油茶籽壳炭微球及其改性物对水中全氟辛烷磺酸盐(PFOS)的吸附
Adsorption of perfluorooctanesulfonate (PFOS) by carbon microspheres and their modified products prepared from Camellia oleifera seed shell
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摘要: 基于废弃油茶籽壳制备了4种炭材料,并应用于对水中全氟辛烷磺酸盐(PFOS)的吸附性能研究.以油茶籽壳生物质为碳源,首先通过水热碳化法制备了胶质炭微球并进一步对炭微球分别进行了退火、KOH浸渍扩孔和KOH研磨扩孔改性,然后将所制备的4种炭材料应用于水中PFOS的吸附去除,并对其吸附机理进行了探讨.吸附动力学结果表明,4种炭材料对PFOS吸附均符合拟二级动力学模型(R2≥0.994),吸附平衡时间分别为2 h、1 h、6 h和2 h.溶液pH值对KOH研磨炭材料的吸附性能影响较小,而对其它3种材料影响较大,4种炭材料对PFOS吸附的最佳pH值分别为2-3、3、2、2-10.4种炭材料对PFOS的吸附均符合Langmuir吸附模型(R2≥0.988),最大吸附量分别为14.4、17.8、223.7、3658.9 mg·g-1.4种炭材料对PFOS的吸附均倾向于单分子层的化学吸附过程,材料的比表面积为影响吸附量的最主要因素,其对PFOS的吸附主要依赖静电作用和疏水作用.
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关键词:
- 油茶籽壳 /
- 炭微球 /
- 全氟辛烷磺酸盐(PFOS) /
- 吸附
Abstract: Four types of biochar materials were prepared from the Camellia oleifera seed shell and applied in the adsorption removal of perfluotooctancesulfonate (PFOS) in aqueous solution. Firstly, the colloidal carbon microspheres were prepared from Camellia oleifera powder by hydrothermal carbonization. The synthesized carbon microspheres were then modified by annealing treatment, impregnating treatment with KOH solution and grinding activation treatment with KOH solid, respectively; and four different carbon materials were obtained. The adsorption properties of PFOS onto the four carbon materials were investigated and the corresponding adsorption mechanisms were studied. The adsorption kinetic results indicated that the PFOS adsorption onto these four adsorbents were all fitted with the pseudo-second-order model well(R2≥0.994), and the adsorption reached equilibrium with in 2 h, 1 h, 6 h and 2 h, respectively. Initial pH of the solution has little effect on PFOS adsorption onto the biochar obtained by KOH grinding treatment, but great effect on that of the other three biochar materials, and the optimum pH value for the four materials was 2-3, 3, 2 and 2-10, respectively. The Langmuir adsorption model described the experimental data of adsorption isotherms better than that Freundlich model (R2≥0.988), with the maximum adsorption capacity of 14.4, 17.8, 223.7 and 3658.9 mg·g-1, respectively. The mechanistic studies suggested that the specific surface area was the primary factor affecting the adsorption process, and the adsorption process was mainly depended on the electrostatic force and hydrophobic effect between the adsorbent and PFOS.-
Key words:
- Camellia oleifera /
- carbon microspheres /
- perfluotooctanesulfonate (PFOS) /
- adsorption
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[1] YU J, LV L, LAN P, et al. Effect of effluent organic matter on the adsorption of perfluorinated compounds onto activated carbon[J]. Journal of Hazardous Materials, 2012, 225-226: 99-106. [2] ZHOU Q, DENG S B, ZHANG Q Y, et al. Sorption of perfluorooctane sulfonate and perfluorooctanoate on activated sludge[J]. Chemosphere, 2010, 81(4): 453-458. [3] GIESY J P, KANNNAN K. Peer peviewed: Perfluorochemical surfactants in the environment[J]. Environmental Science & Technology, 2002, 36(7): 146A-152A. [4] ZHANG C J, YAN H, LI F, et al. Occurrence and fate of perfluorinated