闫 旭, 李旭光, 宋 雯, 朱宝存
济南大学 水利与环境学院, 山东 济南 250022
引用格式:
闫旭,李旭光,宋雯,等.铜锌铝水滑石制备及活化过氧单硫酸盐对水中土霉素降解性能[J].中国粉体技术,2025,31(2):59-70.
YAN Xu,LI Xuguang,SONG Wen,et al. Synthesis of CuZnAl layered double hydroxide and degradation of oxytetracycline in water by activated peroxymonosulfate[J].China Powder Science and Technology,2025,31(2):59-70.
DOI:10.13732/j.issn.1008-5548.2025.02.005
收稿日期:2024-02-21,修回日期:2024-04-28,上线日期:2024-11-20。
基金项目:国家自然科学基金项目,编号:22206057。
第一作者简介:闫旭(2001—),男,硕士生,研究方向为水滑石活化过氧单硫酸盐降解水中抗生素。E-mail:2868385956@qq. com 。
通信作者简介:李旭光(1989—),男,副教授,博士,硕士生导师,研究方向为高级氧化技术及其功能材料。E-mail:stu_lixug@ujn. edu. cn。
摘要:【目的】利用水滑石(layered double hydroxide,LDH)粉体材料催化能力强、结构可调、制备难度低、分散性良好等优点及其在高级氧化技术中的应用潜能,研究铜锌铝水滑石(CuZnAl-LDH)的制备方法,以及活化过氧单硫酸盐 (peroxymonosulfate, PMS)降解水中难降解污染物的性能。【方法】采用共沉淀法制备并表征 CuZnAl-LDH-x;选择水中土霉素(oxytetracycline, OTC)进行降解实验,确定CuZnAl-LDH-x的较优制备条件,研究水化学条件对催化体系中OTC降解率的影响;探究 CuZnAl-LDH-x 活化PMS的催化机制和降解途径;在不同水体样本中进行催化体系的实际应用性能评估。【结果】制得的 CuZnAl-LDH-x 具有致密的六边形层状结构;当 Cu、Zn、Al 元素的物质的量比为 5∶1∶2 时,CuZnAl-LDH-1-PMS 体系对 OTC 降解效果最佳;在 CuZnAl-LDH-1-PMS 体系初始 pH 为 6、CuZnAl-LDH-1质量浓度为20mg/L、PMS浓度为 1.0mmol/L、OTC质量浓度为10mg/L时降解效果最佳,降解时间为 40 min时降解率高达 96. 25%; CuZnAl-LDH-1-PMS体系具有良好的抗干扰性, pH、无机阴离子和腐殖酸等因素的影响较小;在 CuZnAl-LDH-1-PMS体系降解 OTC过程中存在自由基和非自由基2种途径,其中羟基自由基对降解率的贡献最大;CuZnAl-LDH-1-PMS体系在4种实际水体中对 OTC 的降解率仍能达到 74%~95%。【结论】CuZnAl-LDH-x制备过程简便,具备高效活化PMS并降解抗生素类污染物的能力,可以作为基于过硫酸盐的高级氧化水处理技术的催化剂。
关键词: 铜锌铝水滑石;活化过氧单硫酸盐;土霉素;降解;高级氧化水处理技术
Objective Layered double hydroxide (LDH) is a widely available and cost-effective material known for its unique structure,large specific surface area,controllable interlayer ion exchange,and stability. LDH is capable of activating peroxymonosulfate (PMS)in advanced oxidation processes,offering advantages such as high efficiency,abundant surface hydroxyl groups,and a range of active species. In this study,CuZnAl-LDH was synthesized using the co-precipitation method. The structure and properties of CuZnAl-LDH were characterized using scanning electron microscopy (SEM),high-resolution transmission electron microscopy (HRTEM),X-ray diffraction (XRD),and Fourier-transform infrared(FTIR)spectroscopy. The synthesis of CuZnAl-LDH was explored leveraging the favorable attributes of LDHs,such as robust catalytic activity,customizable structure,simple synthesis process,excellent dispersibility,and potential application in advanced oxidation processes. Furthermore,the effectiveness of activated PMS in degrading recalcitrant pollutants in water was investigated,highlighting the potential of CuZnAl-LDH as a catalyst in advanced oxidation applications.
Methods The CuZnAl-LDH-x(x=1,2,…,5)was prepared by the co-precipitation method using CuCl2·2H2O,ZnCl2 and AlCl3·6H2O at various molar ratios of Cu,Zn,and Al elements. The obtained powder was characterized by SEM,FTIR and XRD. The degradation experiments in CuZnAl-LDH-PMS system were conducted using OTC as a typical antibiotic in water. The experimental conditions,including the molar ratio of Cu,Zn,and Al elements,catalyst and PMS dosage,solution pH,and environmental factors such as inorganic anions and humic acid,were optimized. The mechanisms were also investigated by a quenching experiment and electron paramagnetic resonance(EPR) spectroscopy,and high performance liquid chromatography-mass spectrometry( HPLC-MS) was used to determine the degradation products of OTC in CuZnAl-LDH-1-PMS system. With distilled water as a control,tap water,Yellow River water,a city landscape lake water ,and a campus landscape lake water were selected as water samples to conduct OTC degradation experiment .
