| 842 | 6 | 55 |
| 下载次数 | 被引频次 | 阅读次数 |
为了提高SiO2/TiO2材料吸附?光催化氧化处理含氰废水的效果,使用重力自组装的聚苯乙烯微球(PS)作为硬模板,硅溶胶浸渍方法制备了大孔SiO2;进一步,使用溶胶凝胶法负载TiO2颗粒在SiO2载体上,制备了具有三维互联大孔结构的SiO2/TiO2复合材料,采用N2吸附?脱附、扫描电子显微镜(SEM)、X射线衍射光谱分析(XRD)、傅氏转换红外光谱分析(FTIR)等手段对其进行表征。采用高压汞灯作为光源,探讨了TiO2颗粒负载量(质量分数)、材料用量、催化时间和吸附时间对含氰废水降解效果的影响。实验结果表明:TiO2颗粒负载量为10%,处理100 mL含氰废水材料使用量为0.35 g,经过1.0 h暗吸附和4.0 h光照后,总氰化物、铜、铁和锌的去除率分别为98.79%、99.10%、100.00%和92.26%。材料具有较强的热稳定性和重复利用性。吸附–催化机理研究结果表明:好的吸附性能可以促进催化分解过程,氧气捕获电子是提高催化效果的主要因素;氰根降解为无毒的氮氧化物和碳氧化物,金属以沉淀形式去除。
Abstract:Introduction Photocatalytic oxidation degradation of cyanide is an effective technology to treat cyanide wastewater.TiO2/SiO2 is a common catalyst.A preliminary research indicates that the pore structure of SiO2 has a certain influence on the degradation of cyanide and the removal of zinc and copper.If TiO2 particles are only loaded on the surface of mesoporous SiO2,the contact between the surface of SiO2 and the target substance in wastewater is reduced,thus affecting its adsorption performance.In this study,a macroporous SiO2 was prepared,and TiO2 particles were loaded on the surface and in three-dimensional interconnected channels of Si O2,thus increasing the adsorption sites on the surface of SiO2 and improving the adsorption performance of target pollutants,and enhancing its efficiency of treating cyanide in wastewater.Methods Gravity self-assembled polystyrene microspheres (PS) were used as hard templates,impregnated in silica sol for 8.0 h,dried in an oven at 60℃,and roasted in a Muffle furnace at 550℃for 10 h to obtain macroporous SiO2.SiO2/TiO2 precursors were prepared by a sol-gel method and roasted at 500℃for 90 min.SiO2/TiO2 composites with a three-dimensional interconnected macroporous structure were prepared.The wastewater and materials were placed and mixed in a beaker in a certain proportion.After stirring magnetically for a period of time,a small air pump was used to pump air into the bottom of the beaker at room temperature,and a high-pressure mercury lamp was used as the light source for photocatalytic oxidation of the wastewater.The effects of TiO_2particle loading mass,catalyst dosage,catalytic time,adsorption time on the treatment of cyanide wastewater were investigated.N_2adsorption-desorption,scanning electron microscopy (SEM),X-ray diffraction spectroscopy (XRD),Fourier transform infrared spectroscopy (FTIR) and other characterization techniques were used to determine the structural characteristics of the material and its adsorption-catalytic degradation mechanism.Results and discussion PS presents a monodisperse,independent and spherical structure with a particle size of 1.65μm.PS templates are arranged in an orderly manner,independent of each other but closely connected,and they do not show a large continuous structure.SiO2 is a three-dimensional ordered macroporous structure with a pore size of 1.2μm,which is smaller than the diameter of microspheres,indicating that the skeleton structure shrinks during the roasting process.SiO2 particle is broken mainly because of mechanical grinding.The long distance of the channels is orderly,the large holes are uniform and interconnected through small holes.The sizes of the small holes are 170–220 nm,the holes are formed due to the accumulation of microspheres.TiO_2particles are fragmented and loaded on the concave surface of SiO2.The particle size of TiO2 is uneven,and smaller than the pore size of SiO2.TiO2 particles