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首页> 外文期刊>Water, Air, and Soil Pollution >AIR-POLLUTION EFFECT AND PALEOTEMPERATURE SCALE VERSUS δ~(13)C RECORDS IN TREE RINGS AND IN A PEAT CORE (SOUTHERN POLAND)
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AIR-POLLUTION EFFECT AND PALEOTEMPERATURE SCALE VERSUS δ~(13)C RECORDS IN TREE RINGS AND IN A PEAT CORE (SOUTHERN POLAND)

机译:树环和泥炭中(波兰南部)的空气污染效应和古温度尺度与δ〜(13)C记录的对比

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摘要

Carbon isotope analyses of peat profiles from the Karkonosze Mts. (SW Poland) and tree-ring cellulose from Wisla river valley in the Krakow region (S Poland) have been carried out. The samples analysed represent approximately the last 1100 years. The δ~(13)C profile in peat from the Szrenica peat bog ranges from -26.74 to -21.81 per thousand and the δ~(13)C value of tree rings range from -27.82 to -21.94 per thousand. The observed variations in the δ~(13)C values of the peat samples and tree rings from Poland in general correlated with each other (Figure 1). This suggests that the δ~(13)C value of organic matter in terrestrial conditions is generally controlled by the same environmental factors. On average, over the last millennium (X-XIX century), the δ~(13)C value of peat cellulose has been 1.8 per thousand isotopically heavier compared to the corresponding tree ring cellulose value. It is not possible to provide a precise calibration of isotope signatures in tree rings, as the assimilation isotope effect depends mostly on local microclimatic conditions and specific species demands. In the region under study, temperature was the dominant factor controlling the δ~(13)C value of tree ring cellulose and peat-bog Sphagnum before the XIX century. It is estimated that, in the temperate climate of Poland, the carbon isotope fractionation between living plants and atmospheric carbon dioxide (Δ~(13)C_(p-a)) for C3 plants is about -0.26 per thousand/1℃. This corresponds to 2.1 per thousand/1000 m of elevation. Since the mid-XIX, in the Wisfa valley when the river was regulated and water deficit in the neighbouring areas became common (Trafas, 1975), water availability plays a primary role in isotope fractionation of the vegetation. Since the 1955, just after the 'Lenin' steelworks started operation, pollution became the dominant factor controlling the carbon isotope signature of plants. Contamination of the atmosphere by fossil fuel burning from the 'Lenin' steelworks increased the δ~(13)C value of tree ring cellulose by about 1.3 per thousand. This was probably caused by an increased concentration of atmospheric pollution (SO_x and dust) limiting the ventilation rate of the stomata.
机译:Karkonosze山的泥炭剖面的碳同位素分析。 (波兰西南部)和来自克拉科夫地区(波兰南部)的维斯瓦河谷的树木年轮纤维素的生产。分析的样本大约代表最近1100年。 Szrenica泥炭沼泽中泥炭的δ〜(13)C分布范围为每千个-26.74至-21.81,树环的δ〜(13)C值分布范围为-27.82至-21.94。从波兰观察到的泥炭样品和树木年轮的δ〜(13)C值的变化通常相互关联(图1)。这表明在陆地条件下有机质的δ〜(13)C值通常受相同的环境因素控制。平均而言,在最近一个千年中(X-XIX世纪),与相应的年轮纤维素值相比,泥煤纤维素的δ〜(13)C值为每千同位素同位素重1.8。由于同化同位素效应主要取决于当地的微气候条件和特定物种的需求,因此无法对树环中的同位素特征进行精确校准。在所研究的区域中,温度是控制十九世纪前树木年轮纤维素和泥炭泥炭藓的δ〜(13)C值的主导因素。据估计,在波兰的温带气候下,C3植物的活植物与大气二氧化碳之间的碳同位素分馏(Δ〜(13)C_(p-a))约为-0.26 /千/ 1℃。这相当于每千高/ 1000 m高2.1。自十九世纪中叶以来,在维斯法河谷,当时河流受到管制,而邻近地区的水短缺现象普遍(Trafas,1975),水的可利用性在植被的同位素分级中起着主要作用。自1955年以来,“列宁”钢厂开始运营后,污染就成为控制植物碳同位素特征的主要因素。列宁钢铁厂燃烧化石燃料对大气的污染使树环纤维素的δ〜(13)C值提高了约1.3 /千。这可能是由于大气污染(SO_x和粉尘)浓度增加限制了气孔的通气率所致。

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