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Adsorption-Desorption Studies of Cadmium in Three Different Soil Orders

机译:三种不同土壤阶次对镉的吸附-解吸研究

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Sorption isotherms have been widely used to assess the heavy metals retention characteristics of soilparticles. Adsorption behaviour of cadmium (Cd) in soils is an important process which exerts a majorinfluence on its uptake by plant roots. Desorption behaviour of the retained metals, however, usuallydiffer from that of adsorption, leading to a lack of coincidence in the experimentally obtained adsorptionand desorption isotherms. Three soils differing in physico-chemical properties (pH 5.7 to 8.2) andvaried taxonomy (Typic Ustochrepts, Typic Rhodustalfs and Entic Chromusterts), were subjected toCd treatment at various concentrations (0, 2, 4, 8, 15, 30, 45, 75 mg Cd/L). The Cd adsorbed by eachsoil was calculated as the difference between the amount of Cd present in the solution initially and thatremaining after equilibration. Immediately after adsorption, desorption took place using successivedilution method with five consecutive desorption steps. Both, Cd adsorption and desorption data weredescribed by Freundlich equation. The adsorption and desorption reactions, however, did not providethe same isotherms, indicating that hysteresis occurred in Cd adsorption-desorption process. Resultsindicated that the adsorption capacity of the soils for Cd increased with an increase in the pH oralkalinity of the soils. The rate of adsorption was, however, found to decrease with increased pH. Butno specific trend was observed in case of desorption. All the three soils used in this study followedFreundlich adsorption isotherms. The adsorption data, in general, indicated that Cd was in a fixed format higher pH levels. The Cd adsorption was in the order of Entic Chromusterts > Typic Ustochrepts >Typic Rhodustalfs.
机译:吸附等温线已被广泛用于评估土壤颗粒的重金属保留特性。镉在土壤中的吸附行为是重要的过程,对植物根系对镉的吸收具有重要影响。但是,保留金属的解吸行为通常与吸附行为不同,导致实验获得的吸附和解吸等温线缺乏一致。对三种物理化学性质(pH 5.7至8.2)和分类学不同的土壤(典型的Ustochrepts,Typic Rhodustalfs和Entic Chromusterts)进行了不同浓度(0、2、4、8、15、30、45、75的Cd处理)毫克Cd / L)。计算每种土壤吸附的Cd,将其作为溶液中最初存在的Cd量与平衡后剩余的Cd量之差。吸附后,立即使用连续稀释法和五个连续的解吸步骤进行解吸。镉的吸附和解吸数据均用Freundlich方程描述。然而,吸附和解吸反应没有提供相同的等温线,表明在Cd吸附-解吸过程中出现了滞后现象。结果表明,土壤对镉的吸附能力随土壤pH口腔碱度的增加而增加。然而,发现吸附速率随pH增加而降低。但是在解吸的情况下没有观察到特定趋势。在本研究中使用的所有三种土壤均遵循Freundlich吸附等温线。通常,吸附数据表明Cd处于较高pH值的固定形式。 Cd的吸附顺序为Entic Chromusterts> Typic Ustochrepts> Typhod Rhodustalfs。

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