíGUEZ PASTOR M, RICO D P. Characterization of soluble and bound EPS obtained from 2 submerged membrane bioreactors by 3D-EEM and HPSEC[J]. Talanta, 2013, 115(17): 706-712.
[28]
ABASS O K, FANG F, ZHUO M, et al. Integrated interrogation of causes of membrane fouling in a pilot-scale anoxic-oxic membrane bioreactor treating oil refinery wastewater[J]. Science of the Total Environment, 2018, 642: 77-89. doi: 10.1016/j.scitotenv.2018.06.049
1.School of Environment and Municipal Engineering, Xi'an University of Architecture and Technology, Xi'an 710055, China 2.Shaanxi Microbe Biotechnology Co. Ltd., Weinan 714000, China Received Date: 2019-10-14 Accepted Date: 2019-12-24 Available Online: 2020-08-12 Keywords:hybrid suspended biofilm enhanced-membrane bioreactor(HSBE-MBR)/ biopharmaceutical wastewater/ method of filler addition/ membrane fouling/ characteristic of mixed liquor Abstract:To improve MBR removal performance and alleviate membrane fouling, the hybrid suspended biofilm enhanced-membrane bioreactor (HSBE-MBR) was employed for biopharmaceutical wastewater treatment. The aim of the study was to explore the effect of the filler addition method on the removal characteristics of typical pollutants, operation stability and membrane fouling and to determine the membrane fouling mechanism. Results showed that the average removal efficiencies of TCOD, ${\rm{NH}}_4^ + $-N and TN were 91.61%, 97.08% and 79.40%, respectively when the fillers were added in the anoxic and oxic zone (condition 1). The average removal efficiencies of TCOD, ${\rm{NH}}_4^ + $-N and TN were 91.09%, 97.24% and 83.66%, respectively when the fillers were added in the anoxic, oxic and membrane zone (condition 2). Under above two conditions, HSBE-MBR had good performance on TCOD, ${\rm{NH}}_4^ + $-N and TN removal, and maintained the good operation stability, TN removal efficiency increased by 4.26% under condition 2. HSBE-MBR operation time increased from 0.02~8.17 d (condition 1) to 0.26~138 d (condition 2). Cake formation was identified as the main membrane fouling mechanism under conditions 1 and 2, and their cake resistance ratios were 94.7% and 90.1%, respectively. The fillers added in membrane zone could effectively mitigate the cake formation on the membrane surface, and reduce the cake resistance by 8.07%. Meanwhile, the concentrations of soluble microbial product (SMP), loosely bound-EPS (LB-EPS) and tightly bound-EPS (TB-EPS) in the sludge mixed liquor were reduced from (63.70±12.95), (13.97±2.03) and (153.82±12.64) mg·g?1 (condition 1) to (31.77±3.17), (9.11±0.40) and (78.12±18.92) mg·g?1 (condition 2), respectively. The result of particle size distribution showed that the average particle size of the sludge increased from 31.35 μm (condition 1) to 34.71 μm (condition 2) when adding the fillers in the membrane zone. According to the characteristics of pollutants removal and membrane fouling, the optimal method of the fillers addition is to add them in the anoxic, oxic and membrane zone. This provides the reference for further improvement of the operation stability and membrane fouling alleviation of MBR.