acids in two wastewater treatment plants in Shanghai, China[J]. Environmental Science and Pollution Research, 2015, 22(3): 1804-1811. [5] NAILE J E, KHIM J S, WANG T, et al. Perfluorinated compounds in water, sediment, soil and biota from estuarine and coastal areas of Korea[J]. Environmental Pollution, 2010, 158(5): 1237-1244. [6] SENTHILKUMAR K, OHI E, SAJWAN K, et al. Perfluorinated compounds in river water, river sediment, market fish, and wildlife samples from Japan[J]. Bulletin of Environmental Contamination and Toxicology, 2007, 79(4): 427-431. [7] VAN DE VIJVER K I, HOFF P T, VAN DONGEN W, et al. Exposure patterns of perfluorooctane sulfonate in aquatic invertebrates from the Western Scheldt estuary and the southern North Sea[J]. Environmental Toxicology and Chemistry, 2003, 22(9): 2037-2041. [8] LOOS R, LOCORO G, HUBER T, et al. Analysis of perfluorooctanoate (PFOA) and other perfluorinated compounds (PFCs) in the River Po watershed in N-Italy[J]. Chemosphere, 2008, 71(2): 306-313. [9] XU C M, CHEN H, JIANG F.Adsorption of perflourooctane sulfonate (PFOS) and perfluorooctanoate (PFOA) on polyaniline nanotubes[J]. Colloids and Surfaces A: Physicochemical and Engineering Aspects, 2015, 479: 60-67. [10] SCHAEFER C E, ANDAYA C, URTIAGA A, et al. Electrochemical treatment of perfluorooctanoic acid (PFOA) and perfluorooctane sulfonic acid (PFOS) in groundwater impacted by aqueous film forming foams (AFFFs)[J]. Journal of Hazardous Materials, 2015, 295:170-175. [11] JIN L, ZHANG P Y. Photochemical decomposition of perfluorooctane sulfonate (PFOS) in an anoxic alkaline solution by 185 nm vacuum ultraviolet[J]. Chemical Engineering Journal, 2015, 280: 241-247. [12] CAMPBELL T, HOFFMANN M R.Sonochemical degradation of perfluorinated surfactants: Power and multiple frequency effects[J]. Separation and Purification Technology, 2015, 156, Part 3: 1019-1027. [13] DENG S B, BEI Y, LU X Y, et al. Effect of co-existing organic compounds on adsorption of perfluorinated compounds onto carbon nanotubes[J]. Frontiers of Environmental Science & Engineering, 2015, 9(5): 784-792. [14] DENG S B, NIE Y, DU Z W, et al. Enhanced adsorption of perfluorooctane sulfonate and perfluorooctanoate by bamboo-derived granular activated carbon[J]. Journal of Hazardous Materials, 2015, 282: 150-157. [15] CARTER K E, FARRELL J.Removal of perfluorooctane and perfluorobutane sulfonate from water via carbon adsorption and ion exchange[J]. Separation Science and Technology, 2010, 45(6): 762-767. [16] ZHOU Q, PAN G, ZHANG J. Effective sorption of perfluorooctane sulfonate (PFOS) on hexadecyltrimethylammonium bromide immobilized mesoporous SiO2 hollow sphere[J]. Chemosphere, 2013, 90(9): 2461-2466. [17] OCHOA-HERRERA V, SIERRA-ALVAREZ R. Removal of perfluorinated surfactants by sorption onto granular activated carbon, zeolite and sludge[J]. Chemosphere, 2008, 72(10): 1588-1593. [18] 贾大伟, 田秉晖, 张国珍, 等. Fe3O4纳米磁性微粒对全氟辛烷磺酸盐的吸附[J]. 环境工程学报, 2012, 6(2): 389-392. JIA D D, TIAN B H, ZHANG G Z, et al. Adsorption of pernuorooctane sulfonate on Fe3O4 magnetic nanoparticles[J]. Chinese Journal of Environmental Engineering, 2012, 6(2): 389-392(in Chinese).
