|
|
Effects of inorganic scaling on the separation of polyfluoroalkyl substances from water by nanofiltration membrane |
WANG Jia-xuan1,2,3,4, SUN Pei-dong1, LIU Zhe5, HOU Yu-shi6, GUO Jun-jiang5, LI Kun1, WANG Lei4,5 |
1. School of Architecture and Civil Engineering, Xi'an University of Science and Technology, Xi'an 710054, China; 2. Post-doctoral Research Center of Mining Engineering, Xi'an University of Science and Technology, Xi'an 710054, China; 3. Ecology and Environment Bureau of Yulin, Yulin 719000, China; 4. Research Institute of Membrane Separation Technology of Shaanxi Province, Xi'an University of Architecture and Technology, Xi'an 710055, China; 5. School of Environmental and Municipal Engineering, Xi'an University of Architecture and Technology, Xi'an 710055, China; 6. Shaanxi Architectural Design and Research Institute (Group) Co., Xi'an 710018, China |
|
|
Abstract Perfluorooctane sulfonate (PFOS) and perfluorobutane sulfonate (PFBS) which have different chain lengths were selected as the target polyfluoroalkyl substances (PFASs). Gypsum was chosen as the typical inorganic scaling. The characteristics and related mechanisms of PFASs removal by nanofiltration membrane in different gypsum scaling stages were studied. The tests were referred to as gypsum test. At the same time, the non-scaling inorganic salt solution with the same ionic strength was used to carry out a comparative test to investigate the retention rule of the target PFASs. The results showed that when gypsum coexisted with target PFASs, PFOS steady-state rejection of gypsum scaling experiment (>97.1%) displayed a higher retention than that of comparison experiment (<93.0%). While the steady-state removal rate of PFBS of comparison experiment (46.2%) was greater than that of gypsum scaling experiment (38.2%). For the same PFAS, the membrane surface charge of gypsum scaling experiment was less than that of the comparison test at the same filtration moment. Comprehensive analysis based on the combination of rejection rate, membrane flux and zeta potential showed that in the processing of gypsum scaling, the interception of PFOS was mainly controlled by the complexation and bridging of Ca2+ and PFOS, which affected the steric hindrance intensity of PFOS separation. At the initial stage of filtration, electrostatic repulsion played a major role in PFBS retention. When the scaling layer had formed, the cake enhanced concentration polarization effect became the main reason for the decrease of PFBS rejection.
|
Received: 07 June 2022
|
|
|
|
|
[1] |
Tachachartvanich P, Ramaprasad A S E, Durkin K A, et al. In Vitro Characterization of the Endocrine Disrupting Effects of Per-and Poly-fluoroalkyl Substances (PFASs) on the Human Androgen Receptor[J]. Journal of Hazardous Materials, 2022,429:128243.
|
[2] |
He J, Zhang S, Su Y, et al. Progress on the sample techniques and analytical methods for typical perfluorinated organic acids[J]. Se pu Chinese Journal of Chromatography, 2020,38(1):86-94.
|
[3] |
Van Gossum H, Bots J, Snijkers T, et al. Behaviour of damselfly larvae (Enallagma cyathigerum)(Insecta, Odonata) after long-term exposure to PFOS[J]. Environmental Pollution, 2009,157(4):1332-1336.
|
[4] |
Yin C, Pan C G, Xiao S K, et al. Insights into the effects of salinity on the sorption and desorption of legacy and emerging per-and polyfluoroalkyl substances (PFASs) on marine sediments[J]. Environmental Pollution, 2022,300:118957.
|
[5] |
Xu B, Qiu W, Du J, et al. Translocation, bioaccumulation and distribution of per-and polyfluoroalkyl substances (PFASs) in plants[J]. Iscience, 2022,300:104061.
|
[6] |
Xu Z, Ma X, Wei Z, et al. A novel fate and transport model for evaluating the presence and environmental risk of per-/poly- fluoroalkyl substances (PFASs) among multi-media in Lingang hybrid constructed wetland, Tianjin, China[J]. Chemosphere, 2022,291:132724.
|
[7] |
Tanner E M, Bornehag C G, Gennings C. Dynamic growth metrics for examining prenatal exposure impacts on child growth trajectories:Application to perfluorooctanoic acid (PFOA) and postnatal weight gain[J]. Environmental research, 2020,182:109044.
|
[8] |
Pierpaoli M, Szopińska M, Wilk B K, et al. Electrochemical oxidation of PFOA and PFOS in landfill leachates at low and highly boron-doped diamond electrodes[J]. Journal of Hazardous Materials, 2021,403:123606.
|
[9] |
Qian Y, Guo X, Zhang Y, et al. Perfluorooctanoic acid degradation using UV–persulfate process:modeling of the degradation and chlorate formation[J]. Environmental science & technology, 2016, 50(2):772-781.
|
[10] |
Fang Z, Li Z, Zhang X, et al. Enhanced arsenite removal from silicate-containing water by using redox polymer-based Fe (III) oxides nanocomposite[J]. Water Research, 2021,189:116673.
|
[11] |
Mastropietro T F, Bruno R, Pardo E, et al. Reverse osmosis and nanofiltration membranes for highly efficient PFASs removal:overview, challenges and future perspectives[J]. Dalton Transactions, 2021,50(16):5398-5410.
|
[12] |
Xiao X, Tu S, Lu M, et al. Discussion on the reaction mechanism of the photocatalytic degradation of organic contaminants from a viewpoint of semiconductor photo-induced electrocatalysis[J]. Applied Catalysis B:Environmental, 2016,198:124-132.