Results and Discussion The synthesized CuZnAl-LDH exhibited a dense hexagonal layered structure with XRD peaks,typical LDH structure. Among the CuZnAl-LDH-x-PMS systems,the composition with a molar ratio of Cu,Zn,and Al elements at 5∶1∶2 demonstrated the highest efficiency in degrading OTC.Under optimized conditions( initial pH of 6,CuZnAl-LDH-1 dosage of 20mg/L,and PMS concentration of 1mmol/L),the removal ratio of 10 mg/L OTC reached 96. 25% after 40 min. The CuZnAl-LDH-1-PMS catalytic system exhibited robust resistance to interference from environmental factors such as pH,inorganic anion and humic acid. The quenching experiment and EPR test showed that the degradation of OTC in CuZnAl-LDH-1- PMS system occurred via free radical pathway(·OH,SO4−·,·O2−) and non-free radical pathway(1O2),with·OH identified as the primary active radical species. A total of 10 intermediates were detected,leading to two degradation pathways for OTC. Compared with distilled water, the degradation rates of OTC in tap water, Yellow River water,a city landscape lake water,and a campus landscape lake water decreased slightly.
Conclusion CuZnAl-LDH-x was synthesized via a simple co-precipitation method and characterized by its typical layered structure,resembling hydrotalcite,and its properties. The CuZnAl-LDH-PMS system efficiently activates PMS to degrade OTC,achieving a maximum degradation rate. The CuZnAl-LDH-PMS catalytic system exhibited robust resistance to interference from factors like pH,inorganic anions( Cl-,HCO3-,NO3-,SO42-),and humic acid(HA),with minimal impact on OTC degradation rates. Bursting and EPR experiments revealed that OTC degradation by the CuZnAl-LDH-PMS system involved both free radical pathways(·OH,SO4−·,·O2−) and non-free radical pathways(1O2), with·OH identified as the primary active radical species. In actual water samples such as tap water,Yellow River water,a city and a campus landscape lake water,OTC degradation rates ranged from 74% to 95%,indicating the practical application potential of the CuZnAl-LDH-PMS catalytic system.
Keywords:CuZnAl layered double hydroxide;activated peroxymonosulfate;oxytetracycline;degradation;advanced oxidiation water treatment technology
[1]张爽,丁欣欣,闫良国. 改性水滑石类材料的制备及其吸附性能研究进展[J]. 中国粉体技术,2021,27(1):1-10.
ZHANG S, DING X X, YAN L G. Research progress on preparation and adsorption properties of modified layered double hydroxides[J]. China Powder Science and Technology, 2021,27(1):1-10.
[2]LIU X, YANG S, FENG T J,et al. Removal of amoxicillin from water by concrete-based hydrotalcites: efficiency and mechanism[J]. Process Safety and Environmental Protection, 2022, 163: 210-217.
[3]DWIASI D W, MUDASIR M, ROTO R. Ion exchange of benzoate in Ni-Al-benzoate layered double hydroxide by amoxicillin[J]. Open Chemistry,2019,17(1):1043-1049.
[4]王鹏瑞,杨丹, 张雪, 等. 钙铝和铁铝水滑石的制备及其吸附水中六价铬的性能[J]. 中国粉体技术, 2021, 27(3):59-67.
WANG P R,YANG D,ZHANG X,et al. Preparation of Ca-Al-and Fe-Al-layered double hydroxides and adsorptive removal C(r VI)in aqueous solutions[J]. China Powder Science and Technology, 2021, 27(3):59-67.
[5]LI M H, ZHAO L X, XIE M, et al. Singlet oxygen-oriented degradation of sulfamethoxazole by Li-Al-LDH activated peroxy-monosulfate[J]. Separation and Purification Technology,2022 ,290:120898.
[6]ZHU J Y,ZHU Y X,ZHOU W J. Cu-doped Ni-LDH with abundant oxygen vacancies for enhanced methyl 4-hydroxybenzoate degradation via peroxymonosulfate activation: key role of superoxide radicals[J].Journal of Colloid and Interface Science,2022,610: 504-517.
[7]MI X H, MA R, PU X C, et al. FeNi-layered double hydroxide( LDH)@biochar composite for, activation of peroxymonosulfate(PMS) towards enhanced degradation of doxycycline( DOX): characterizations of the catalysts, catalytic performances,degradation pathways and mechanisms[J]. Journal of Cleaner Production, 2022, 378: 134514.
[8]WU L Y,PENG B,LI Q Z,et al. Effects of Cu2+ incorporation on ZnAl-layered double hydroxide[ J]. New Journal of Chemistry,2020, 44(14): 5293-5302.
[9]刘定鹏,秦军,吕晴,等. 以粉煤灰为原料制备镁铝水滑石[J]. 硅酸盐学报,2020,48(8):1341-1347.
