Mohan Dinesh, Singh Kunwar P, Singh Vinod K
Environmental Chemistry Division, Industrial Toxicology Research Centre, Post Box No. 80, Mahatma Gandhi Marg, Lucknow 226001, India.
J Hazard Mater. 2006 Jul 31;135(1-3):280-95. doi: 10.1016/j.jhazmat.2005.11.075. Epub 2006 Jan 25.
An efficient adsorption process is developed for the decontamination of trivalent chromium from tannery effluents. A low cost activated carbon (ATFAC) was prepared from coconut shell fibers (an agricultural waste), characterized and utilized for Cr(III) removal from water/wastewater. A commercially available activated carbon fabric cloth (ACF) was also studied for comparative evaluation. All the equilibrium and kinetic studies were conducted at different temperatures, particle size, pHs, and adsorbent doses in batch mode. The Langmuir and Freundlich isotherm models were applied. The Langmuir model best fit the equilibrium isotherm data. The maximum adsorption capacities of ATFAC and ACF at 25 degrees C are 12.2 and 39.56 mg/g, respectively. Cr(III) adsorption increased with an increase in temperature (10 degrees C: ATFAC--10.97 mg/g, ACF--36.05 mg/g; 40 degrees C: ATFAC--16.10 mg/g, ACF--40.29 mg/g). The kinetic studies were conducted to delineate the effect of temperature, initial adsorbate concentration, particle size of the adsorbent, and solid to liquid ratio. The adsorption of Cr(III) follows the pseudo-second-order rate kinetics. From kinetic studies various rate and thermodynamic parameters such as effective diffusion coefficient, activation energy and entropy of activation were evaluated. The sorption capacity of activated carbon (ATFAC) and activated carbon fabric cloth is comparable to many other adsorbents/carbons/biosorbents utilized for the removal of trivalent chromium from water/wastewater.
开发了一种高效的吸附工艺用于制革废水的三价铬去污。以椰壳纤维(一种农业废弃物)制备了低成本活性炭(ATFAC),对其进行了表征并用于从水/废水中去除Cr(III)。还研究了一种市售活性炭织物布(ACF)以进行对比评估。所有的平衡和动力学研究均在不同温度、粒径、pH值和吸附剂剂量下以间歇模式进行。应用了Langmuir和Freundlich等温线模型。Langmuir模型最适合平衡等温线数据。25℃时ATFAC和ACF的最大吸附容量分别为12.2和39.56mg/g。Cr(III)的吸附随温度升高而增加(10℃:ATFAC - 10.97mg/g,ACF - 36.05mg/g;40℃:ATFAC - 16.10mg/g,ACF - 40.29mg/g)。进行动力学研究以描述温度、初始吸附质浓度、吸附剂粒径和固液比对吸附效果的影响。Cr(III)的吸附遵循准二级速率动力学。通过动力学研究评估了各种速率和热力学参数,如有效扩散系数、活化能和活化熵。活性炭(ATFAC)和活性炭织物布的吸附容量与用于从水/废水中去除三价铬的许多其他吸附剂/碳/生物吸附剂相当。