共被期刊论文引用了2次
您的检索式:您选中1篇文献正在查看引证文献汇总
|
|
|
题名
|
作者
|
年代
|
出处
|
被引量
|
| 1 | Characteristics and mechanisms of Ni(Ⅱ) removal from aqueous solution by Chinese loess显示文摘Nickel is a toxic heavy metal among trace elements which has a detrimental impact on living organisms. There is growing need of finding an economic and effective solution for Ni(Ⅱ) immobilization in environments. Chinese loess was selected as adsorbent to remove Ni(Ⅱ) from aqueous solution. Adsorbent dosage, reaction time, solute concentration, temperature, and solution p H also have influences on efficiency of Ni(Ⅱ) removal. The monolayer adsorption capacity of loess towards Ni(Ⅱ) is determined to be about 15.61 mg/g. High temperature and p H favor the removal of Ni(Ⅱ) using Chinese loess soil and the optimal dosage of loess is determined to be 10 g/L. The kinetics and adsorption isotherms of the adsorption process can be best-fitted with the pseudo second order kinetics and Langmuir isothermal model, respectively. The thermodynamic analysis reveals that the adsorption process is spontaneous, endothermic and the system disorder increases with duration. Nickel ions can be removed with the removal efficiency of 98.5% at p H greater than or equal to 9.7. Further studies on loess and Ni(Ⅱ) laden loess(using X-Ray diffraction, Fourier transform infrared spectroscopy) and Ni(Ⅱ) species distribution at various p H have been conducted to discuss the adsorption mechanism. Loess soils in China have proven to be a potential adsorbent for Ni(Ⅱ) removal from aqueous solutions. | 王艳 唐晓武 王恒宇 | 2015 | Journal of Central South University2015,22,11: | 0 |
| 2 | 硅胶负载硫脲型吸附材料对Zn(Ⅱ)的吸附性能研究显示文摘研究了通过均相法和异相法合成的硅胶负载硫脲型吸附材料(HO-SG-GPTS-TS和HE-SG-GPTS-TS)对Zn(II)的吸附性能,考察了溶液p H值、温度、时间及金属离子初始浓度等因素对吸附性能的影响。结果表明,均相法合成产物HO-SG-GPTS-TS对Zn(II)的吸附量较异相法合成产物HE-SG-GPTS-TS高。对Zn(II)的最佳吸附p H值均为6。等温吸附结果表明,随温度及浓度的升高,对Zn(II)的吸附量增大,吸附过程符合Langmuir模型,为单分子层吸附;D-R模型拟合结果表明,对Zn(II)平均吸附自由能均大于8k J/mol,为化学吸附过程。动力学研究表明,吸附材料对Zn(II)的吸附符合拟二级动力学模型,为液膜扩散控制过程。 | 杨迎霞 宗伟 孔令利 牛余忠 陈厚 孙昌梅 曲荣君 | 2015 | 离子交换与吸附2015,31,3: | 0 |
      /1