are evenly dispersed on the surface of SiO2 or in the physical structure of the cavity,which eliminates the agglomeration of TiO2.N2 adsorption-desorption test shows that the SiO2/TiO2 material has a large pore structure,and the specific surface area is increased by 5 times,compared with TiO2 nanoparticles.The thermogravimetric curve shows that the materials have less weight loss at 250–800℃.The X-ray diffraction pattern of the material shows that the diffraction peak intensity of SiO2 loading with TiO2 particles decreases.The experimental results show that the degradation efficiency of total cyanide and the removal efficiencies of copper,iron and zinc are 98.79%,99.10%,100.00%and 92.26%,respectively,under the optimum conditions (i.e.,10%of TiO2 particle loading mass,0.35 g of the material mass when treating 100 mL cyanide wastewater,1.0 h of dark adsorption and4.0 h of illumination time).The material was regenerated in a sulfuric acid solution by ultrasonic treatment.Under the same experimental conditions,the total cyanide degradation efficiency is reduced by 4.95%after three catalytic cycles,indicating that the material has strong stability and reusability.The XRD results before and after adsorption-catalysis show that ZnO,CuSCN,Cu_2Fe(CN)6 and Fe_2O3 are adsorbed on the surface of the material.The FTIR results show that a characteristic peak of C≡N appears on the surface of the material after 1-h adsorption and a characteristic peak of NO3~–appears after 4-h catalysis.The EDS of the material after 1-h adsorption shows that cyanide is adsorbed on the surface of the material,and metal ions are uniformly distributed on the surface of the material.The EDS of the material after 4-h illumination shows that the metal content is higher than that after 1-h adsorption,and the distribution of Si and Ti is uniformly crossed.The results of free radical quenching experiment show that electron capture by oxygen is the main factor to improve the catalytic effect.Conclusions Macroporous SiO2/TiO2 materials were prepared by PS self-assembly template,impregnation,roasting and loading,which were used to treat cyanide wastewater.Under optimal experimental conditions,the degradation efficiency of total cyanide and the removal efficiencies of copper,iron and zinc were 98.79%,99.10%,100.00%and 92.26%,respectively.The three-dimensional ordered pore structure of macroporous SiO2 made TiO2 particles evenly dispersing on its surface and inside the cross-linked pore.The mechanism indicated that the cyanide was degraded into non-toxic nitrogen oxides and carbon oxides,and the metals were removed by precipitation.
[1] CHEN Y, SONG Y H, CHEN Y, et al. Comparative experimental study on the harmless treatment of cyanide tailings through slurry electrolysis[J]. Sep Purif Technol, 2020, 251:117314.
[2]马平杰.金矿尾矿及废水中氰化物的处理研究进展[J].中国新技术新产品, 2017(3):109–110.MA Pingjie. N Technol N Prod China, 2017(3):109–110.
[3]黄爱华.提金含氰废水处理工艺研究现状及发展趋势分析[J].黄金科学技术, 2014, 22(2):83–89.HUANG Aihua. Gold Sci Technol, 2014, 22(2):83–89.
[4]邱廷省,郝志伟,成先雄.含氰废水处理技术评述与展望[J].江西冶金, 2002, 22(3):25–29.QIU Tingsheng, HAO Zhiwei, CHENG Xianxiong. Jiangxi Metall,2002, 22(3):25–29.
[5]栾鑫宇,朱佳,张金松.混凝沉淀处理综合电镀废水试验探究[J].辽宁化工, 2020, 49(4):337–340.LUAN Xinyu, ZHU Jia, ZHANG Jinsong. Liaoning Chem Ind, 2020,49(4):337–340.
[6]张曼曼,冯占立,王军强,等.黄金湿法冶炼含氰废水处理研究进展[J].化学工业与工程, 2019, 36(1):2–9.ZHANG Manman, FENG Zhanli, WANG Junqiang, et al. Chem Ind Eng, 2019, 36(1):2–9.
