低北极苔原灌木林对土壤形态特征的影响

S. Loiko, D. Kuzmina, G. Istigechev, I. V. Kritskov, A. Lim, N. Klimova, A. Novoselov, A. Konstantinov, Elvira V. Novolodskaya, S. P. Kulizhsky
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The coordinates of the center of alder shrubs are N67°22'17.4'', E78°42'11.7'' (Fig. 1). The formation of alder shrubs at the study site began no later than 1957. We studied 34 soil profiles. Of these, eight soil profiles were studied in the tundra, eight more in the tundra ecotone and alder shrubs. Eighteen soil profiles characterized the periphery or central zone of alder shrubs (Fig. 2, 3). In the field, we studied the vegetation, the depth of permafrost, photographed soil profiles, and took samples of soil horizons and a micromonolith. We quantified soil morphological parameters such as soil horizon boundary depth, soil horizon thickness, thixotropy index, gley patch percentage, root penetration depth, charcoal abundance, and horizon coloration in the CIE-L*a*b* system. A topographic survey was made within the key site. The age of shrubs and the relief form for each soil profile were determined. The obtained values were processed using the methods of basic statistics and the method of principal components. The studied alder shrubs in the Taz Tundra are located in the upper part of the slopes of stream valleys. The expansion of shrubs at the key site has been observed since the beginning of the second half of the 20th century. For the key site with alder, the succession stages of transformation of tundra into a shrub ecosystem are described. At the first stage, only a few young shoots of alder are observed in tundra (Fig. 10). Alder appears as a result of seed germination on devoid of vegetation areas of cryoturbated soils (patterned-ground). Alder actively colonizes the territory adjacent to the original places of germination, which leads to the expansion of the original range and the concentric structure of shrubs. The second stage is represented by tundra and alder ecotone. 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Alder leaves susceptible to decomposition fall on the soil surface, which is important for earthworms and has a priming effect for the decomposition of tundra litter. The depth of the root system increases. An increase in evapotranspiration leads to a decrease in soil moisture and disappearance of their thixotropic properties. The area of gley patches in soils decreases (Fig. 6). The thickness of peat and litter horizons decreases (Fig. 7). Initially, thixotropic horizons are structured according to the ooid type (Fig. 8). Root and animal tunnels, which are stable in seasonal cycles, are formed in the soil. The resulting pores and soil aggregates allow the development of soil mesofauna. All the above mentioned cause formation of humus-accumulative horizons on convex slopes under alder. Reductaquic Cryosols and Folic Reductaquic Cryosols evolve into Gleyic Cambisol, Stagnic Cambisol (Ochric), and Gleysol (Ochric). 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引用次数: 1

