nav emailalert searchbtn searchbox tablepage yinyongbenwen piczone journalimg journalInfo journalinfonormal searchdiv searchzone qikanlogo popupnotification paper paperNew
2022, 09, 162-172
粉煤灰浮选精炭制备活性炭吸附溶液中Cu2+
基金项目(Foundation): 国家水体污染控制与治理科技重大专项(2017ZX0730100500303)
邮箱(Email):
DOI:
发布时间: 2022-08-30
出版时间: 2022-08-30
移动端阅读
摘要:

粉煤灰浮选得到的精炭具有灰分含量低(Ad=17.85%)、碳含量高(Cd=77.53%)的特点,是活性炭制备的廉价碳源。采用KOH活化法对浮选精炭进行活化,可以得到碘吸附值1 140.78 mg/g、亚甲基蓝吸附值140.00 mg/g、比表面积853.75 m2/g的优质活性炭。最佳的活化条件为:碱炭比3.0、活化温度800℃、活化时间60 min。红外光谱分析、BET比表面分析和扫描电子显微镜分析显示,制备的活性炭中含氧活性基团较多、孔隙发达,特别是2 nm以下的微孔丰富,微孔孔容占比48.30%,活性炭平均孔径2.33 nm。该活性炭对溶液中Cu2+的吸附性能良好,在投加量为2.5 g/L、pH=5.0、吸附温度25℃、吸附平衡时间120 min的条件下,初始浓度分别为50、75、100 mg/L时,Cu2+去除率分别达到99.70%、93.61%、81.67%。吸附机理分析表明,Cu2+在活性炭表面的吸附以化学吸附为主,符合Langmuir单分子层等温吸附模型。本研究为水处理用优质活性炭的低成本制备提供了一条新的技术途径。

Abstract:

The refined carbon obtained by fly ash flotation has the characteristics of low ash content(Ad=17.85%)and high carbon content(Cd=77.53%),it is a cheap carbon source for preparation of activated carbon.High quality activated carbon with iodine adsorption value of 1 140.78 mg/g, methylene blue adsorption value of 140.00 mg/g, and specific surface area of 853.75 m2/g can be obtained by activating flotation refined carbon by KOH activation method.The optimum activation conditions include alkali carbon ratio of 3.0,activation temperature of 800 ℃,and activation time of 60 min.The results of infrared spectroscopic analysis, BET specific surface analysis, and scanning electron microscope analysis show that the activated carbon prepared by flotation refined carbon contains many oxygen-containing active groups, the pores are developed, especially the pores below 2 nm are abundant.The micropores pore volume accounts for 48.30%,and the average pore diameter of activated carbon is only 2.33 nm.The activated carbon has good adsorption performance for Cu2+in solution.When the dosage is 2.5 g/L,pH=5.0,adsorption temperature is 25 ℃,adsorption equilibrium time is 120 min, and initial concentration is 50,75,and 100 mg/L respectively, the removal rate of Cu2+can reach 99.70%,93.61% and 81.67% respectively.The adsorption mechanism analysis shows that adsorption of Cu2+on the surface of activated carbon is mainly chemical adsorption, which conforms to the Langmuir monolayer isothermal adsorption model.This study can provide a new technical approach for low-cost preparation of high-quality activated carbon for water treatment.

参考文献

[1] VARDHAN K H,KUMAR P S,PANDA R C.A review on heavy metal pollution,toxicity and remedial measures:Current trends and future perspectives[J].Journal of Molecular Liquids,2019,290:111197.DOI:10.1016/j.molliq.2019.111197.

[2] BRIFFA J,SINAGRA E,BLUNDELL R.Heavy metal pollution in the environment and their toxicological effects on humans[J].Heliyon,2020,6(9):e4691.DOI:10.1016/j.heliyon.2020.e04691.

[3] TONG K S,KASSIM M J,AZRAA A.Adsorption of copper ion from its aqueous solution by a novel biosorbent Uncaria gambir:Equilibrium,kinetics,and thermodynamic studies[J].Chemical Engineering Journal,2011,170(1):145-153.

[4] 杨海,黄新,林子增,等.离子交换法处理重金属废水的研究进展[J].应用化工,2019,48(7):1675-1680.YANG H,HUANG X,LIN Z Z,et al.Research progress in the treatment of heavy metal wastewater by ion exchange[J].Applied Chemical Industry,2019,48(7):1675-1680.

