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91.
云贵高原是青藏隆起在南亚大陆形成的一个海拔梯度大、地势格局复杂的特异环境单元.该地域兼受东南季风与西南季风的交汇影响,是全球变化的敏感区之一.青藏隆起对云贵高原现代环境影响主要表现在1)全球性大气扩散污染物的屏蔽效应和局地性大气扩散污染物的滞留效应;2)区域化学风化的增强效应和物理侵蚀的梯级效应;3)地表环境地球化学过程的低纬度-高海拔效应.核素示踪模式分析表明滇西与黔中地区之间137Cs自大气散落差异明显[1986年以前,洱海和红枫湖沉积物中137Cs散落的累计值分别为(0.11±0.01)Bq/cm2及(0.37±0.01)Bq/cm2],而7Be的散落相近.这说明青藏隆起对滇西地区存在全球性扩散大气污染物散落的屏蔽效应. 相似文献
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Four thousand years of atmospheric lead pollution in northern Europe: a summary from Swedish lake sediments 总被引:8,自引:7,他引:8
This paper presents a large palaeolimnological study of the pre-industrial and industrial history of atmospheric lead pollution deposition in Sweden. Both lead concentrations and 206Pb/207Pb ratios have been analysed in 31 lakes covering most of Sweden, plus one lake in north-west Russia. Four of the lakes have varved (annually-laminated) sediments. Isotope analysis is a sensitive and effective method to distinguish pollution lead from natural catchment lead and to detect early pollution influence, because the 206Pb/207Pb ratio in unpolluted background sediments in Sweden was > 1.3, while that of lead from pollution, derived from ores and coal, was < 1.2. The sediments show a consistent picture of past temporal changes in atmospheric lead pollution. These changes include: the first traces of pollution 3,500-3,000 yrs ago; a pollution peak in Greek-Roman Times (about 0 AD); lower lead fall-out between 400 and 900 AD; a significant and permanent increase in atmospheric lead fall-out from about 1000 AD; an increase with the Industrial revolution; a major increase following World War II; the maximum peak in the 1970s; and decreasing fall-out over the last decades. The four varved sediments provide high-resolution records of atmospheric pollution. They reveal pollution peaks about 1200 and 1530 AD which match the history of metal production in Europe. According to the varve records the lead pollution level in the late 1990s had decreased beneath the level of the 1530s. The pollution level 1200 AD was about 35% of the 1980s, when lead pollution was still near its all time high. About 50% of the total accumulated atmospheric lead pollution deposition through time was deposited in the pre-industrial period. The sediments also show a consistent picture of the geographic distribution of atmospheric lead deposition over time, with higher deposition in south Sweden and declining levels to the north, which supports the hypothesis that the main sources of pre-industrial atmospheric lead pollution in Sweden were cultural areas in mainland Europe and Great Britain. 相似文献
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洞庭湖的冲淤变化和空间分布 总被引:25,自引:4,他引:25
在实测的1974,1988,1998年1:2.5万地形图的基础上,利用地理信息系统的数据处理和空间分析方法,分析洞庭湖24年来的冲淤规律,得到了2个时期(1974-1988,1988-1998)洞庭湖冲淤量和冲淤区域的空间分布位置,研究表明,洞庭湖近24个来总的趋势冲淤厚度没有明显的变化,为0.017m/a。以两期冲淤变化的趋势预测了2010年三峡工程全部完工时洞庭湖的冲淤变化状况,结果表明,1998-2010年间洞庭湖将平均淤高0.33m。最后以3年数字地形模型为基础,分析了洞庭湖24年来的不同水位下湖盆容积的变化。 相似文献
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Dirk Goossens 《地球表面变化过程与地形》2001,26(11):1213-1219
This article presents a simple physical concept of aeolian dust accumulation, based on the behaviour of the subprocesses of dust deposition and dust erosion. The concept is tested in an aeolian dust wind tunnel. The agreement between the accumulation curve predicted by the model and the accumulation curve obtained in the experiments is close to perfect and shows that it is necessary to discriminate between the processes of aeolian dust deposition and aeolian dust accumulation. Two important thresholds determine the accumulation process. For wind speeds below the deflation threshold, the aeolian accumulation of dust increases linearly with the wind speed. For wind velocities between the deflation threshold and the accumulation limit, the sedimentation balance is above unity and there is still accumulation, though it rapidly drops once the deflation threshold has been exceeded. At wind speeds beyond the accumulation limit, the sedimentation balance is below unity and there will no longer be an accumulation of dust. The thresholds have been determined in a wind tunnel test at friction velocity u* = 0·34 m s?1 (deflation threshold) and u* = 0·43 m s?1 (accumulation limit), but these values are only indicative since they depend heavily on the characteristics of the accumulation surface and of the airborne grains. Copyright © 2001 John Wiley & Sons, Ltd. 相似文献
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