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Pollutant deposition via snowpack in the context of granite buffering capacity, Western Sudetes, Poland

机译:在花岗岩缓冲能力,西部苏丹,波兰污染物沉积通过积雪沉积

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At the end of each analyzed winter season, the cores of the snowpack profile were collected in the phase of maximum snow water equivalent and a few days later during long spring thaw. Comparison between pH and snow water equivalent allowed to calculate the load of hydrogen ion in the whole snowpack profile. To obtain detailed recognition of the structure of released load of pollutants, the results of determination of chemical composition of snowpack for winter season 2005/2006 are also included. The release of pollutants from snow and their real penetration into soil, ground and surface waters take place during thaw episodes. The initial results indicate however, that the first portions of water penetrating from snow into ground may bring a huge pollutant load and it depends on the amount of snowpack water storage and Total Inorganic Ionic Content value. During one week of continuous ablation in snow season 2005/2006, total load of H+ accumulated in snowpack show 40% decrease (it means: 16,4 mMoles m~(-2)). The fastest removal via the first portions of melting water occurred in case of H~+, (NO_3)~-, (SO_4)~(2-) and Mg~(2+), which is in contrast with much smaller removal rate of Na~+, Cl~- and (NH_4)~+. Such mechanism is responsible for significant acidification of soil and water ecosystems because granite bedrock is able to buffer only 20-30 mMoles m~(-2) of H+ within the whole year. The rate of pollutant deposition released from snowpack is closely related to the number and depth of thaw episodes. It means that the most intense acidification of soil and water ecosystems occurs at areas with deep snowpack during spring thaw events. The growth of snowpack during winter, maximum height and water storage change significantly from one year to another, however the basic mechanisms related to the additional environmental acidification under the influence of snow ablation at the end of each winter season are similar.
机译:在每次分析的冬季结束时,在长弹水中的最大雪水等当量的阶段收集了积雪型材的核心。 pH和雪水之间的比较允许在整个积雪型材中计算氢离子的负载。为了获得详细识别释放污染物的释放载荷的结构,还包括冬季2005/2006年冬季积雪化学成分的结果。在解冻事件期间,将污染物和实际渗透到土壤,地面和表面水域中的污染物释放。然而,初始结果表明,从雪中穿入地面的第一部分渗透可能带来巨大的污染物负荷,这取决于积雪储水量和总无机离子含量值。在雪季连续消融的一周内,积雪中累积的H +的总负荷显示为40%(意味着:16,4毫摩尔M〜(2))。在H〜+的情况下,通过第一部分熔化水的最快除去,(NO_3)〜 - ,(SO_4)〜(2-)和Mg〜(2+),其与较小的去除率相反na〜+,cl〜 - (nh_4)〜+。这种机制负责土壤和水生态系统的显着酸化,因为花岗岩基岩能够在全年内仅缓冲20-30毫摩尔M〜(-2)的H +。从积雪释放的污染物沉积速率与解冻事件的数量和深度密切相关。这意味着在春季解冻事件中有深雪堆的区域发生土壤和水生态系统的最强烈酸化。在冬季,最大高度和储水过程中的积雪的增长从一年到另一年度变化,但是与每个冬季结束时雪消融的额外环境酸化的基本机制相似。

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