ISSN 1008-5548

CN 37-1316/TU

最新出版

陶瓷蜂窝净化材料的制备及吸附性能

Preparation of honeycomb ceramics purification materials and their adsorption performance


付 琳1 ,姬文晋1 ,何家俊1 ,黄超强1 ,李永峰1,2 ,窦永深2

(1. 广东工业大学 轻工化工学院,广东 广州 510006;2. 佛山市顺德区金磊环保科技有限公司,广东 佛山 528308)


引用格式:

付琳,姬文晋,何家俊,等. 陶瓷蜂窝净化材料的制备及吸附性能[J]. 中国粉体技术,2024,30(3):170-182.

FU L, JI W J, HE J J,et al. Preparation of honeycomb ceramics purification materials and their adsorption performance[J].China Powder Science and Technology,2024,30(3):170−182.

DOI:10.13732/j.issn.1008-5548.2024.03.015

收稿日期:2023-11-15,修回日期:2023-12-18,上线日期:2024-04-16。

基金项目:国家自然科学基金项目,编号:22278086。

第一作者简介:付琳(2000—),女,硕士生,研究方向为有机污染物净化治理。E-mail:1639545624@qq. com。

通信作者简介:李永峰(1976— ),男,教授,博士,广州市珠江科技新星,硕士生导师,研究方向为大气污染物净化治理。E-mail:gdliyf@gdut. edu. cn。


摘要:【目的】 为了去除三甲胺异味污染物,分析不同改性方法对陶瓷蜂窝吸附净化三甲胺性能的影响。【方法】 采用涂覆工艺,在陶瓷蜂窝基底上负载金属离子活性涂层制备整体式净化材料,以三甲胺的吸附容量作为净化评价指标,研究涂覆工艺参数优化和金属离子改性规律。【结果】 陶瓷蜂窝净化材料的最优制备工艺条件为:胶黏剂类型为铝溶胶,添加的尿素浓度为0. 9 mol/L,热处理温度为120~150℃,添加的金属离子为Ca2+ 和Fe3+ 、浓度为0. 3 mol/L。用Ca2+ 离子改性的陶瓷蜂窝净化材料三甲胺饱和吸附容量可达到368 mg/g,且在多次热再生后重复使用时净化性能保持不变;制备规模放大10倍后,所制得的陶瓷蜂窝材料也能保持三甲胺吸附净化性能。【结论】 金属离子改性陶瓷蜂窝净化材料可有效去除三甲胺等异味污染物,具有饱和吸附量高、可多次重复使用等特点;净化材料制备规模放大后的净化性能保持重现性,具备规模化生产潜质。

关键词:净化材料;三甲胺;陶瓷蜂窝;涂覆工艺

Abstract

Objective Trimethylamine is a toxic, nitrogen-containing volatile organic compound, and commonly recognized as a indoor odor pollutant with pungent odor contributing significantly to external air pollution. Microbiota easily metabolizes trimethylamine pollutants,leading to the formation of trimethylamine-n-oxide,closely associated with various cardiovascular diseases.Therefore,there is an urgent need to purify indoor air from odor pollutants for people's well-being. In this paper,in order to remove trimethylamine odor pollutants,the effects of different modification methods on the adsorption and purification performance of ceramic honeycomb purification materials for trimethylamine was fully analyzed, and the goal of efficient purification of trimethylamine odor pollutants was finally achieved.

Methods A coating technology was used to directly load metal ion active coatings on ceramic honeycomb substrates to prepare integrated chemical purification materials:firstly,the ceramic honeycomb substrate underwent pretreatment,including pickling,ultrasonic,high temperature calcination;then,the pre-treated substrate was dipped into the mixed coating slurry consisting of aluminum sol,urea and metal ion salt for 10 h; finally,the coating sample was taken out,purged the residual slurry and dried at a temperature range of 100 to 200 ℃ for 10h to obtain the monolithic ceramic honeycomb purification material modified with different metal ions.The static adsorption capacity of trimethylamine was used as the evaluation index for the purification efficiency of odor pollutants,and the optimization of coating process parameters including adhesive type,concentration of added urea,thermal treatment temperature and the modification law of metal ions considering different types and concentration of metal ions,were studied in detail.