[7]陈志达,樊振江.离子交换法处理含氰废水[J].环境保护, 1982,10(2):8–11.CHEN Zhida, FAN Zhenjiang. Environ Prot, 1982, 10(2):8–11.
[8]龚喜林,屈伟华,李勤.酸性液氯法除氰工业实践[J].黄金, 1992,13(8):51–57.GONG Xilin, QU Weihua, LI Qin. Gold, 1992, 13(8):51–57.
[9]许芙蓉,刘杰.对因科SO2—空气法脱除氰化物的研究[J].黄金,1985, 6(4):33–36.XU Furong, LIU Jie. Gold, 1985, 6(4):33–36.
[10] PARGA J R, COCKE D L. Oxidation of cyanide in a hydrocyclone reactor by chlorine dioxide[J]. Desalination, 2001, 140(3):289–296.
[11] CASTELLANOS-LEAL E L, ACEVEDO-PE?A P, GüIZAARGüELLO V R, et al. N and F codoped TiO2 thin films on stainless steel for photoelectrocatalytic removal of cyanide ions in aqueous solutions[J]. Mat Res, 2017, 20(2):487–495.
[12] DAGHRIR R, DROGUI P, ROBERT D. Modified Ti O2 for environmental photocatalytic applications:A review[J]. Ind Eng Chem Res, 2013, 52(10):3581–3599.
[13] NKAMBULE T I, KUVAREGA A T, KRAUSE R W M, et al.Synthesis and characterisation of Pd-modified N-doped TiO2 for photocatalytic degradation of natural organic matter(NOM)fractions[J]. Environ Sci Pollut Res Int, 2012, 19(9):4120–4132.
[14] WANG X J, WU Z, WANG Y, et al. Adsorption-photodegradation of humic acid in water by using ZnO coupled TiO2/bamboo charcoal under visible light irradiation[J]. J Hazard Mater, 2013, 262:16–24.
[15] TAKASHI K, YASUSHI I, HIROMI Y. Photocatalytic properties of Ti O2-loaded porous silica with hierarchical macroporous and mesoporous architectures in the degradation of gaseous organic molecules[J]. Catal Today, 2019, 332:222–226.
[16] COSTA J A S, DE JESUS R A, SANTOS D O, et al. Synthesis,functionalization, and environmental application of silica-based mesoporous materials of the M41S and SBA-n families:A review[J]. J Environ Chem Eng, 2021, 9(3):105259.
[17]张亚莉,杨静,于先进,等.二氧化硅/二氧化钛催化吸附材料的制备及处理含氰废水研究[J].湿法冶金, 2014, 33(4):313–316.ZHANG Yali, YANG Jing, YU Xianjin, et al. Hydrometall China,2014, 33(4):313–316.
[18] BAEISSA E S. Photocatalytic removal of cyanide by cobalt metal doped on TiO2–SiO2 nanoparticles by photo-assisted deposition and impregnation methods[J]. J Ind Eng Chem, 2014, 20(5):3761–3766.
[19] PAN Y B, ZHANG Y L, HUANG Y G, et al. Enhanced photocatalytic oxidation degradability for real cyanide wastewater by designing photocatalyst GO/TiO2/ZSM-5:Performance and mechanism research[J]. Chem Eng J, 2022, 428:131257.
[20] YANG Z, ZHANG Y L, HUANG Y G, et al. Enhanced photocatalytic reaction and mechanism for treating cyanide-containing wastewater by silicon-based nano-titania[J]. Hydrometallurgy, 2020, 198:105512.
[21]张洋,张亚莉,黄耀国,等. Mn-N共掺杂Ti O2/ZSM-5复合材料及光催化降解含氰废水[J].中国有色金属学报, 2023, 33(1):191–202.ZHANG Yang, ZHANG Yali, HUANG Yaoguo, et al. Chin J Nonferrous Met, 2023, 33(1):191–202.
