Department of Environmental Engineering, Room 131, College of Material Science and Chemical Engineering, Harbin Engineering University, 145 Nantong Street, Nangang District, Harbin, Heilongjiang Province, 150001, People's Republic of China.
Department of Environmental Engineering, School of Municipal and Environmental Engineering, Harbin Institute of Technology, Harbin, 150001, People's Republic of China.
Environ Sci Pollut Res Int. 2018 Jan;25(1):541-551. doi: 10.1007/s11356-017-0365-8. Epub 2017 Oct 18.
To estimate the pollution of As and Pb in the Songhua River which flows through the major rice-producing regions in China, the present study investigated the level and release of As and Pb in surficial sediments which collected from nine sites in Songhua River (M-M). The concentration of As and Pb was ranged as follows: As = 3.10415.01 μg/g, Pb = 20.1037.42 μg/g; the average concentration: As = 6.466 ± 3.077 μg/g, Pb = 28.88 ± 5.077 μg/g. By analysis vertically, the average concentration of As was 5.166 ± 1.496 μg/g in the upstream, 5.815 ± 1.793 μg/g in the midstream, and 9.716 ± 4.977 μg/g in the downstream. The average concentration of Pb was 27.83 ± 4.552 μg/g in the upstream, 28.66 ± 6.333 μg/g in the midstream, and 30.99 ± 4.837 μg/g in the downstream. It indicated that the concentration of As and Pb increased gradually from upstream to downstream. As existed mainly as insoluble state and Pb existed mainly as sulfide and organic combining state in surficial sediments, and the species of As and Pb could transform with the change of the circumstance. The release of quantity of As was higher than Pb. The pH of 6 was not conducive to the release of As and Pb. When the temperature was 35 and 6 °C, the release of As and Pb in surficial sediments were restrained, respectively. Fumaric acid and citric acid played an important role in promoting the release of As, but not conducive to Pb. Furthermore, the reasonable aeration rate was beneficial to the release process of As and Pb in surficial sediment. By kinetic analysis, the Elovich equation (Ct = 84.931-8.952lnt) could be used to describe the dynamic process of the release of As in a relatively short time. The Elovich equation (C = 2.724 + 1.3724lnt) and double constant rate equation (lnC = 1.4646 + 0.1522lnT) could well describe the dynamics process of the release of Pb.
为了评估流经中国主要水稻产区的松花江中砷(As)和铅(Pb)的污染情况,本研究调查了从松花江(M-M)9 个采样点采集的表层沉积物中 As 和 Pb 的含量和释放情况。As 和 Pb 的浓度范围如下:As = 3.104-15.01μg/g,Pb = 20.10-37.42μg/g;平均浓度:As = 6.466±3.077μg/g,Pb = 28.88±5.077μg/g。通过垂直分析,上游、中游和下游的 As 平均浓度分别为 5.166±1.496μg/g、5.815±1.793μg/g 和 9.716±4.977μg/g。Pb 的平均浓度分别为 27.83±4.552μg/g、28.66±6.333μg/g 和 30.99±4.837μg/g。这表明,As 和 Pb 的浓度从上游到下游逐渐增加。As 主要以不溶态存在,Pb 主要以硫化物和有机结合态存在,As 和 Pb 的形态随环境变化而变化。As 的释放量高于 Pb。当 pH 值为 6 时,不利于 As 和 Pb 的释放。当温度分别为 35°C 和 6°C 时,表层沉积物中 As 和 Pb 的释放受到抑制。富马酸和柠檬酸在促进 As 的释放方面发挥了重要作用,但不利于 Pb。此外,合理的曝气速率有利于表层沉积物中 As 和 Pb 的释放过程。通过动力学分析,Elovich 方程(Ct=84.931-8.952lnt)可用于描述较短时间内 As 释放的动态过程。Elovich 方程(C = 2.724+1.3724lnt)和双常数速率方程(lnC = 1.4646+0.1522lnT)可以很好地描述 Pb 释放的动力学过程。