Results and Discussion The adsorption effect of pure ceramic honeycomb substrate on trimethylamine is not evident. Under the action of different adhesives modified ceramic honeycomb, the trimethylamine adsorption capacity curve illustrates that when the adhesive is aluminum sol, the modified ceramic honeycomb material exhibits the highest adsorption performance for trimethylamine,followed by silica sol and water.The adsorption performance of the modified ceramic honeycomb material for trimethylamine improved with an increase of the concentration of the pore making agent urea. However,when the concentration of the urea substance was 1. 2 mol/L,the adsorption capacity of the modified ceramic honeycomb material for trimethylamine did not show a significantly improvement. Simultaneously,at different heat treatment temperatures, the adsorption capacity of trimethylamine on ceramic honeycomb materials initially increased and then declined with the increase of temperature. At a heat treatment temperature from 120 to 150 ℃,the ceramic honeycomb material exhibits optimaladsorption performance for trimethylamine.The sequence of adsorption capacities for different metal ions,ranked fromhigh to low,is Ca2+,Fe3+,Zn2+,Cu2+ and Mg2+,respectively. The adsorption capacities of modified Ca2+ and Fe3+ ceramic honeycomb materials for trimethylamine are 368 mg/g and 341 mg/g,respectively. As the concentration of metal ions increases,the adsorption capacity of ceramic honeycomb material for trimethylamine initially rises and then declines. When the concentration of metal ions is 0.3 mol/L,the modified ceramic honeycomb material exhibits optimal adsorption performance for trimethylamine. Overall,the optimum preparation conditions for ceramic honeycomb purification materials can be selected as follows:choosing aluminum sol as the adhesive,setting the concentration of urea additive at 0. 9 mol/L,selecting a heat treatment temperature between120 and 150 ℃,using Ca2+ and Fe3+ as metal ion additives,and maintaining a concentration of metal ion additive at 0. 3 mol/L.Compared to pure ceramic honeycomb materials,the metal-ion-modified ceramic honeycomb purification materials,coated with aluminum sol and urea additive,significantlyimprove the adsorption capacity of trimethylamine. The adsorption capacity of trimethylamine can be increased to hundreds of times when compared to the unmodified material. Furthermore, even after thermal regeneration and repeated use of the same purification material, the decrease in the adsorption performance of trimethylamine is minimal. Additionally, upon scaling up the preparation by tenfold,the static adsorptioncapacity of the entire chemical purification material,obtained by the same preparation process for trimethylamine pollutants,remains consistent with that of the small-scale purification material.Overall,the saturation adsorption capacity of Ca2+ modified ceramic honeycomb material for trimethylamine reaches 368 mg/g. Even after repeated thermal regeneration, the purification performance of ceramic honeycomb material for trimethylamine remains unchanged. Simultaneously, the ceramic honeycomb material obtained after a tenfold enlargement of a single batch can still maintain the adsorption and purification properties of trimethylamine. These results indicates that the preparation method is simple, the adsorption properties are commendable,and the obtained ceramic honeycomb purification material has good potential for large-scale production.

Conclusion The as-prepared ceramic honeycomb purification material modified by metal ions proves to behighly effective in removing odor pollutants such as trimethylamine. Itboaststhe advantages such as high saturated adsorption capacity and the ability for repeated use. Moreover,the ceramic honeycomb material has good amplification repeatability and has the potential of large-scale production,allowing it well-suited for widespread application in the field of odor air purification.

Keywords:purification material;trimethylamine;ceramic honeycomb;coating process


参考文献(References)

[1]徐彦鹏,吕道飞,郭雅欣,等. 三甲胺移除技术的研究进展[J]. 广州化工,2023,51(11):8-10.XU Y P, LV D F, GUO Y X, et al. Research progress of trimethylamine removal technology[J]. Guangzhou Chemical Industry,2023,51(11):8-10.

[2]DAI L,MASSY Z A, STENVINKEL P, et al. The association between TMAO, CMPF,and clinical outcomes in advanced chronic kidney disease: results from the European QUALity (EQUAL) study[J]. The American Journal Clinical Nutrition,2022,116(6):1842-1851.

[3]LAI X X, ZHOU X Y, ZHANG H L, et al. Toluene oxidation over monolithic MnOx/La-Al2O3 catalyst prepared by a CTAB-assisted impregnation method[J]. Applied Surface Science,2020,526:146714.

[4]PASCUAL C, AKMIRZA I, PEREZ R, et al. Trimethylamine abatement in algal-bacterial photobioreactors[J]. Environmental Science and Pollution Research International,2020,27(9):9028-9837.

[5]FU L, LIU Y, HAO S, et al. Preparation of magnetic composite adsorbents from laterite nickel ore for organic amineremoval[J]. Arabian Journal of Chemistry,2021,14(2):102933.

