杨军,喻清,张攀,李照鹏,吕翔,江婷婷,戚燚林,熊远海.功能化水葫芦生物吸附剂的制备及其对铀的吸附机理[J].南华大学学报(自然科学版),2021,(3):7~16.[YANG Jun,YU Qing,ZHANG Pan,LI Zhaopeng,Lü Xiang,JIANG Tingting,QI Yilin,XIONG Yuanhai.Preparation of Functional Water Hyacinth Biological Adsorbent and its Adsorption Mechanism for Uranium[J].Journal of University of South China(Science and Technology),2021,(3):7~16.]
功能化水葫芦生物吸附剂的制备及其对铀的吸附机理
Preparation of Functional Water Hyacinth Biological Adsorbent and its Adsorption Mechanism for Uranium
投稿时间:2020-12-25  
DOI:
中文关键词:  水葫芦  柠檬酸  热改性  
英文关键词:water hyacinth  citricacid  thermal modification  uranium
基金项目:国家自然科学基金资助项目(51804164;51774187);湖南省教育厅资助项目(18B276;18B266;18A247;17A184);湖南省大学生研究性学习和创新性实验计划项目(20202799);金属矿山安全与健康国家重点实验室开放课题(zdsys2018-007);南华大学大学生研究性学习和创新性实验计划项目(201412;201422;201501);湖南省高新技术产业科技创新引领计划(科技攻关类)项目(2020SK2024)
作者单位
杨军 西安中核蓝天铀业有限公司,陕西 西安 710500 
喻清 南华大学 资源环境与安全工程学院, 湖南 衡阳 421001 
张攀 华中科技大学 环境科学与工程学院,湖北 武汉 430074 
李照鹏 中南大学 资源与安全工程学院,湖南 长沙 410083 
吕翔 南华大学 资源环境与安全工程学院, 湖南 衡阳 421001 
江婷婷 南华大学 资源环境与安全工程学院, 湖南 衡阳 421001 
戚燚林 南华大学 资源环境与安全工程学院, 湖南 衡阳 421001 
熊远海 南华大学 资源环境与安全工程学院, 湖南 衡阳 421001 
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中文摘要:
      采用氢氧化钠预处理—柠檬酸热改性的两阶段处理方法,对水葫芦(water hyacinth,WH)通过酯化反应引入外来羧基,制备成一种新型的功能化水葫芦生物吸附剂(modified water hyacinth,MWH)。利用批次静态吸附实验,研究了pH、铀初始质量浓度、WH/MWH投加量、吸附时间等因素对WH/MWH吸附铀的影响,通过SEM、EDS、FTIR表征手段以及吸附动力学,研究了WH/MWH吸附含铀废水的机理。结果表明:当含铀废水溶液初始质量浓度为1 mg/L、溶液pH=7、WH/MWH的投加量为0.2 g/L、吸附时间4 h时即达到吸附平衡,最大吸附容量为4.06 mg/g,较WH而言,MWH对铀的吸附率提高了34.03%,吸附容量提高了1.7 mg/g。MWH吸附铀的过程更符合准二级动力学模型,说明MWH吸附含铀废水主要是以化学吸附为主,同时伴随表面吸附以及离子交换作用。
英文摘要:
      The modified Water Hyacinth MWH was prepared by sodium hydroxide pretreatment and thermal modification with citric acid. The effects of pH, initial uranium concentration, WH/MWH dosage, adsorption time and other factors on the adsorption of uranium by WH/MWH were studied by batch static adsorption experiment. The mechanism of WH/MWH adsorption of uranium-containing wastewater was studied by SEM, EDS, FTIR characterization and adsorption kinetics. The results showed that when the initial concentration of uranium-containing wastewater was 1 mg/L, the pH value of the solution was 7, the dosage of WH /MWH was 0.2 g/L and the adsorption time was 4 hours, the adsorption equilibrium was reached, and the maximum adsorption capacity was 4.06 mg/g. Compared with WH, the adsorption rate of MWH to uranium increased by 34.03%, and the adsorption capacity increased by 1.7 mg/g. The uranium adsorption process of MWH is more in line with the quasi-second-order kinetic model, indicating that adsorption of uranium-containing wastewater with MWH is mainly chemical adsorption, accompanied with surface adsorption and ion exchange.
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