[5] ZHANG Y,DUAN X M.Chemical precipitation of heavy metals from wastewater by using the synthetical magnesium hydroxy carbonate[J].Water Science and Technology,2020,81(6):1130-1136.

[6] GIRI A K,CORDEIRO M N D S.Heavy metal ion separation from industrial wastewater using stacked graphene membranes:A molecular dynamics simulation study[J].Journal of Molecular Liquids,2021,338:116688.DOI:10.1016/j.molliq.2021.116688.

[7] BOBADILLA M C,GONZALEA-MARCOS A,VERGARA E,et al.Bioremediation of waste water to remove heavy metals using the spent mushroom substrate of agaricus bisporus[J].Water,2019,11(3):454.DOI:10.3390/w11030454.

[8] 朱亦珺.生物吸附法处理污泥中重金属镍[J].有色金属工程,2019,9(7):104-108.ZHU Y J.Disposal of sludge containing nickel heavy metals by biosorption[J].Nonferrous Metals Engineering,2019,9(7):104-108.

[9] 黄兆琴,胡淋潮,祁本武,等.老化生物炭表面性质的变化及其对土壤吸附Cu(Ⅱ)的影响[J].有色金属(冶炼部分),2020(12):80-88.HUANG Z Q,HU L C,QI B W,et al.Changes of biochar properties during aging process and its effect on soil adsorptionbehavior of Cu(Ⅱ)[J].Nonferrous Metals (Extractive Metallurgy),2020(12):80-88.

[10] DEMIRBAS E,DIZGE N,SULAK M T,et al.Adsorption kinetics and equilibrium of copper from aqueous solutions using hazelnut shell activated carbon[J].Chemical Engineering Journal,2009,148(2/3):480-487.

[11] EMENIKE P G C,OMOLE D O,NGENE B U,et al.Assessment of KOH-activated unripe Musa paradisiaca peel for adsorption of copper from aqueous solution[J].Cogent Engineering,2017,4(1):1376488.DOI:10.1080/23311916.2017.1376488.

[12] AHMAD M,WANG J Q,XU J,et al.Magnetic tubular carbon nanofibers as efficient Cu(Ⅱ)ion adsorbent from wastewater[J].Journal of Cleaner Production,2019,252:119825.DOI:10.1016/j.jclepro.2019.119825.

[13] 袁敏,黄小钟,王崇光,等.铜绿微囊藻对水中铜离子的吸附研究[J].当代化工研究,2017(4):11-12.YUAN M,HUANG X Z,WANG C G,et al.Study on the adsorption of copper ions by Microcystis aeruginosa in water[J].Modern Chemical Research,2017(4):11-12.

[14] 陈尚,刘青,赵世强,等.树脂吸附铜锌离子的数值模拟[J].有色金属科学与工程,2019,10(2):6-12.CHEN S,LIU Q,ZHAO S Q,et al.Mathematical simulation on adsorption of zinc ion and copper ion with resin[J].Nonferrous Metals Science and Engineering,2019,10(2):6-12.

[15] 于先进,张亚莉,房涛,等.离子交换法处理氰化贫液中铜的工艺及动力学[J].有色金属(冶炼部分),2014(5):8-11.YU X J,ZHANG Y L,FANG T,et al.Process and kinetics of copper adsorption from cyaniding barren solution with ion exchange resin[J].Nonferrous Metals(Extractive Metallurgy),2014(5):8-11.

[16] HARJA M,BUEMA G,LUPU N,et al.Fly ash coated with magnetic materials:Improved adsorbent for Cu(Ⅱ) removal from wastewater[J].Materials,2021,14(1):63.DOI:10.3390/ma14010063.

[17] 王艳,马梦娟,宋朝霞,等.芝麻秆制备的活性炭对废水中铜离子的吸附[J].河南工程学院学报(自然科学版),2018,30(1):41-44.WANG Y,MA M J,SONG Z X,et al.Adsorption of copper ions using activated carbon prepared from sesame stalk[J].Journal of Henan University of Engineering(Natural Science Edition),2018,30(1):41-44.