LIU D P, QIN J, LV Q, et al. Preparation of magnesium-aluminum hydrotalcite from fly ash[J]. Journal of the Chinese Ceramic Society,2020,48(8):1341-1347.
[10]AMANI-GHADIM A R,KHODAM F,ABER S,et al. Mesoporous CuZnAl-layered double hydroxide/graphene oxide nanohybrid as an energy storage electrode for supercapacitor application[J]. Bulletin of Materials Science,2021,44(1): 61.
[11]LEI X D, WANG L N,ZHAO X H, et al. Oriented CuZnAl ternary layered double hydroxide films: in situ hydrothermal growth and anticorrosion properties[J]. Industrial and Engineering Chemistry Research, 2013, 52(50): 17934-17940.
[12]ZHU J Y, ZHU Z L, ZHANG H, et al. Efficient degradation of organic pollutants by peroxymonosulfate activated with MgCuFe-layered double hydroxide[J]. RSC Advances, 2019,9(4): 2284-2291.
[13]HOU J D, LUO W, LUO S Z, et al. Facile synthesis of CuMAl(M=Cr,Mn,Zn,and Co) with highly dispersed Cu and tailorable surface acidity for efficient 2-methylpyrazine synthesis[ J]. RSC Advances, 2017, 7(77): 48662-48669.
[14]PAN C, FU L B, DING Y B,et al. Homogeneous catalytic activation of peroxymonosulfate and heterogeneous reductive regeneration of Co2+ by MoS2:the pivotal role of pH[ J]. Science of the Total Environment,2020,712:136447.
[15]SOLÍS R R, MENA I F,NADAGOUDA M N,et al. Adsorptive interaction of peroxymonosulfate with graphene and catalytic assessment via non-radical pathway for the removal of aqueous pharmaceuticals[J]. Journal of Hazardous Materials, 2020, 384: 121340.
[16]LI M K, HUANG F L, HU L, et al. Efficient activation of peroxymonosulfate by a novel catalyst prepared directly from electrolytic manganese slag for degradation of recalcitrant organic pollutes[J]. Chemical Engineering Journal, 2020, 401: 126085.
[17]LU Y Q, DING C S, GUO J, et al. Cobalt-doped ZnAl-LDH nanosheet arrays as recyclable piezo-catalysts for effective activation of peroxymonosulfate to degrade norfloxacin: non-radical pathways and theoretical calculation studies[J]. Nano Energy, 2023, 112: 108515.
[18]TANG Y W, KANG J, WANG M,et al. Catalytic degradation of oxytetracycline via FeVO4 nanorods activating PMS and the insights into the performance and mechanism[J]. Journal of Environmental Chemical Engineering, 2021, 9(5): 105864.
[19]LI Y J,LI J, PAN Y T, et al. Peroxymonosulfate activation on FeCo2S4 modified g-C3N4(FeCo2S4-CN):mechanism of singlet oxygen evolution for nonradical efficient degradation of sulfamethoxazole[J]. Chemical Engineering Journal, 2020, 384: 123361.
[20]王俊议,陈九玉,王鹏,等.层状双金属氢氧化物的原位改性及其吸附性能[J]. 中国粉体技术,2019,25(5):1-7.
WANG J Y, CHEN J Y, WANG P, et al. In situ modification of layered double metal hydroxide and its adsorption properties[J]. China Powder Science and Technology, 2019, 25(5): 1-7.
[21]ZHOU Y,FENG S,DUAN X M,et al. MnO2/UIO-66 improves the catalysed degradation of oxytetracycline under UV/ H2O2/PMS system[J].Journal of Solid State Chemistry,2021,300:122231.
[22]JI H D,DU P H,ZHAO D Y,et al. 2D/1D graphitic carbon nitride/titanate nanotubes heterostructure for efficient photocatalysis of sulfamethazine under solar light: catalytic“hot spots” at the rutile-anatase-titanate interfaces[J]. Applied Catalysis B: Environmental, 2020, 263: 118357.
[23]ZHU W T, YU X C, LIAO J Q, et al. Photocatalytic treatment of oxytetracycline hydrochloride from mariculture wastewater using bismuth oxide doped copper oxide[ J]. Environmental Engineering Science, 2022, 39(2): 146-154.
[24]李智颖, 顾傲天, 付豪, 等. ZIF-8@LDO多孔复合材料的合成及表征[J]. 中国粉体技术,2021, 27(6): 11-18.
LI Z Y, GU A T, FU H,et al. Synthesis and characterization of ZIF-8@ LDO porous composites[J].China Powder Science and Technology, 2021, 27(6): 11-18.
[25]GU A T,WANG P,CHEN K W, et al. Core-shell bimetallic Fe-Co MOFs to activated peroxymonosulfate for efficient degradation of 2-chlorophenol[J].Separation and Purification Technology, 2022,298:121461.
[26]GU A T,CHEN K W,ZHOU X Y,et al. Trimetallic MOFs-derived Fe-Co-Cu oxycarbide toward peroxymonosulfate activation for efficient trichlorophenol degradation via high-valent metal-oxo species[J]. Chemical Engineering Journal, 2023, 468: 143444.