水合氧化铁去除Cu~(2+)的实验研究

研究了实时生成的水合氧化铁(HFO)对Cu2+的去除。研究结果表明:生成的水合氧化铁是棕黄色无定形铁的氧化物,盐滴定方法测得其零电荷点PZC为8.28±0.02;它对Cu2+吸附的动力学特征受控于HFO的生成动力学,其吸附等温线可用Henry公式和类似Langmuir公式的叠加来拟合;随着吸附剂量的增加,它对Cu2的吸附率和吸附量的影响分别呈现出指数形式(Y=aXb)的增加和减少。Cu2+从溶液中去除的可能机理包括表面络合反应、共沉淀、表面沉淀、Cu2+的水解作用、Cu2+的水解产物与水合氧化铁的絮凝作用等。     

东京根霉对重金属Cr^3＋、Mn^2＋和Zn^2＋的吸附研究

利用固定化发酵中产生的废菌体——东京根霉（Rhizopustonkinesis）去除废水中Cr^3＋、Mn^2＋和Zn^2＋,研究了预处理、pH、温度、金属离子初始浓度、吸附时间等条件对吸附量的影响。结果表明，用NaOH浸泡4—6h、在pH=5—6，温度25-35℃时吸附效果最好，用Langmuir、Freundlich和Temkin方程对其吸附等温线进行拟合，相关性都比较好；用不同的吸附动力学方程描述东京根霉吸附金属离子的最优和最次模型分别为Elovich方程和一级扩散方程，双常数方程和抛物线扩散方程拟合介于前二者之间。     

膨润土对Pb2+、Cu2+、Cr3+的吸附动力学及等温线研究

研究所用膨润土的主要成分为SiO2和Al2O3,属于Ca基膨润土,BET表面积为50.83 m2/g.在恒温及恒定pH条件下,用静态吸附法研究了膨润土对Pb2 、Cu2 、Cr3 的吸附特性,结果表明其较好地符合Lagergten二级吸附速率方程,对这3种离子的吸附速率为Pb2 ＞Cu2 ＞Cr3 .利用3种等温线方程对吸附过程进行拟合,发现利用Langmuir吸附等温方程计算的值与膨润土吸附Pb2 、Cu2 、Cr3 试验数据最为吻合.膨润土对3种金属离子的平衡吸附量为Cr3 ＞Cu2 ＞Pb2 .     

Experimental investigation of adsorption capacity of anthill in the removal of heavy metals from aqueous solution

In the present work, the adsorption capacity of anthill was investigated as a low‐cost adsorbent to remove the heavy metal ions, lead (II) ion (Pb²⁺), and zinc (II) ion (Zn²⁺) from an aqueous solution. The equilibrium adsorption isotherms of the heavy metal ions were investigated under batch process. For the study we examined the effect of the solution's pH and the initial cations concentrations on the adsorption process under a fixed contact time and temperature. The anthill sample was characterized using a scanning electron microscope (SEM), X‐ray fluorescence (XRF), and Fourier transform infrared (FTIR) techniques. From the SEM analysis, structural change in the adsorbent was a result of heavy metals adsorption. Based on the XRF analysis, the main composition of the anthill sample was silica (SiO₂), alumina (Al₂O₃), and zirconia (ZrO₂). The change in the peaks of the spectra before and after adsorption indicated that there was active participation of surface functional groups during the adsorption process. The experimental data obtained were analyzed using 2‐ and 3‐parameter isotherm models. The isotherm data fitted very well to the 3‐parameter Radke–Prausnitz model. It was noted that Pb²⁺ and Zn²⁺ can be effectively removed from aqueous solution using anthill as an adsorbent.     

好氧颗粒污泥对酸性红B的生物吸附模型研究

考察了灭活好氧颗粒污泥吸附酸性红B的吸附等温线、吸附动力学和热力学.结果表明,Langmuir和Redlich-Peterson比Freudlich吸附等温线更符合试验数据,20 ℃时Langmuir最大单分子层吸附量为123.46 mg/g.吸附动力学符合准2级动力学模型.灭活AGS内部扩散过程用Webber-Morris模型拟合,结果表明颗粒内部扩散过程是限速步骤,但边界层扩散和动力学阻力亦不能忽略.热力学分析表明,吸附过程是吸热且自发的过程.     

