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Kinetics, equilibrium and thermodynamics of cerium removal by adsorption on low-rank coal

机译:低阶煤吸附除铈的动力学,平衡和热力学

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The removal of cerium ions on low-rank coal has been studied as a function of contact time, nature of electrolytes (HClO4, HCl, H2SO4 and HNO3), dose of adsorbent, metal ion concentration and temperature. The radiotracer technique was applied to examine the distribution of cerium (Ce3+) using a batch method. Maximum adsorption was found to be at pH 5, using 0.4 g of adsorbent for 4 mL of 5 mg L-1 cerium concentration with equilibration time of 25 min. The adsorption of cerium was decreased with the increase in the concentrations of all the mineral acids used. The kinetic data indicated an intraparticle diffusion process with adsorption being pseudo-second order. The examined rate constant K-2 was 25 g mg(-1) min(-1). The adsorption data obeyed the Langmuir, Freundlich and Dubinin-Radushkevich isotherm plots over the cerium concentration range of 7.137 x 10(-3) to 6.423 x 10(-4) mol L-1. The characteristic Freundlich constants, that is, 1 = 0.381 and K = 5.152 x 10(-2) m mol g(-1) whereas the Langmuir constants Q = 2.889 x 10(-3) m mol g(-1) and b = 14.072 x 10(3) dm(3) mol(-1) have been calculated for the adsorption system. The adsorption mean free energy from the Dubinin-Radushkevich isotherm is 12.987 kJ mol-1 indicating chemical adsorption of ion-exchange mechanism. The uptake of cerium was increased with the rise in temperature (283-333 K). Thermodynamic quantities, that is, Delta H, Delta G and Delta S have been computed and discussed for the system. Adsorbent was characterized by using scanning electron microscopy and Fourier transform infrared spectroscopy before and after the adsorption of cerium. Effect of coexistent ions on the adsorption of cerium has also been investigated. Removal of cerium from tap water sample shows that the proposed method is successfully applicable.
机译:根据接触时间,电解质(HClO4,HCl,H2SO4和HNO3)的性质,吸附剂的剂量,金属离子浓度和温度的变化,对低阶煤上铈离子的去除进行了研究。应用放射性示踪技术,采用分批法研究了铈(Ce3 +)的分布。发现最大吸附为pH 5,使用0.4 g吸附剂对4 mL 5 mg L-1铈浓度的吸附剂,平衡时间为25分钟。铈的吸附随着所用所有无机酸浓度的增加而降低。动力学数据表明颗粒内扩散过程的吸附为伪二级。检查的速率常数K-2为25 g mg(-1)min(-1)。铈的浓度范围为7.137 x 10(-3)至6.423 x 10(-4)mol L-1,其吸附数据符合Langmuir,Freundlich和Dubinin-Radushkevich等温线图。特征Freundlich常数,即1 / n = 0.381和K = 5.152 x 10(-2)m mol g(-1),而Langmuir常数Q = 2.889 x 10(-3)m mol g(-1)和b = 14.072 x 10(3)dm(3)mol(-1)已计算出吸附系统。 Dubinin-Radushkevich等温线的吸附平均自由能为12.987 kJ mol-1,表明离子交换机理的化学吸附。铈的摄取随着温度的升高(283-333 K)而增加。已经为系统计算并讨论了热力学量,即Delta H,Delta G和DeltaS。在吸附铈之前和之后,通过扫描电子显微镜和傅立叶变换红外光谱对吸附剂进行表征。还研究了共存离子对铈吸附的影响。从自来水样品中去除铈表明该方法是成功适用的。

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