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Biological soil crusts as an integral component of desert environments

机译:生物土壤结皮是沙漠环境的组成部分

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The biology and ecology of biological soil crusts, a soil surface community of mosses, lichens, cyanobacteria, green algae, fungi, and bacteria, have only recently been a topic of research. Most efforts began in the western U.S. (Cameron, Harper, Rushforth, and St. Clair), Australia (Rogers), and Israel (Friedmann, Evenari, and Lange) in the late 1960s and 1970s (e.g., Friedmann et al. 1967; Evenari 1985reviewed in Harper and Marble 1988). However, these groups worked independently of each other and, in fact, were often not aware of each other’s work. In addition, biological soil crust communities were seen as more a novelty than a critical component of dryland ecosystems. Since then, researchers have investigated many different aspects of these communities and have shown that although small to microscopic, biological soil crusts are critical in many ecological processes of deserts. They often cover most of desert soil surfaces and substantially mediate inputs and outputs from desert soils (Belnap et al. 2003). They can be a large source of biodiversity for deserts, as they can contain more species than the surrounding vascular plant community (Rosentreter 1986). These communities are important in reducing soil erosion and increasing soil fertility through the capture of dust and the fixation of atmospheric nitrogen and carbon into forms available to other life forms (Elbert et al. 2012). Because of their many effects on soil characteristics, such as external and internal morphological characteristics, aggregate stability, soil moisture, and permeability, they also affect seed germination and establishment and local hydrological cycles. Covering up to 70% of the surface area in many arid and semi-arid regions around the world (Belnap and Lange 2003), biological soil crusts are a key component within desert environments.
机译:生物土壤结皮的生物学和生态学,苔藓,地衣,蓝细菌,绿藻,真菌和细菌的土壤表面群落直到最近才成为研究的主题。大多数努力始于1960年代末和1970年代末的美国西部(Cameron,Harper,Rushforth和St. Clair),澳大利亚(Rogers)和以色列(Friedmann,Evenari和Lange)(例如Friedman等1967; 1993年)。 Evenari 1985(在Harper和Marble 1988中进行了评论)。但是,这些小组彼此独立工作,实际上,他们通常并不了解彼此的工作。此外,人们认为生物土壤结壳群落比旱地生态系统的关键组成部分更具新颖性。从那时起,研究人员对这些群落的许多不同方面进行了调查,结果表明,尽管从微小到微观,生物土壤结壳在沙漠的许多生态过程中都至关重要。它们通常覆盖大部分沙漠土壤表面,并在很大程度上介导沙漠土壤的输入和输出(Belnap等,2003)。它们可能是沙漠生物多样性的主要来源,因为它们所包含的物种比周围的维管植物群落还多(Rosentreter 1986)。这些社区对于减少土壤侵蚀和通过捕获灰尘并将大气中的氮和碳固定为其他生命形式可用的土壤而言,具有重要意义(Elbert等,2012)。由于它们对土壤特征的许多影响,例如外部和内部形态特征,聚集体稳定性,土壤湿度和渗透性,它们还影响种子的发芽,结实和局部水文循环。在世界许多干旱和半干旱地区,生物土壤结壳覆盖了70%的表面积(Belnap和Lange 2003),是沙漠环境中的关键组成部分。

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