摘要

亚北极地区的气候变暖导致灌木生态系统的扩张。最常见的高原冻土带灌木是桤木与矮桦树和柳树的结合。然而,在低北极苔原土壤形态特征的变化的性质和速率在灌木化期间仍然是未知的。为了研究新灌丛生态系统对冻土带土壤的影响,我们以西伯利亚西部冻土带南部的桤木灌丛为研究对象。关键地点位于塔兹河和普尔河之间。塔佐夫斯基村,亚马尔-涅涅茨自治区(俄罗斯)就在附近。这个地区被称为塔兹冻土带,靠近它向森林冻土带的过渡。桤木灌木中心坐标为N67°22′17.4”,E78°42′11.7”(图1)。研究地点桤木灌木的形成不迟于1957年。我们研究了34个土壤剖面。其中,在冻土带研究了8个土壤剖面,在冻土带过渡带和桤木灌木中研究了8个土壤剖面。18个土壤剖面显示了桤木灌木的外围或中心地带(图2、3)。在野外,我们研究了植被、永久冻土的深度、土壤剖面的照片,并采集了土壤层和一个小整体的样本。我们量化了CIE-L*a*b*体系的土壤形态参数,如土壤水平边界深度、土壤水平厚度、触变性指数、灰色斑块百分比、根系穿透深度、木炭丰度和水平颜色。在关键地点内进行了地形调查。确定了各土壤剖面灌木的年龄和地形形态。利用基本统计方法和主成分法对所得值进行处理。研究对象是塔兹冻土带的桤木灌木,分布在溪谷斜坡的上部。自20世纪下半叶开始,在关键地点观察到灌木的扩张。对桤木关键样地,描述了冻土带向灌木生态系统转变的演替阶段。在第一阶段,在冻土带上只观察到少量的桤木幼芽(图10)。桤木的出现是由于种子萌发在低温土壤(斑纹地)的无植被区域。桤木主动向原发芽地附近的领地殖民,导致原范围扩大,灌木呈同心圆结构。第二阶段以冻土带和桤木过渡带为代表。在这个交错带,桤木的盖度和高度增加,原始灌木(矮桦和野生迷迭香)的生境也增加。土壤性质的主要变化与活性层厚度的增加有关。第三阶段是桤木灌木的外围部分,此时桤木高度最大,达到4.5 m。第四阶段是桤木灌木的中心地带,在那里出现了芦苇-莎草草地和杂草。在桤木灌木消失的地方形成了草地。第三和第四阶段的主要变化与土壤形成的热液条件的根本改善有关,这导致永久冻土表面加深至3-4.5 m,形成了一个通道。固氮桤木使土壤富氮,从而提高土壤肥力。桤木易分解的叶片落在土壤表面,这对蚯蚓很重要,对冻土带凋落物的分解有启动作用。根系的深度增加。蒸散量的增加导致土壤水分的减少和触变特性的消失。土壤中沟斑的面积减少(图6)。泥炭层和凋落物层的厚度减少(图7)。最初,触变层按照卵型构造(图8)。土壤中形成了在季节循环中稳定的根系和动物隧道。由此产生的孔隙和土壤团聚体使土壤中动物群得以发育。这些都导致了桤木下凸坡上腐殖质堆积层的形成。还原性低温溶胶和叶酸性低温溶胶演化为Gleyic Cambisol、stagic Cambisol (Ochric)和Gleysol (Ochric)。因此,我们的研究证实了这样的假设:在几十年的时间里,灌丛扩张过程中苔原植被的急剧变化导致了土壤形态特征的显著分类变化。文章包含10幅图,79篇参考文献。作者声明无利益冲突。
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The Transformation of Morphological Properties of Soils Due to the Low Arctic Tundra Shrubification
Climate warming in the Subarctic leads to the expansion of shrub ecosystems. The most common upland tundra shrubification is by alder in combination with dwarf birch and willows. However, the nature and rate of changes in the morphological properties of soils in the low arctic tundra during shrubification remain unknown. To study the impact of new shrub ecosystems on tundra soils, we studied alder shrubs in the south of the Western Siberian tundra. The key site is located between the rivers Taz and Pur. The village of Tazovsky, Yamalo-Nenets Autonomous Okrug (Russia) is located nearby. This area is called the Taz tundra, near its transition to the forest tundra. The coordinates of the center of alder shrubs are N67°22'17.4'', E78°42'11.7'' (Fig. 1). The formation of alder shrubs at the study site began no later than 1957. We studied 34 soil profiles. Of these, eight soil profiles were studied in the tundra, eight more in the tundra ecotone and alder shrubs. Eighteen soil profiles characterized the periphery or central zone of alder shrubs (Fig. 2, 3). In the field, we studied the vegetation, the depth of permafrost, photographed soil profiles, and took samples of soil horizons and a micromonolith. We quantified soil morphological parameters such as soil horizon boundary depth, soil horizon thickness, thixotropy index, gley patch percentage, root penetration depth, charcoal abundance, and horizon coloration in the CIE-L*a*b* system. A topographic survey was made within the key site. The age of shrubs and the relief form for each soil profile were determined. The obtained values were processed using the methods of basic statistics and the method of principal components. The studied alder shrubs in the Taz Tundra are located in the upper part of the slopes of stream valleys. The expansion of shrubs at the key site has been observed since the beginning of the second half of the 20th century. For the key site with alder, the succession stages of transformation of tundra into a shrub ecosystem are described. At the first stage, only a few young shoots of alder are observed in tundra (Fig. 10). Alder appears as a result of seed germination on devoid of vegetation areas of cryoturbated soils (patterned-ground). Alder actively colonizes the territory adjacent to the original places of germination, which leads to the expansion of the original range and the concentric structure of shrubs. The second stage is represented by tundra and alder ecotone. In this ecotone, the cover and height of alder increase, and so does the habitus of the original shrubs (dwarf birch and wild rosemary). The main transformations of soil properties are associated with an increase in the active layer thickness. The third stage is the peripheral part of the alder shrubs, where the height of the alder is maximum and reaches 4.5 m. The fourth stage is the central zone of the alder shrubs, where there appear reed-sedge meadows with fireweed. Meadows form in places where the alder bushes died out. The main changes at the third and fourth stages are associated with a radical improvement in the hydrothermal conditions of soil formation, which leads to deepening of the permafrost surface to 3-4.5 m, and a talik is formed. Soil fertility increases due to its enrichment with nitrogen by nitrogen-fixing alder. Alder leaves susceptible to decomposition fall on the soil surface, which is important for earthworms and has a priming effect for the decomposition of tundra litter. The depth of the root system increases. An increase in evapotranspiration leads to a decrease in soil moisture and disappearance of their thixotropic properties. The area of gley patches in soils decreases (Fig. 6). The thickness of peat and litter horizons decreases (Fig. 7). Initially, thixotropic horizons are structured according to the ooid type (Fig. 8). Root and animal tunnels, which are stable in seasonal cycles, are formed in the soil. The resulting pores and soil aggregates allow the development of soil mesofauna. All the above mentioned cause formation of humus-accumulative horizons on convex slopes under alder. Reductaquic Cryosols and Folic Reductaquic Cryosols evolve into Gleyic Cambisol, Stagnic Cambisol (Ochric), and Gleysol (Ochric). Thus, our study confirmed the hypothesis that the radical change of tundra vegetation during the expansion of shrubs causes significant classificatory changes in the morphological properties of soils over several decades. The article contains 10 figures, 79 references. The Authors declare no conflict of interest.
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