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夏季和秋季长江口邻近海域海水中砷的行为和分布及悬浮颗粒物中砷的分布。

Behaviour and distribution of arsenic in seawater and suspended particulate matter in the adjacent area of the Changjiang Estuary during summer and autumn.

机构信息

Key Laboratory of Marine Environmental Science and Ecology, Ministry of Education, Ocean University of China, Qingdao 266100, China; College of Environmental Science and Engineering, Ocean University of China, Qingdao 266100, China.

出版信息

Ecotoxicol Environ Saf. 2021 Dec 20;227:112884. doi: 10.1016/j.ecoenv.2021.112884. Epub 2021 Oct 8.

Abstract

Water and suspended particulate matter (SPM) were collected from the Changjiang Estuary and its adjacent areas during summer (July) and autumn (October) to study the distributions and partitioning of arsenic. The dissolved arsenic (DAs) and particulate arsenic (PAs) concentration distributions were strongly affected by inputs from riverine discharge and water masses in the East China Sea, generally exhibiting a decreasing trend from inshore to offshore. The DAs concentration was higher in the surface water due to the influence of seawater stratification in summer, but it was not obvious in autumn. DAs and PAs concentrations in the estuary were significantly higher in autumn than in summer. Seasonal variations in arsenic were due to seasonal differences in riverine input (mainly the Changjiang River) and the intrusion of water masses. PAs showed a positive correlation with both SPM and turbidity. The highest PAs concentration was observed in the northern Changjiang Estuary affected by the YSCC, with higher turbidity during autumn. The higher concentration of PAs in autumn was affected by the high SPM input and resuspension of sediment. The water-particulate distribution coefficient of As in summer showed an increasing tendency with salinity, which might be caused by the decrease in the diameter of suspended particles in the open sea.

摘要

本研究于夏季(7 月)和秋季(10 月)采集长江口及其毗邻海域的水和悬浮颗粒物(SPM),以研究砷的分布和分配。溶解态砷(DAs)和颗粒态砷(PAs)的浓度分布受河流排放和东海水团的输入强烈影响,通常表现出从近岸到近海逐渐降低的趋势。由于夏季海水分层的影响,表层水中的 DAs 浓度较高,但秋季并不明显。与夏季相比,秋季长江口的 DAs 和 PAs 浓度明显升高。砷的季节性变化归因于河流输入(主要是长江)和水团入侵的季节性差异。PAs 与 SPM 和浊度呈正相关。在受长江冲淡水影响的北部长江口观察到最高的 PAs 浓度,秋季浊度较高。秋季 PAs 浓度较高是由于高 SPM 输入和沉积物再悬浮所致。夏季,As 的水-颗粒物分配系数随盐度呈增加趋势,这可能是由于开阔海域悬浮颗粒物直径减小所致。

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