The prediction of adsorption isotherms of ester vapors on hypercrosslinked polymeric adsorbent

Adsorption isotherms of methyl acetate, ethyl acetate, propyl acetate, isopropyl acetate and ethyl propionate on hypercrosslinked polymeric resin (ND- 100) were measured at 303K, 318K and 333K,respectively, and well fitted by Dubinin–Astakhov (DA) equation. The plots of the adsorbed volume (q _v ) versus the adsorption potential (ε) at three different temperatures all fell basically onto one single curve for every ester. A predicted model based on DA equation was obtained on the basis of adsorption equilibrium data of methyl acetate, ethyl acetate and ethyl propionate at 318K. The model equation successfully predicted the adsorption isotherms of methyl acetate, ethyl acetate and ethyl propionate on ND-100 at 303K, and 333K, and also gave accurate predictive results for adsorption isotherms of the other two ester compounds (propyl acetate and isopropyl acetate) on ND-100 at 303K, 318K and 333K. The results proved the effectiveness of DA model for predicting the adsorption isotherms of ester compounds onto ND-100. In addition, the relationship between physico-chemical properties of adsorbates and their adsorption properties was also investigated. The results showed that molecular weight, molar volume and molar polarizability had good linear correlations with the parameter E (which represents adsorption characteristic energy) of DA equation.     

TiO2@酵母微球吸附废水中的荧光增白剂-VBL及再生研究

采用静电自组装的方法制备出具有草莓结构的TiO2@酵母微球作为吸附材料,对阴离子型荧光增白剂-VBL(FWA-VBL)废水进行吸附研究,考察了溶液pH、溶液初始浓度和TiO2@酵母投加量对吸附效果的影响.结果表明,酸性条件有利于TiO2@酵母微球对FWA-VBL的吸附,平衡吸附量随着溶液初始浓度的增加而增加,随着TiO2@酵母微球投加量的增加而减小.TiO2@酵母对FWA-VBL的吸附行为更加符合Langmuir等温模型,在温度为323.15K下最大吸附量为167.50mg/g; 吸附动力学符合二级动力学方程; 热力学参数表明吸附过程是自发的吸热过程.归因于光催化-吸附耦合效应,TiO2@酵母微球展现出了良好的原位再生能力.H2O2的添加有助于提高TiO2@酵母微球的再生性能.     

Removal of selenite using ‘waste’ Fe(III)/Cr(III) hydroxide: Adsorption kinetics and isotherms

Removal of selenite [Se (IV)] from aqueous solution on to industrial solid ‘waste’ Fe(III)/Cr(III) hydroxide as adsorbent was investigated in the present article. Maximum adsorption was found to be at pH 4.0. Pretreated Fe(III)/Cr(III) hydroxide was found to be more efficient for the removal of selenite compared to untreated adsorbent. Langmuir and Freundlich isotherms have been studied. The Langmuir adsorption capacity (Q ₀) of the pretreated and untreated adsorbents was found to be 15.63 and 6.04?mg?g^?1, respectively. The adsorption process fit into the second-order kinetics. Thermodynamic parameters show that the adsorption process is spontaneous and endothermic in the temperature range 32 to 60°C. Coexisting anions vanadate and phosphate significantly affect the adsorption of selenite for both the pretreated and untreated adsorbents. Molybdate, thiocyanate, sulphate, nitrate and chloride do not significantly affect the removal of selenite for pretreated adsorbent.     

Recovery of seven kinds of cfc and cfc replacements on high‐surface area activated carbon

The adsorption isotherms, the constants of the Dubinin—Radushkevich plots, and the constants of the Langmuir plots of chlorofluorocarbon (CFC) and CFC replacements on high‐surface area activated carbon were investigated to estimate the recovery efficiency of CFC and CFC replacements. The adsorption and desorption of HFC134a on a high‐surface area activated carbon was much easier than that of CFC 113 and the CFC replacements. The recovery efficiency of CFC replacements depends on the hydrogen atoms in molecule. It is possible that the saturated amount adsorbed in the pores or on the surface of the activated carbon could be evaluated by the W_s constant of the the Langmuir equation and the W_o constant of the Dubinin‐Radushkevich equation. The a constant of the Langmuir equation and the BE_o constant of the Dubinin‐Radushkevich equation depend on the molecular composition.