Manna Biswaranjan, Ghosh Uday Chand
Department of Chemistry, Presidency College, 86/1 College Street, Kolkata 700073, India.
J Hazard Mater. 2007 Jun 1;144(1-2):522-31. doi: 10.1016/j.jhazmat.2006.10.066. Epub 2006 Oct 27.
The hydrated stannic oxide (HSO) was synthesized and arsenic adsorption behaviour is reported. HSO is found to be amorphous, and stable thermally up to 700 degrees C. The adsorption of As(III) is much higher than As(V) in the drinking water pH (6.5-8.5) range. The time required for reaching equilibrium is 4.0 and 3.0 h, respectively for As(III) and As(V). The adsorption kinetic data obtained at pH 7.0 (+/-0.1) and temperature 27(+/-1) degrees C follow the pseudo-second-order kinetic model best (R(2)>0.98). The analyzes of isotherm adsorption data by two parameter isotherm model equations show the order to obey: Langmuir>Freundlich>Temkin for As(III), and Langmuir>Temkin>Freundlich for As(V). The monolayer adsorption capacities (mg/g) obtained for As(III) and As(V) are 15.85 and 4.30, respectively. Excepting phosphate, other anions studied show no adverse effect on adsorption of As(III) onto HSO. A fixed bed HSO packed column (internal diameter 0.70 cm, bed height 3.7 cm and particle size 0.14-0.29 mm) generates 2400 and 450 BV of potable water (As<0.01 mg/L), respectively, for As(III) and As(V) from arsenic spiked (1.0 mg/L) water samples at pH 7.0 (+/-0.1), which indicated that HSO can be used as an efficient scavenger for As(III) from the contaminated water.
合成了水合氧化锡(HSO)并报道了其对砷的吸附行为。发现HSO为无定形,在高达700摄氏度时热稳定。在饮用水pH值(6.5 - 8.5)范围内,As(III)的吸附量远高于As(V)。As(III)和As(V)达到平衡所需时间分别为4.0小时和3.0小时。在pH 7.0(±0.1)和温度27(±1)摄氏度下获得的吸附动力学数据最符合准二级动力学模型(R²>0.98)。通过双参数等温吸附模型方程对等温吸附数据的分析表明,对于As(III),等温吸附顺序为:Langmuir>Freundlich>Temkin;对于As(V),顺序为:Langmuir>Temkin>Freundlich。As(III)和As(V)的单层吸附容量(mg/g)分别为15.85和4.30。除了磷酸盐外,所研究的其他阴离子对As(III)在HSO上的吸附没有不利影响。一个填充HSO的固定床柱(内径0.70厘米,床高3.7厘米,粒径0.14 - 0.29毫米),对于pH 7.0(±0.1)、砷含量为1.0毫克/升的加标水样中的As(III)和As(V),分别产生2400和450床体积的饮用水(As<0.01毫克/升),这表明HSO可作为从受污染水中有效去除As(III)的吸附剂。