沉水植物轮叶黑藻和穗花狐尾藻对Cu2+的等温吸附特征

研究了沉水植物轮叶黑藻和穗花狐尾藻对Cu²⁺的吸附等温线,分别采用了线性和非线性2种方法拟合吸附等温线,并比较分析2种方法的拟合效果和适用性.结果表明:①在采用等温吸附模型比较和评价不同生物吸附剂的性能时,不能仅仅根据R²和χ²的大小进行拟合方程的适用性比较.为了获得更为真实可靠的拟合结果,在实践中可以利用线性和非线性方法分别进行拟合,而每一种拟合方法也要同时采用多种模型,在对多个拟合结果比较的基础上选择更符合实验数据的吸附模型;②在本实验中,沉水植物轮叶黑藻和穗花狐尾藻吸附Cu²⁺的行为更符合Langmuir模型,而Freundlich模型特别是其线性表达式的计算值与实验数据的误差较大;③沉水植物中粗纤维素占干物质的比重是影响其吸附容量的重要因素之一,其细胞壁上多糖的—OH和—CONH₂可能是吸附的活性中心;④根据Langmuir模型线性拟合参数q_m,轮叶黑藻、穗花狐尾藻对Cu²⁺的最大吸附量分别为21.55 mg/g和10.80mg/g,其吸附Cu²⁺的最大活性比表面积分别为3.23m²/g和1.62m²/g.

Equilibrium Sorption Isotherm for Cu2+ onto Hydrilla verticillata Royle and Myriophyllum spicatum

Equilibrium sorption isotherms for Cu2+ onto Hydrilla verticillata Royle and Myriophyllum spicatum were studied. Both methods of linear and non-linear fitting were applied to describe the sorption isotherms, and their applicability were analyzed and compared. The results were: (1) The applicability of simulated equation can't be compared only by R2 and chi2 when equilibrium sorption model was used to quantify and contrast the performance of different biosorbents. Both methods of linear and non-linear fitting can be applied in different fitting equations to describe the equilibrium sorption isotherms respectively in order to obtain the actual and credible fitting results, and the fitting equation best accorded with experimental data can be selected; (2) In this experiment, the Langmuir model is more suitable to describe the sorption isotherm of Cu2+ biosorption by H. verticillata and M. spicatum, and there is greater difference between the experimental data and the calculated value of Freundlich model, especially for the linear form of Freundlich model; (3) The content of crude cellulose in dry matter is one of the main factor affecting the biosorption capacity of a submerged aquatic plant, and -OH and -CONH2 groups of polysaccharides on cell wall maybe are active center of biosorption; (4) According to the coefficients qm of the linear form of Langmuir model, the maximum sorption capacity of Cu2+ was found to be 21.55 mg/g and 10.80mg/g for H. verticillata and M. spicatum, respectively. The maximum specific surface area for H. verticillata for binding Cu2+ was 3.23m2/g, and it was 1.62m2/g for M. spicatum.