[22] PAN Y B, ZHANG Y L, HUANG Y G, et al. Synergistic effect of adsorptive photocatalytic oxidation and degradation mechanism of cyanides and Cu/Zn complexes over TiO2/ZSM-5 in real wastewater[J]. J Hazard Mater, 2021, 416:125802.
[23] WEI P H, ZHANG Y L, HUANG Y G, et al. Structural design of SiO2/TiO2 materials and their adsorption-photocatalytic activities and mechanism of treating cyanide wastewater[J]. J Mol Liq, 2023, 377:121519.
[24] WANG L J, FAN H L, SHANGGUAN J, et al. Design of a sorbent to enhance reactive adsorption of hydrogen sulfide[J]. ACS Appl Mater Interfaces, 2014, 6(23):21167–21177.
[25]房洪杰,刘慧,闫芳,等.以三聚氰胺甲醛微球为模板制备介孔二氧化硅和二氧化钛空心微球[J].硅酸盐学报, 2015, 43(2):215–221.FANG Hongjie, LIU Hui, YAN Fang, et al. J Chin Ceram Soc, 2015,43(2):215–221.
[26]王浩,赵大方,李效东,等.有序大孔材料的研究进展[J].硅酸盐学报, 2006, 34(1):107–113.WANG Hao, ZHAO Dafang, LI Xiaodong, et al. J Chin Ceram Soc,2006, 34(1):107–113.
[27]孙秀丽,陈爱平,吕慧,等. SBA-15/Ni/TiO2/CNTs复合材料的制备及其光催化性能[J].化工学报, 2014, 65(9):3718–3723.SUN Xiuli, CHEN Aiping, LüHui, et al. CIESC J, 2014, 65(9):3718–3723.
[28]王子帅,王耀强,肖刚,等.磁性纳米Fe3O4@TiO2可见光下光催化还原Cr(Ⅵ)[J].化工学报, 2019, 70(10):4062–4071.WANG Zishuai, WANG Yaoqiang, XIAO Gang, et al. CIESC J, 2019,70(10):4062–4071.
[29] NAYL A A, AHMED I M, ABD-ELHAMID A I, et al. Selective sorption of 134Cs and 60Co radioisotopes using synthetic nanocopper ferrocyanide-SiO2 materials[J]. Sep Purif Technol, 2020, 234:116060.
[30] LI Y, GUO Y, LIU Y Z. Synthesis of high purity TiO2 nanoparticles from Ti(SO4)2 in presence of EDTA as complexing agent[J]. China Particuology, 2005, 3(4):240–242.
[31] SU Y Y, TENG Z G, YAO H, et al. A multifunctional PB@mSiO2-PEG/DOX nanoplatform for combined photothermalchemotherapy of tumor[J]. ACS Appl Mater Interfaces, 2016, 8(27):17038–17046.
[32] SONG H O, ZHOU Y, LI A M, et al. Selective removal of nitrate from water by a macroporous strong basic anion exchange resin[J].Desalination, 2012, 296:53–60.
[33] RAJ K A, VISWANATHAN B. Single-step synthesis and structural study of mesoporous sulfated titania nanopowder by a controlled hydrolysis process[J]. ACS Appl Mater Interfaces, 2009, 1(11):2462–2469.
[34] PAN Y B, ZHANG Y L, HUANG Y G, et al. Functional Ag-doped coralloid titanosilicate zeolite(cts-Ag)for efficiently catalytic and photodegradative removal of free cyanides and copper/zinc-cyanide complexes in real wastewater[J]. J. Alloys Compd., 2022, 926:166848.
基本信息:
DOI:10.14062/j.issn.0454-5648.20230324
中图分类号:O643.36;O647.3;X703
引用信息:
[1]尉鹏海,张亚莉,黄耀国,等.三维大孔SiO_2/TiO_2复合材料制备及吸附-光催化降解含氰废水[J].硅酸盐学报,2024,52(01):98-108.DOI:10.14062/j.issn.0454-5648.20230324.
基金信息:
国家自然科学基金(51974180)
2023-12-08
2023-12-08
2023-12-08