Bargagli R
Dipartimento di Biologia Ambientale, Università di Siena, Italy.
Rev Environ Contam Toxicol. 2000;166:129-73.
Metals are natural constituents of the abiotic and biotic components of all ecosystems, and under natural conditions they are cycled within and between the geochemical spheres--the atmosphere, lithosphere, hydrosphere, and biosphere--at quite steady fluxes. In the second half of the twentieth century, the huge increase in energy and mineral consumption determined anthropogenic emissions of several metals exceeding those from natural sources, e.g., volcanoes and windborne soil particles. In the Northern Hemisphere, the biogeochemical cycles of Pb, Cd, Zn, Cu, and other metals were significantly altered, even in Arctic regions. On the contrary, available data on trace metal concentrations in abiotic matrices from continental Antarctica, summarized in this review, suggest that the biogeochemical cycle of Pb is probably the only one that has been significantly altered by anthropogenic emissions in Antarctica and elsewhere in the Southern Hemisphere, especially in the period 1950-1975. Environmental contamination by other metals from anthropogenic sources in Antarctica itself can generally only be detected in snow samples taken within a range of a few kilometers or several hundred meters from scientific stations. Local metal pollution from human activities in Antarctica may compromise studies aimed at assessing the biogeochemical cycle of trace elements and the effects of global climate change. Thus, this review focuses on concentrations of metals in atmospheric particulate, snow, surface soils, and freshwater from the Antarctic continent and surface sediments and seawater from the Southern Ocean, which can plausibly be regarded as global background values of trace elements. These baselines are also necessary in view of the construction of new stations, the expansion of existing facilities to support research, and the growth of tourism and fisheries. Despite difficulties in making comparisons with data from other remote areas of the world, concentrations of trace metals in most samples of atmospheric particulates, snow, ice, soils, and marine sediments from Antarctica can be taken as global background levels. Comparison between the results of trace element surveys in marine waters of the Southern Ocean and in other seas is practically impossible. The upwelling or subduction of water masses, the seasonality in ice cover and in phytoplankton biomass, the low fallout of atmospheric dust, and many other peculiar characteristics of the Southern Ocean make concentrations of trace metals in surface waters quite variable in space and time. The depletion of nutrients in surface waters, which is a regular feature of many marine environments, rarely occurs in the Southern Ocean. Waters in some regions are characterized by very low concentrations of Fe and Mn, whereas in others the content of Cd is relatively high at the beginning of summer and may decrease about one order of magnitude during the phytoplankton bloom. Although in most Antarctic coastal ecosystems the input of metals from geochemical and anthropogenic sources and from long-range transport is negligible, concentrations of Cd in the waters and biota may be higher than in waters and related species of organisms from polluted coastal areas. Like the Southern Ocean, Antarctic lakes have many peculiar characteristics. They are often perennially ice covered and without outlet, and their water, which is gained only from short-term melting of snow and glaciers in summer, is lost mainly by sublimation of surface ice. Several lakes are distinctly stratified: the water under the ice may be cool, rich in oxygen, and among the cleanest and clearest of natural waters, whereas water near the bottom becomes anoxic, tepid, and richer in major and trace elements. Considering the specificity of Antarctic environments, to evaluate the extent and consequences of global changes and increasing human activities in Antarctica itself, research on the biogeochemistry of trace metals and monitoring programs
金属是所有生态系统中非生物和生物成分的天然组成部分,在自然条件下,它们在大气圈、岩石圈、水圈和生物圈等地球化学圈层内部及之间以相当稳定的通量循环。在20世纪后半叶,能源和矿产消耗的大幅增加导致几种金属的人为排放量超过了自然来源(如火山和风力携带的土壤颗粒)的排放量。在北半球,铅、镉、锌、铜和其他金属的生物地球化学循环发生了显著变化,即使在北极地区也是如此。相反,本综述总结的来自南极大陆非生物基质中痕量金属浓度的现有数据表明,铅的生物地球化学循环可能是唯一在南极和南半球其他地区,特别是在1950 - 1975年期间,受到人为排放显著改变的循环。来自南极自身人为源的其他金属对环境的污染通常只能在距离科学站几公里或几百米范围内采集的雪样中检测到。南极人类活动造成的局部金属污染可能会影响旨在评估微量元素生物地球化学循环和全球气候变化影响的研究。因此,本综述重点关注南极大陆大气颗粒物、雪、表层土壤和淡水中以及南大洋表层沉积物和海水中的金属浓度,这些浓度可以合理地被视为微量元素的全球背景值。鉴于新站的建设、现有设施的扩建以支持研究以及旅游业和渔业的发展,这些基线也是必要的。尽管难以与世界其他偏远地区的数据进行比较,但南极大气颗粒物、雪、冰、土壤和海洋沉积物的大多数样本中的痕量金属浓度可以被视为全球背景水平。南大洋和其他海域海水中微量元素调查结果之间的比较实际上是不可能的。水体的上升流或俯冲、冰盖和浮游植物生物量的季节性变化、大气尘埃沉降量低以及南大洋的许多其他特殊特征使得表层水中痕量金属的浓度在空间和时间上变化很大。表层水营养物质的消耗在许多海洋环境中是常见特征,但在南大洋很少发生。一些地区的水体中铁和锰的浓度非常低,而在其他地区,夏季初镉的含量相对较高,在浮游植物大量繁殖期间可能会降低约一个数量级。尽管在大多数南极沿海生态系统中,来自地球化学和人为源以及长距离传输的金属输入可以忽略不计,但水体和生物群中镉的浓度可能高于受污染沿海地区的水体和相关生物物种中的浓度。与南大洋一样,南极湖泊也有许多独特之处。它们通常常年被冰覆盖且无出水口,其水仅在夏季通过雪和冰川的短期融化获得,主要通过表层冰的升华流失。一些湖泊有明显的分层现象:冰层下的水可能凉爽、富含氧气,是最清洁、最清澈的天然水体之一,而靠近底部的水则缺氧、温热,主要和微量元素含量更高。考虑到南极环境的特殊性,为了评估全球变化和南极自身人类活动增加的程度及后果,关于痕量金属生物地球化学的研究和监测项目