[18] IMAMOGLU M,TEKIR O.Removal of copper(Ⅱ)and lead(Ⅱ)ions from aqueous solutions by adsorption on activated carbon from a new precursor hazelnut husks[J].Desalination,2008,228(1/2/3):108-113.

[19] RAMADHAN D,MAHIDIN M,MUSLIM A,et al.Preliminary study of novel coal spills-based physical activated carbon for copper ions adsorption in aqueous solution:Kinetics and isotherms[J].Journal of Advanced Research in Fluid Mechanics and Thermal Sciences,2020,71(1):28-38.

[20] 方惠兰.粉煤灰浮选活性炭对含铬废水的吸附研究[J].福建分析测试,2012,21(4):13-15.FANG H L.Study on treatment of waste water of Cr(Ⅵ) by activated carbon made of fly ash flotation carbon[J].Fujian Analysis & Testing,2012,21(4):13-15.

[21] 王丽萍,李超.粉煤灰资源化技术开发与利用研究进展[J].矿产保护与利用,2019,39(4):38-45.WANG L P,LI C.Research progress on development and utilization of fly ash resource technology[J].Conservation and Utilization of Mineral Resources,2019,39(4):38-45.

[22] 张祥成,孟永彪.浅析中国粉煤灰的综合利用现状[J].无机盐工业,2020,52(2):1-5.ZHANG X C,MENG Y B.Brief analysis on present situation of comprehensive utilization of fly ash in China[J].Inorganic Chemicals Industry,2020,52(2):1-5.

[23] 曹天婧.浮选分离未燃炭与粉煤灰及未燃炭制备活性炭研究[D].北京:北京科技大学,2022.CAO T J.Study on efficient enrichment of carbon in fly ash and its application[D].Beijing:University of Science and Technology Beijing,2022.

[24] MITOME T,UCHIDA Y,EGASHIRA Y,et al.Adsorption of indole on KOH-activated mesoporous carbon[J].Colloids & Surfaces A Physicochemical & Engineering Aspects,2013,424:89-95.

[25] 邢宝林,谌伦建,张传祥,等.KOH活化法制备褐煤基活性炭的活化机理研究[J].中国矿业大学学报,2014,43(6):1038-1045.XING B L,CHEN L J,ZHANG C X,et al.Activation mechanism of lignite-based activated carbon prepared by KOH activation[J].Journal of China University of Mining & Technology,2014,43(6):1038-1045.

[26] 王秀芳,田勇,张会平.高比表面积煤质活性炭的制备与活化机理[J].化工学报,2009,60(3):733-737.WANG X F,TIAN Y,ZHANG H P.Preparation and activation mechanism of high specific surface area coal based activated carbon[J].CIESC Journal,2009,60(3):733-737.

[27] KANG H Y,PARK S S,RIM Y S.Preparation of activated carbon from paper mill sludge by KOH-activation[J].Korean Journal of Chemical Engineering,2006,23(6):948-953.

[28] ZHANG L Y,ZHANG H Y,GUO W,et al.Removal of malachite green and crystal violet cationic dyes from aqueous solution using activated sintering process red mud[J].Applied Clay Science,2014,93-94:85-93.

[29] KARTHIKEYAN K G,ELLIOTT H A.Surface complexation modeling of copper sorption by hydrous oxides of iron and aluminum[J].Journal of Colloid and Interface Science,1999,220(1):88-95.

[30] CUI X Q,HAO H L,ZHANG C K,et al.Capacity and mechanisms of ammonium and cadmium sorption on different wetland-plant derived biochars[J].Science of the Total Environment,2016,539:566-575.

[31] GAO X Y,WU L,XU Q,et al.Adsorption kinetics and mechanisms of copper ions on activated carbons derived from pinewood sawdust by fast H3PO4 activation[J].Environmental Science and Pollution Research,2018,25(10):7907-7915.

基本信息:

中图分类号:X703;TQ424

引用信息:

[1]段旭琴,曹天婧,杨娟,等.粉煤灰浮选精炭制备活性炭吸附溶液中Cu~(2+)[J].有色金属(冶炼部分),2022(09):162-172.

基金信息:

国家水体污染控制与治理科技重大专项(2017ZX0730100500303)

发布时间:

2022-08-30

出版时间:

2022-08-30

检 索 高级检索

引用

GB/T 7714-2015 格式引文
MLA格式引文
APA格式引文