Jech Sierra D, Havrilla Caroline A, Barger Nichole N
Department of Ecology and Evolutionary Biology, University of Colorado Boulder, Boulder, CO, United States.
Department of Forest and Rangeland Stewardship, Colorado State University, Fort Collins, CO, United States.
Front Microbiol. 2023 Aug 3;14:1176760. doi: 10.3389/fmicb.2023.1176760. eCollection 2023.
Up to 35% of global drylands have experienced degradation due to anthropogenic impacts, including physical disturbances like trampling and soil removal. These physical disturbances can result in the loss of soil communities known as biological soil crusts (biocrusts) and the important functions they provide, such as soil stability and fertility. The reestablishment of biocrust organisms after disturbance is determined by many factors, including propagule availability, climate, and vascular plant community structure. The role of these factors in natural recovery may be intensified by the extent (or size) of a disturbance. For example, large disturbances can result in reduced propagule availability or enhanced erosion, which impact both the dispersal and establishment of biocrust organisms on disturbed soils, leading to a slower natural recovery. To test how disturbance extent impacts biocrust's natural recovery, we installed four disturbance extents by completely removing biocrust from the mineral soil in plots ranging from 0.01 m to 1 m and measured productivity and erosion resistance. We found that small disturbance extents did not differ in chlorophyll a content, total exopolysaccharide content, or soil stability after 1.5 years of natural recovery. However, the concentration of glycocalyx exopolysaccharide was higher in the smallest disturbances after the recovery period. Our results indicate that disturbances <1 m in scale recover at similar rates, with soil stability returning to high levels in just a few years after severe disturbance. Our findings align with prior work on biocrust natural recovery in drylands and highlight the opportunity for future work to address (1) cyanobacteria, moss, and lichen propagule dispersal; (2) rates and mechanisms of biocrust succession; and (3) the role of wind or water in determining biocrust colonization patterns as compared to lateral growth.
由于包括践踏和土壤移除等物理干扰在内的人为影响,全球高达35%的旱地已经经历了退化。这些物理干扰会导致被称为生物土壤结皮(生物结皮)的土壤群落及其所提供的重要功能丧失,比如土壤稳定性和肥力。干扰后生物结皮生物的重新建立由许多因素决定,包括繁殖体可用性、气候和维管植物群落结构。这些因素在自然恢复中的作用可能会因干扰的程度(或规模)而增强。例如,大规模干扰会导致繁殖体可用性降低或侵蚀加剧,这会影响生物结皮生物在受干扰土壤上的扩散和定殖,导致自然恢复速度变慢。为了测试干扰程度如何影响生物结皮的自然恢复,我们通过在面积从0.01平方米到1平方米的样地中完全去除矿质土壤上的生物结皮,设置了四种干扰程度,并测量了生产力和抗侵蚀能力。我们发现,经过1.5年的自然恢复后,小干扰程度样地的叶绿素a含量、总胞外多糖含量或土壤稳定性没有差异。然而,恢复期后最小干扰程度样地的糖萼胞外多糖浓度更高。我们的结果表明,规模小于1米的干扰以相似的速度恢复,在严重干扰后的短短几年内土壤稳定性就会恢复到较高水平。我们的研究结果与之前关于旱地生物结皮自然恢复的工作一致,并突出了未来工作在以下方面的机会:(1)蓝细菌、苔藓和地衣繁殖体的扩散;(2)生物结皮演替的速率和机制;(3)与横向生长相比,风和水在决定生物结皮定殖模式中的作用。