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作 者:张政勤[1] 罗文贱[1] 陈勇[1] 杨少海[1] 邹献中[1]
机构地区:[1]广东省农业科学院农业资源与环境研究所,农业部南方植物营养与肥料重点实验室,广东省养分资源循环利用与耕地保育重点实验室,广州510640
出 处:《土壤学报》2015年第5期1188-1195,共8页Acta Pedologica Sinica
基 金:广东省中小企业发展资金项目“农田重金属污染阻控产品的产业化与推广”资助
摘 要:研究了江西红壤和昆明铁质砖红壤在去离子水中和在0.1molL^-1 NaNO3溶液中吸附铜离子后,依次在包括去离子水在内,浓度由低到高的NaNO3溶液中解吸时,铜离子解吸率在不同吸附pH段的分配规律。结果表明,随着吸附pH的升高,可在去离子水中解吸的铜离子解吸率变化规律与在NaNO3溶液中者完全不同。在所研究的吸附pH范围内,大致以吸附pH3.7~4.0为界,低于此值时,吸附性铜离子基本以在去离子水中解吸为主,反之则基本为交换性解吸。土壤中氧化铁含量和吸附时溶液的NaNO3浓度越高,则能被交换解吸的铜离子所占总解吸率的比例越低。其原因与不同pH段各种铜离子吸附态在不同吸附条件下的比例分配以及解吸对体系pH的影响有关。An adsorption and desorption test was conducted of two variable charge soils (Ali-Haplic Acrisol from Jiangxi and Hyper-Rhodic Ferralsol from Kunmin of Yunnan ) to explore distribution of desorption rates of pre-adsorbed Cu ( Ⅱ ) from the soils in NaNO3 solution relative to concentration of the solution and pH, at which Cu (Ⅱ) was adsorbed during the pre-adsorption phase. For the test, the soil samples were first put into de-ionized water and 0.1 mol L-1 NaNO3, separately, for pre-adsorption of Cu (Ⅱ) and then into de-ionized water and NaNO3 solutions varying in concentration gradually from low to high, sequentially, for desorption of Cu ( Ⅱ ) . Results show that with rising pH, Cu ( Ⅱ ) desorption rate varied sharply with NaNO3 solution. In de-ionized water, Cu (Ⅱ) desorption rate declined monotonously with the rise of pH in the Cu ( Ⅱ ) pre-adsorption phase; while in NaNO3 solutions, Cu ( Ⅱ ) desorption ratefollowed a peak-shaped curve, but the total Cu ( Ⅱ ) desorption rate also declined monotonously with the rise of pH in the Cu ( Ⅱ ) pre-adsorption phase. The Cu ( Ⅱ ) desorption rate was the highest in the solution of 0.1 mol L-1 NaNO3. In short, desorption rates of the Cu (Ⅱ) desorbable in de-ionized and in NaNO3 solutions were distributed mainly in the high and low sections, respectively, of the range of pH studied. Desorption rate of the Cu ( Ⅱ ) desorbable in NaNO3 was closely related to content of ferric oxide in the soils and NaNO3 concentration in Cu ( Ⅱ ) pre-adsorption, so the higher the content of ferric oxide in the soil, or the higher the NaNO3 concentration in pre-adsorption at pH 〉 4.0 - 4.5, the lower the proportion of Cu ( Ⅱ ) desorbed by NaNO3. The cause of such a phenomena is believed to be associated with the effect of ion-strength, specific weight of exchangeable Cu ( Ⅱ ) relative to adsorption condition and the effect of desorption on pH of the system. Besides, comparison was also made
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