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Fe(II)、Fe(III)对砷与不同分子量腐植酸络合性能的影响
引用本文:姚淑华,雍玉玲,李士凤,王海博,吕洪涛,石中亮.Fe(II)、Fe(III)对砷与不同分子量腐植酸络合性能的影响[J].中国环境科学,2022,42(10):4650-4657.
作者姓名:姚淑华  雍玉玲  李士凤  王海博  吕洪涛  石中亮
作者单位:1. 沈阳化工大学, 辽宁省工业排放重金属处理与资源化技术工程研究中心 辽宁 沈阳 110142;2. 辽宁省生态环境事务服务中心, 辽宁 沈阳 110161
基金项目:辽宁省高等学校创新团队项目(LT2020016);辽宁省教育厅科学研究项目(LQ2020027,LQ2020023,LJ2020008)
摘    要:以腐植酸(HA)代表天然有机质,采用平衡透析和超滤的方法研究铁离子(Fe (II)、Fe (III))对不同分子量HA与砷离子(As (V)、As (III))络合作用的影响,并利用红外光谱(FT-IR)表征其络合特征.结果发现,Fe (II)和Fe (III)均能增强HA络合As能力,且对As (V)络合能力的增强作用大于As (III);pH值显著影响HA络合As能力;溶解性有机碳(DOC)浓度由5mg/L增大到200mg/L,As络合百分比随之增加,此时HA-Fe (III)络合As (III)百分比最大,为24.55%;初始As浓度由10μg/L增加1000μg/L,As络合百分比随之降低,其中HA-Fe (III)络合As (III)百分比最低,为3.11%.相同环境条件下,分子量>100kDa络合As百分比最大,其中HA-Fe (II)络合As (III)的百分比最高为26.43%;分子量小于10kDa的HA络合As百分比明显高于其他分子量的HA.Fe的增强作用主要源于Fe与羧基形成桥梁再与As络合形成三元络合物.

关 键 词:  铁离子  腐植酸  络合  分子量  
收稿时间:2022-03-24

Effect of Fe(II)/Fe(III) on complexation properties of arsenic and humic acid with different molecular weights
YAO Shu-hua,YONG Yu-ling,LI Shi-feng,WANG Hai-bo,LV Hong-tao,SHI Zhong-liang.Effect of Fe(II)/Fe(III) on complexation properties of arsenic and humic acid with different molecular weights[J].China Environmental Science,2022,42(10):4650-4657.
Authors:YAO Shu-hua  YONG Yu-ling  LI Shi-feng  WANG Hai-bo  LV Hong-tao  SHI Zhong-liang
Institution:1. Shenyang University of Chemical Technology, Liaoning Engineering Research Center for Treatment and Recycling of Industrially Discharged Heavy Metals, Shenyang 110142, China;2. Affairs Service Center of Ecological Environment of Liaoning Province, Shenyang 110142, China
Abstract:Humic acid (HA) was used to represent natural organic matter, and the effects of Iron ions (Fe(II)/Fe(III)) on the complexation of HA with arsenic (As(V)/As(III)) of different molecular weights were investigated by equilibrium dialysis and ultrafiltration, and the complexation characteristics were characterized by infrared spectroscopy (FT-IR). Both Fe(II) and Fe(III) enhanced the As complexation ability of HA, and the enhancement effect on As(V) complexation ability was greater than that of As(III); pH significantly affected the As complexation ability of HA; the percentage of As complexation increased with the increase of dissolved organic carbon (DOC) concentration of HA from 50 to 200mg/L, and the percentage of HA-Fe(III) complexation was the maximum at 24.55%. Increasing the initial As concentration from 10μg/L to 1000μg/L, the percentage of As complexation decreased, with the minimum As(III) complexation percentage by HA-Fe(III) at 3.11%. Under the same environmental conditions, the percentage of As complexed with molecular weight more than 100kDa was the highest, and the percentage of As(III) complexed at HA-Fe(II) was 26.43%; The percentage of As complexed at HA with molecular weight less than 10kDa was significantly higher than that at other molecular weights. The enhancement of Fe was mainly due to the formation of a bridge between Fe and carboxyl groups of HA and then complexation with As to form a ternary complex.
Keywords:arsenic  iron ion  humic acid  complexation  molecular weight  
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