|
[13] |
王佳璇,胡御宁,岳向雷,等.溶液特性及共存物对纳滤膜去除水中全氟辛酸的影响[J]. 中国环境科学, 2022,42(2):665-671. Wang J X, Hu Y N, Yue X L, et al. Effects of solution characteristics and coexisted substances on the removal of perfluorooctanoic acid from water by nanofiltration membrane[J]. China Environmental Science, 2022,42(2):665-671.
|
[14] |
Wang J, Wang L, Xu C, et al. Perfluorooctane sulfonate and perfluorobutane sulfonate removal from water by nanofiltration membrane:The roles of solute concentration, ionic strength, and macromolecular organic foulants[J]. Chemical Engineering Journal, 2018,332:787-797.
|
[15] |
Wang P, Lu Y, Wang T, et al. Coupled production and emission of short chain perfluoroalkyl acids from a fast developing fluorochemical industry:Evidence from yearly and seasonal monitoring in Daling River Basin, China[J]. Environmental Pollution, 2016,218:1234- 1244.
|
[16] |
Xiong J, Hou Y, Wang J, et al. The rejection of perfluoroalkyl substances by nanofiltration and reverse osmosis:influencing factors and combination processes[J]. Environmental Science:Water Research & Technology, 2021,7(11):1928-1943.
|
[17] |
Zhao C, Zhang J, He G, et al. Perfluorooctane sulfonate removal by nanofiltration membrane the role of calcium ions[J]. Chemical Engineering Journal, 2013,233:224-232.
|
[18] |
Zhao C, Tang C Y, Li P, et al. Perfluorooctane sulfonate removal by nanofiltration membrane—the effect and interaction of magnesium ion/humic acid[J]. Journal of Membrane Science, 2016,503:31-41.
|
[19] |
Toure H, Anwar Sadmani A H M. Nanofiltration of perfluorooctanoic acid and perfluorooctane sulfonic acid as a function of water matrix properties[J]. Water Supply, 2019,19(8):2199-2205.
|
[20] |
Thomas M V, Puleo D A, Al-Sabbagh M. Calcium sulfate:a review[J]. Journal of long-term effects of medical implants, 2005,15(6):599-607.
|
[21] |
Power W H, Fabuss B M. Transient Solubilities in the Calcium Sulfate-Water System[J]. Journal of Chemical & Engineering Data, 1964,9(3):437-442.
|
[22] |
Vogel D, Simon A, Alturki A A, et al. Effects of fouling and scaling on the retention of trace organic contaminants by a nanofiltration membrane:the role of cake-enhanced concentration polarization[J]. Separation and Purification Technology, 2010,73(2):256-263.
|
[23] |
Shmulevsky M, Li X, Shemer H, et al. Analysis of the onset of calcium sulfate scaling on RO membranes[J]. Journal of membrane science, 2017,524:299-304.
|
[24] |
Bystrianský M, Nir O, Šír M, et al. The presence of ferric iron promotes calcium sulphate scaling in reverse osmosis processes[J]. Desalination, 2016,393:115-119.
|
[25] |
Karabelas A J, Karanasiou A, Mitrouli S T. Incipient membrane scaling by calcium sulfate during desalination in narrow spacer-filled channels[J]. Desalination, 2014,345:146-157.
|
[26] |
Cha J, Kim J. Analysis of fine dust correlation between air quality and meteorological factors using SPSS[J]. Journal of the Korea Institute of Information and Communication Engineering, 2018,22(5):722-727.
|
[27] |
Basto M, Pereira J M. An SPSS R-menu for ordinal factor analysis[J]. Journal of statistical software, 2012,46:1-29.
|
[28] |
Lim H S, Lee K M, Cho J W, et al. Analysis of the relationship between fire factors and influential factors using SPSS[J]. Journal of the Korean Society of Hazard Mitigation, 2019,19(5):103-112.
|
[29] |
Weaver B, Wuensch K L. SPSS and SAS programs for comparing Pearson correlations and OLS regression coefficients[J]. Behavior research methods, 2013,45(3):880-895.
|
[30] |
Vogel D, Simon A, Alturki A A, et al. Effects of fouling and scaling on the retention of trace organic contaminants by a nanofiltration membrane:the role of cake-enhanced concentration polarization[J]. Separation and Purification Technology, 2010,73(2):256-263.
|
[31] |
Zhao C, Hu G, Hou D, et al. Study on the effects of cations and anions on the removal of perfluorooctane sulphonate by nanofiltration membrane[J]. Separation and Purification Technology, 2018,202:385- 396.
|
[32] |
Song Y, Li X, Li C, et al. Exploring and comparing the roles of Ca2+ and Mg2+ in small-sized natural organics-induced charged nanofiltration membrane fouling[J]. Separation and Purification Technology, 2020,251:117415.
|
[33] |
Miao R, Li X, Wu Y, et al. A comparison of the roles of Ca2+ and Mg2+ on membrane fouling with humic acid:Are there any differences or similarities[J]. Journal of Membrane Science, 2018,545:81-87.
|
[34] |
Fang W, Wang R, Chou S, et al. Composite forward osmosis hollow fiber membranes:Integration of RO-and NF-like selective layers to enhance membrane properties of anti-scaling and anti-internal concentration polarization[J]. Journal of membrane science, 2012,394:140-150.
|
[1] |
WANG Wen-chao, HE Cong-hui, XU Heng, FANG Kuo, GAO Fang, XUE Xiao-fei, LIU Mu, SUN Kai, WANG Kai-jun. Study on the effect of online cleaning with NaClO on CE-HLMBR operation[J]. CHINA ENVIRONMENTAL SCIENCECE, 2023, 43(2): 638-647. |
|
|
|
|