三氯化铁改性活性炭(Fe3+-AC)对Cr(Ⅵ)的吸附研究

郝志刚1, 时培祥2, 吕永康3*

化工新型材料 ›› 2023, Vol. 51 ›› Issue (5) : 306 -309.

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化工新型材料 ›› 2023, Vol. 51 ›› Issue (5) : 306-309. DOI: 10.19817/j.cnki.issn1006-3536.2023.05.057
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三氯化铁改性活性炭(Fe3+-AC)对Cr(Ⅵ)的吸附研究

    郝志刚1, 时培祥2, 吕永康3*
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Study on the adsorption of Cr(Ⅵ) on activated carbon modified with FeCl3 (Fe3+-AC)

  • Hao Zhigang1, Shi Peixiang2, Lv Yongkang3
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摘要

工业化发展导致废水中含有大量重金属离子,去除重金属离子成为水质净化的研究热点。以活性炭(AC)为主体吸附剂,进行三氯化铁改性,制备出三氯化铁改性活性炭吸附剂(Fe3+-AC),通过X射线衍射(XRD)、红外光谱(FT-IR)和扫描电镜(SEM)对其结构进行表征。结果表明:三氯化铁已成功改性活性炭,改性后吸附剂Fe3+-AC孔径较AC有所增大,更有利于离子吸附。进一步探究Fe3+-AC对Cr(Ⅵ)的吸附能力,吸附时间为300min,吸附剂投加量为0.2g,pH为6时,吸附效果最好,在此条件下,Fe3+-AC对Cr(Ⅵ)的去除率接近90%,为后续循环吸附研究奠定基础。

Abstract

Industrial development has led to a large number of heavy metal ions in wastewater,and the removal of heavy metal ions has become a research focus of water purification.In this paper,activated carbon (AC) was used as the main adsorbent,and modified by ferric chloride to prepare ferric chloride modified activated carbon adsorbent (Fe3+-AC).Its structure was characterized by XRD,FT-IR and SEM.The results showed that the activated carbon had been successfully modified by ferric chloride,and the pore diameter of the modified adsorbent Fe3+-AC was larger than that of AC,which was more conducive to ion adsorption.The experiment further explored the adsorption capacity of Fe3+-AC for Cr(Ⅵ).The results showed that the adsorption effect was best when the adsorption time was 300 min,the dosage of adsorbent was 0.2g,and the pH was 6.Under this condition,the removal rate of Cr(Ⅵ) by Fe3+-AC was close to 90%,laying a foundation for subsequent cyclic adsorption research.

关键词

三氯化铁 / 改性活性炭 / Cr(Ⅵ) / 吸附性能

Key words

FeCl3 / modified activated carbon / Cr(Ⅵ) / adsorption performance

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三氯化铁改性活性炭(Fe3+-AC)对Cr(Ⅵ)的吸附研究[J]. 化工新型材料, 2023, 51(5): 306-309 DOI:10.19817/j.cnki.issn1006-3536.2023.05.057

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参考文献

[1] He B,Yun Z J,Shi J B,et al.Research progress of heavy metal pollution in China:sources,analytical methods,status,and toxicity[J].Chinese Science Bulletin,2013,58(2):134-140.
[2] Gui R Y,Hu Y Y,Li Q,et al.Effect of cultivation time on soil heavy metal accumulation and bioavailability in phyllostachys praecox stands[J].Pedosphere,2020,30(6):810-816.
[3] 陈振宇,王松,赵元艺.西藏多不杂铜矿区土壤与河床沉积物中重金属元素特征及其环境意义[J].地球科学与环境学报,2020,42(3):376-393.
[4] 钟福隆,范国荣,贺璐,等.活性炭吸附六价铬的研究进展[J].广州化工,2022,50(5):11-16.
[5] 周栋,高娜,高乐.工业含铬废水处理技术研究进展[J].中国冶金,2017,27(1):2-6.
[6] 于天宇,胡思雨.水体重金属污染现状及治理方法概述[J].建筑与预算,2019(6):75-78.
[7] 廖莹莹.改性活性炭对水溶液中六价铬离子吸附效果的测定与分析[J].湖北理工学院学报,2017,33(3):38-42,51.
[8] Han Y T,Cao X,Ouyang X,et al.Adsorption kinetics of magnetic biochar derived from peanut hull on removal of Cr(Ⅵ) from aqueous solution:effects of production conditions and particle size[J].Chemosphere,2016,145:336-341.
[9] 许少鹏,李晨.动水条件下平原河网沉积物对氨氮吸附热力学和动力学研究[J].环境科学导刊,2021,40(5):5-8.
[10] 叶志刚.不同变质程度的煤制活性炭孔隙结构分析[J].中国石油和化工标准与质量,2021,41(18):105-106.
[11] 朱建龙,徐伟杰,郭硕铖,等.水体重金属污染危害及治理技术[J].现代农业科技,2022(6):129-132.
[12] Zhang H,Zhang X H,Zhu Y N,et al.Adsorption of chromium(Ⅵ) from aqueous solution by agricultural waste derived activated carbon[J].Advanced Materials Research,2013,726-731:2100-2106.
[13] Yang J,Yu M,Chen W.Adsorption of hexavalent chromium from aqueous solution by activated carbon prepared from longan seed:kinetics,equilibriumand thermodynamics[J].Journal of Industrial & Engineering Chemistry,2015,21(21):414-422.
[14] 唐佳伟,师学璐,张春晖,等.硝酸改性煤基活性炭吸附处理垃圾渗滤液[J].矿业科学学报,2019,4(3):269-276.
[15] 魏思翔.水体重金属污染的危害与防治对策[J].化学工程与装备,2022(2):240-242.
[16] 张伊,杨金勇,高慧,等.过量重金属元素对动物生理毒性及作用机制的研究进展[J].饲料研究,2021,44(22):141-144.
[17] 吴文铭.紫外-可见分光光度计及其应用[J].生命科学仪器,2009,7(4):61-63.
[18] 库尔班江·努尔麦提,热娜古丽·阿不都热合曼.废水中Cr(Ⅲ)的吸附热力学和动力学研究进展[J].化工时刊,2022,36(2):22-25.

基金资助

国家自然科学基金面上项目(51778397)

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