改性活性炭对Cu(II)、Pb(II)和Cr(VI)的吸附

Nasanjargal Shirendev, Munkhpurev Bat-Amgalan, A. Aleksandr, Burmaa Gunchin, Ganchimeg Yunden
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摘要

研究了氨基功能化活性炭对Cu(II)、Pb(II)和Cr(VI)的吸附性能。以蒙古Tavantolgoi矿床的煤为前驱体进行改性。煤炭化后,在不同时间(120min、180min、240min)和不同温度(800oC、850oC)下用加热蒸汽活化焦炭。活性炭在850℃、240 min条件下用3-氨基丙基三乙氧基硅烷(APTES)处理。利用傅里叶变换红外光谱(FT-IR)、扫描电镜(SEM)和x射线能量色散光谱(EDS)验证了金属离子与吸附剂表面官能团的相互作用。考察了pH值(2 ~ 7)、接触时间(0.5 ~ 6 h)、温度(25℃、35℃、45℃、55℃)、重金属离子初始浓度(10、25、50 mg/L)和常见阳离子(Na、K、Ca、mg)等参数的影响。改性活性炭吸附Cu(II)、Pb(II)和Cr(VI)的最佳pH分别为4、3和3。当温度从25℃提高到55℃时,Cu(II)和Cr(VI)的吸附量分别从6.15 mg/g提高到9.88 mg/g和17.1 mg/g提高到19.0 mg/g(金属离子初始浓度为50 mg/L)。当温度由25℃升高至55℃时,吸附量由3.13 mg/g下降至2.69 mg/g。热力学参数如焓(ΔHo)、熵(ΔSo)和吉布自由能(ΔGo)进行了估计,结果证实了所有吸附过程都是自发的,热力学有利。当Na、K、Ca、Mg的吸附量从0 ~ 200 Mg /L增加到200 Mg /L时,吸附量下降,对Pb(II)的吸附量明显下降。改性活性炭对金属离子的吸附量大小顺序为Cr(VI) Cu(II) Pb(II)。讨论了其吸附机理
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Cu(II), Pb(II) and Cr(VI) Adsorption on the Modified Activated Carbon
In this study, the sorptions of Cu(II), Pb(II), and Cr(VI) on amine-functionalized activated carbon were investigated. Coal from the Tavantolgoi deposit of Mongolia was used as a precursor for the modification. After the coal carbonization, the char was activated with heated steam at different times (120, 180, and 240 min) and several temperatures (800oC and 850oC). The activated carbon at 850oC for 240 min was used for the treatment with 3-aminopropyltriethoxysilane (APTES). The interactions between metal ions and functional groups on the sorbent surface were confirmed by Fourier transform infrared (FT-IR) spectroscopy, scanning electron microscopy (SEM) coupled with X-ray energy dispersive spectroscopy (EDS). The influence of various parameters such as pH (2-7), contact time (0.5-6 h), temperature (25oC, 35oC, 45oC, and 55oC), initial concentration of heavy metals ions (10, 25, and 50 mg/L), and common cations (Na, K, Ca, Mg) was investigated. The optimum pH for Cu(II), Pb(II), and Cr(VI) sorption on the modified activated carbon was chosen as 4, 3, and 3, respectively. The sorption capacity was increased from 6.15 to 9.88 mg/g and 17.1 mg/g to 19.0 mg/g when increased the temperature from 25oC to 55oC for Cu(II) and Cr(VI) adsorption, respectively (initial concentration of metal ions were 50 mg/L). But the sorption capacity was decreased from 3.13 mg/g to 2.69 mg/g when increased the temperature from 25oC to 55oC for Pb(II) adsorption. The thermodynamic parameters such as enthalpy (ΔHo), entropy (ΔSo), and Gibb’s free energy (ΔGo) were estimated, and the results confirmed that all sorption processes are spontaneous and thermodynamically favorable. The sorption capacity was decreased when the amount of Na, K, Ca, or Mg increased from 0 to 200 mg/L, and a remarkable decrease in sorption capacity was observed for Pb(II) adsorption. The order of adsorption capacity of modified activated carbon for metal ions was Cr(VI) Cu(II) Pb(II). The sorption mechanism was discussed for the
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