首页|竹皮活性炭对工业废水中高浓度Cr(Ⅵ)的吸附

竹皮活性炭对工业废水中高浓度Cr(Ⅵ)的吸附

Adsorption of High Concentration Cr(Ⅵ) from Industrial Wastewater by Bamboo Bark Based Activated Carbon

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以竹皮废料为原料,采用水蒸气活化法制备活性炭,用于吸附水中的高浓度Cr(Ⅵ)离子并探究其吸附性能及吸附机理.通过BET、SEM、FTIR、Ph及等电点测定对其微观物理形貌和表面化学性质进行了表征.结果表明,制得的活性炭比表面积高达1068 cm2·g-1,总孔容达0.55 cm3·g-1、微孔比例达72.7%、平均孔径为1.01 nm,主要含有羟基、羰基等含氧官能团.单因素吸附实验发现,对于质量浓度为150 mg·L-1的Cr(Ⅵ)在活性炭用量1.2 g·L-1、Ph为2时吸附效果最佳,吸附去除率达99.7%,残留质量浓度符合国家标准.推测吸附机理为活性炭表面官能团质子化、活性炭与铬离子之间静电吸引、Cr(Ⅵ)表面还原、Cr(Ⅲ)的吸附或释放.
Bamboo bark based activated carbon (AC) prepared by steam activation was used for the treatment of high concentration Cr(Ⅵ) polluted water.BET,SEM,FTIR,Ph and isoelectric point measurements were used to characterize the pore structure and surface chemistry of the AC.The results showed that the specific surface area of the prepared AC was 1068 cm2·g-1,the total pore volume was 0.55 cm3·g-1,the proportion of micropores was 72.7%,and the average pore size was 1.01 nm.It mainly contained hydroxyl,carbonyl and other oxygen-containing functional groups.The single factor adsorption test found that for Cr (Ⅵ) with a mass concentration of 150 mg·L-1,the adsorption effect was the best when the amount of activated carbon was 1.2 g·L-1 and the Ph value was 2,the adsorption removal rate reached 99.7%,and the residual concentration met the national standard.Adsorption mechanisms was speculated to include four steps:AC surface functional groups were protonated;Cr(Ⅵ) anion was absorbed by the protonated surface functional groups through electrostatic attraction;the adsorbed Cr(Ⅵ) was reduced by AC;Cr(Ⅲ) was absorbed by AC or released into solution.

Bamboo bark activated carbonIndustrial wastewaterCr(Ⅵ)Adsorption mechanism

张艳娟、段正康、张锟

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湖南石油化工职业技术学院,湖南岳阳 414000

湘潭大学化工学院,湖南湘潭 411105

竹皮活性炭 工业废水 Cr(Ⅵ)离子 吸附机理

湖南省教育厅科学研究项目

22C1068

2024

当代化工
中国石油抚顺石化公司,中国石化抚顺石油化工研究院,沈阳市医药和化工行业联合会

当代化工

CSTPCD
影响因子:0.412
ISSN:1671-0460
年,卷(期):2024.53(9)
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