Key Laboratory of Marine Chemistry Theory and Technology, Ministry of Education, Ocean University of China, 238 Songling Road, Qingdao 266100, PR China; Laboratory for Marine Ecology and Environmental Science, Qingdao National Laboratory for Marine Science and Technology, Qingdao 266071, PR China.
Leibniz-Institute for Baltic Sea Research, Seestraße 15, D-18119 Warnemünde, Germany.
Sci Total Environ. 2018 Feb 1;613-614:557-568. doi: 10.1016/j.scitotenv.2017.09.029. Epub 2017 Sep 26.
With the increase in anthropogenic environmental disruption, the behavior of arsenic in the Baltic Sea has received more scientific attention because of its complex forms and toxicity, and was re-visited to determine if there have been measurable changes recently. A cruise was conducted in 10-19 May 2011 to investigate the species and distribution of total dissolved inorganic arsenic (TDIAs: [TDIAs]=[As(V)]+[As(III)]) revealing links between the hydrographic dynamics and biological/chemical reactions in the Baltic Sea. In addition, long-term (2002-2010) time-series investigations of particulate arsenic in the Gotland Basin were also conducted in February every year for monitoring purposes. The behavior of TDIAs was non-conservative due to the removal and regeneration processes occurring in the Baltic Sea. Biological scavenging plays a dominant role as sink for TDIAs, with removal amount of 3.1±1.6nmol/L above the pycnocline of the Baltic Sea. Significant regeneration of TDIAs was observed below the pycnocline of the Baltic Sea, which was closely related to hypoxia. The decomposition of organic arsenic and release from the sediment by desorption of As-bearing Fe and Mn oxides were thought to be two major sources for TDIAs regeneration. The median concentration of TDIAs (8.4nmol/L) was much lower than in most marginal seas and oceans, including the near-bottom water around a chemical weapon dumpsite (13.9nmol/L). The hypoxia in the deep water contributed to the increase in As(III) concentrations based on the relationship between As(III)/TDIAs ratio and apparent oxygen utilization. If the difference of As(III) profiles (1981 and 2011) actually represents a long-term increase in As(III) concentrations and a shoaling of the As(III) chemocline, these factors could enhance the toxic effects and extend the residence time of arsenic and, hence, potentially have negative impacts on fisheries and ecosystem health in the Baltic Sea.
随着人为环境破坏的增加,由于砷的复杂形态和毒性,其在波罗的海中的行为受到了更多的科学关注,并重新进行了研究,以确定最近是否发生了可测量的变化。2011 年 5 月 10 日至 19 日进行了一次巡航,以调查总溶解无机砷(TDIAs:[TDIAs]=[As(V)]+[As(III)])的物种和分布,揭示了波罗的海水文动力学与生物/化学反应之间的联系。此外,还每年 2 月在哥特兰盆地进行了长期(2002-2010 年)颗粒态砷的时间序列调查,以进行监测。由于在波罗的海中发生的去除和再生过程,TDIAs 的行为是非保守的。生物清除对 TDIAs 起着主要的汇的作用,在波罗的海的密度跃层上方的去除量为 3.1±1.6nmol/L。在波罗的海的密度跃层下方观察到 TDIAs 的显著再生,这与缺氧密切相关。有机砷的分解和由含砷的铁和锰氧化物解吸从沉积物中释放出来,被认为是 TDIAs 再生的两个主要来源。TDIAs 的中值浓度(8.4nmol/L)远低于大多数边缘海和海洋,包括化学武器倾倒场附近的底层水(13.9nmol/L)。深水缺氧导致基于 As(III)/TDIAs 比值与表观耗氧量之间的关系,As(III)浓度增加。如果 1981 年和 2011 年的 As(III)分布的差异实际上代表了 As(III)浓度的长期增加和 As(III)化学生跃层的变浅,这些因素可能会增强砷的毒性效应并延长其停留时间,从而对波罗的海的渔业和生态系统健康产生潜在的负面影响。