[19] ZHOU Q, DEND S B, YU Q, et al. Sorption of perfluorooctane sulfonate on organo-montmorillonites[J]. Chemosphere, 2010, 78(6): 688-694. [20] ZHANG Q Y, DENG S B, YU G,et al. Removal of perfluorooctane sulfonate from aqueous solution by crosslinked chitosan beads: Sorption kinetics and uptake mechanism[J]. Bioresource Technology, 2011, 102(3): 2265-2271. [21] 李云坤, 杜琳颖, 淦永鉴, 等. 油茶籽壳乙酸乙酯提取物对HepG2抗增殖作用及机制研究[J]. 基因组学与应用生物学, 2015, 34(11): 2299-2305. LI Y K, DU L Y, GAN Y J, er al. Anti-Proliferative effects of the ethyl acetate extract from shells of camellia oleifera on human hepatocellular carcinoma cells (HepG2)[J]. Genomics and Applied Biology, 2015, 34(11): 2299-2305(in Chinese).
[22] 沈骏, 郑茜茜, 吴晓琴, 等. 油茶蒲提取物活性部位对人前列腺增生BPH-1细胞的作用研究[J]. 现代食品科技,2015, 31(7): 6-11. SHEN J, ZHENG X X, WU X Q, er al. Effect of oil tea camellia extract on BPH-1 cells[J]. Modern Food Science and Technology, 2015, 31(7): 6-11(in Chinese).
[23] LI X N, CHEN S, QUAN X, et al. Enhanced adsorption of PFOA and PFOS on multiwalled carbon nanotubes under electrochemical assistance[J]. Environmental Science & Technology, 2011, 45(19): 8498-8505. [24] 闫婷婷, 江芳, 陈欢. 介孔氮化碳对水中全氟辛烷磺酸的吸附去除研究[J]. 环境科学学报, 2014, 34(6): 1464-1472. YAN T T, JIANG F, CHEN H. Adsorptive removal of perfluorooctane sulfonate from water by mesoporous carbon nitride[J]. Acta Scientiate Circumstantiae, 2014, 34(6): 1464-1472(in Chinese).
[25] YU Q, ZHANG R Q, Deng S B, et al. Sorption of perfluorooctane sulfonate and perfluorooctanoate on activated carbons and resin: Kinetic and isotherm study[J]. Water Research, 2009, 43(4): 1150-1158. [26] LIANG X Q, GONDAL M A, CHANG X F, et al. Facile preparation of magnetic separable powdered-activated-carbon/Ni adsorbent and its application in removal of perfluorooctane sulfonate (PFOS) from aqueous solution[J]. Journal of Environmental Science and Health, Part A, 2011, 46(13): 1482-1490. [27] CHEN X, XIA X H, WANG X L, et al. A comparative study on sorption of perfluorooctane sulfonate (PFOS) by chars, ash and carbon nanotubes[J]. Chemosphere, 2011, 83(10): 1313-1319. [28] DENG S B, YU Q, HUANG J, et al. Removal of perfluorooctane sulfonate from wastewater by anion exchange resins: Effects of resin properties and solution chemistry[J]. Water Research, 2010, 44(18): 5188-5195. [29] YAN T T, CHEN H, WANG X, et al. Adsorption of perfluorooctane sulfonate (PFOS) on mesoporous carbon nitride[J]. RSC Advances, 2013, 3(44): 22480-22489. [30] TANG C Y, SHIANG FU Q, GAO D, et al. Effect of solution chemistry on the adsorption of perfluorooctane sulfonate onto mineral surfaces[J]. Water Research, 2010, 44(8): 2654-2662. [31] WANG F, LIU C S, SHIH K.Adsorption behavior of perfluorooctanesulfonate (PFOS) and perfluorooctanoate (PFOA) on boehmite[J]. Chemosphere, 2012, 89(8): 1009-1014. [32] 栾萱, 周琴, 毕磊, 等. 全氟辛烷磺酸盐(PFOS)在藻渣/小球藻上的吸附行为及机理[J]. 环境工程学报, 2014, 8(3): 897-902. LUAN X, ZHOU Q, BI L, et al. Sorption behavior and mechanism of perfluorooctanesulfonate(PFOS) on Chlorella and Chlorella residues[J]. Chinese Journal of Environmental Engineering, 2014, 8(3): 897-902(in Chinese).
[33] YU Q, DENG S B, YU G. Selective removal of perfluorooctane sulfonate from aqueous solution using chitosan-based molecularly imprinted polymer adsorbents[J]. Water Research, 2008, 42(12): 3089-3097. -

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