School of Forestry, Northern Arizona University, 200 East Pine Knoll Drive, Flagstaff, Arizona, 86011, USA.
MPG Ranch, 1001 South Higgins Avenue STE 3A, Missoula, Montana, 59801, USA.
Ecol Appl. 2017 Sep;27(6):1958-1969. doi: 10.1002/eap.1582. Epub 2017 Aug 17.
Degraded rangelands around the world may benefit from the reestablishment of lost biological soil crusts (biocrusts, soil surface cryptogamic-microbial communities). Cultivation of biocrust organisms is the first step in this process, and may benefit from harnessing species interactions. Species interactions are a dominant force structuring ecological communities. One key element of community structure, species richness, is itself important because it can promote the productivity of the entire community. Here, we use biological soil crusts as a model to test the effects of species interactions on production of biocrust materials for use in ecosystem rehabilitation. We screened eight different moss and lichen species from semiarid rangelands of Montana, USA, for growth potential under two watering regimes. Mosses generally grew well, but we were unable to cultivate the selected lichen species. We produced a >400% increase in the biomass of one species (Ceratodon purpureus). We tested whether a parasite-host relationship between two lichens could be used to enhance productivity of the parasite species, but this also resulted in no net gain of lichen productivity. Finally, we constructed all possible community combinations from a pool of five moss species to test for overyielding (community productivity exceeding that expected from the growth of community members in monoculture), and to determine both if, and the mode in which, species richness increases productivity. Polycultures yielded more than would be expected based upon the production of community constituents in monoculture. Using structural equation models, we determined that there was a modest effect of species richness on community productivity (r = 0.24-0.25), which was independent of a stronger effect of the identity of species in the community (r = 0.41-0.50). These results will contribute to the optimization of biocrust cultivation, promoting the development of this emerging ecological rehabilitation technology.
退化的世界各地的牧场可能受益于重新建立失去的生物土壤结皮(biocrusts,土壤表面cryptogamic-微生物群落)。培养biocrust 生物是这个过程的第一步,并且可以受益于利用物种相互作用。物种相互作用是构造生态群落的主要力量。群落结构的一个关键要素是物种丰富度,因为它本身很重要,因为它可以促进整个群落的生产力。在这里,我们使用生物土壤结皮作为模型来测试物种相互作用对生物结皮材料生产的影响,这些材料可用于生态系统恢复。我们从美国蒙大拿州的半干旱牧场筛选了 8 种不同的苔藓和地衣物种,以在两种浇水制度下测试其生长潜力。苔藓一般生长良好,但我们无法培养所选地衣物种。我们使一种物种(Ceratodon purpureus)的生物量增加了超过 400%。我们测试了两种地衣之间的寄生虫-宿主关系是否可以用来提高寄生虫物种的生产力,但这也没有导致地衣生产力的净收益。最后,我们从 5 种地衣物种池中构建了所有可能的群落组合,以测试超产量(群落生产力超过群落成员在纯培养中生长的预期),并确定物种丰富度是否以及以何种方式提高生产力。混养的产量超过了单培养中群落成分的产量预期。使用结构方程模型,我们确定物种丰富度对群落生产力有适度的影响(r = 0.24-0.25),这独立于群落中物种身份的更强影响(r = 0.41-0.50)。这些结果将有助于优化生物结皮的培养,促进这种新兴生态恢复技术的发展。