[6]YAN C, ZHONG M, HAN J Q, et al. Efficient degradation of trimethylamine in gas phase by petal-shaped Co-MoS2catalyst in the photo-electrochemical system[J]. Chemical Engineering Journal,2021,405:127034.

[7]HAN J Q, LIU L F, LU X G. Sustainable and continuous removal of trimethylamine in a bio-photoelectrochemical reactorusing g-C3N4/TiO2 photocathode with power generation[J]. Journal of Chemical Technology & Biotechnology,2021,97(1):218-227.

[8]LI X Q, ZHANG L, YANG Z Q, et al. Adsorption materials for volatile organic compounds (VOCs) and the key factors for VOCs adsorption process: a review[J]. Separation and Purification Technology,2020,235:116213.

[9]SAARELA T, LAFDANI E K, LAURÉN A, et al. Biochar as adsorbent in purification of clear-cut forest runoff water:adsorption rate and adsorption capacity[J]. Biochar,2020,2(2):227-237.

[10]JIANG L, YANG N, ZHU J, et al. Preparation of monolithic Pt-Pd bimetallic catalyst and its performance in catalytic combustion of benzene series[J]. Catalysis Today,2013,216:71-75.

[11]TOMAŠIĆ V, JOVIĆ F. State-of-the-art in the monolithic catalysts/reactors[J]. Applied Catalysis A:General,2006,311:112-121.

[12]ZHAO Q, ZHENG Y F, SONG C F, et al. Novel monolithic catalysts derived from in-situ decoration of Co3O4 and hierarchical Co3O4@MnOx on Ni foam for VOC oxidation[J]. Applied Catalysis B: Environmental,2020,265:11852.

[13]HOU Y J, MA J, SUN Z Z, et al. Degradation of benzophenone in aqueous solution by Mn-Fe-K modified ceramic honeycomb-catalyzed ozonation[J]. Journal Environment Science (China),2006,18(6):1065-1072.

[14]YU J, LI X Y, XU Z H, et al. NaOH-modified ceramic honeycomb with enhanced formaldehyde adsorption and removal performance[J]. Environment Science Technology,2013,47(17):9928-9933.

[15]SANTOS D F M, SOARES O S, FIGUEIREDO J L, et al. Optimization of the preparation conditions of cordierite honeycomb monoliths washcoated with cryptomelane-type manganese oxide for VOC oxidation[J]. Environment Technology,2021,42(16):2504-2515.

[16]HOSSAIN M M, MOK Y S, NGUYEN D B, et al. Nonthermal plasma in practical-scale honeycomb catalysts for the removal of toluene[J]. Journal Hazardous Materials,2021,404:123958.

[17]CHAI W S, ZHANG L, LI W Z, et al. Preparation of plastics and foaming agent-free and porous bamboo charcoal based composites using sodium silicate as adhesives[J]. Materials (Basel),2021,14(10):2468.

[18]赵晓敏,陈代荣,焦秀玲,等. 溶胶组成对氧化铝纤维微观结构及性质的影响[J]. 广州化工,2019,47(9):68-75.ZHAO X M, CHEN D R, JIAO X L, et al. Effect of sol composition on microstructure and properties of alumina fiber[J].Guangzhou Chemical Industry,2019,47(9):68-75

[19]刘羽祚,李喜德,李菊英,等. 造孔剂(NH42CO3和尿素含量对TiAl多孔材料性能的影响[J]. 粉末冶金材料科学与工程,2019,24(3):255-260.LIU Y Z, LI X D, LI J Y, et al. Effect of pore-forming agent (NH42CO3and urea content on properties of TiAl porous material[J]. Powder Metallurgy Materials Science and Engineering,2019,24(3):255-260.

[20]同帜,李岩,闫笑,等 . 3 种不同造孔剂对黄土基陶瓷膜支撑体性能的分析研究[J]. 功能材料,2020,51(2):2182-2187.TONG Z, LI Y, YAN X, et al. Analysis of properties of three different pore-forming agents on loess based ceramic mem⁃brane support[J]. Functional Materials,2020,51(2):2182-2187.

[21]薛红丹,董国君,龚凡,等. 选择性催化还原(SCR)脱除NOx的实验研究[J].应用科技,2006(3):50-52.XUE H D, DONG G J, GONG F, et al. Experimental study on removal of NOx by selective catalytic reduction(SCR)[J].Applied Science and Technology,2006(3):50-52.

[22]CACUA K, ORDOÑEZ F, ZAPATA C, et al. Surfactant concentration and pH effects on the zeta potential values of alumina nanofluids to inspect stability[J]. Colloids and Surfaces A: Physicochemical and Engineering Aspects,2019,583:123960.