白茅屬
入侵物种
生物
竞赛(生物学)
引进物种
生态学
农学
生物量(生态学)
乡土植物
植物生态学
生态系统
作者
Catherine Fahey,S. Luke Flory
标识
DOI:10.1111/1365-2745.13807
摘要
Abstract Invasive plants can alter soil microbial communities and generate positive plant–soil feedbacks that facilitate their performance, but the magnitude and direction of feedbacks may change with novel conditions under climate change. We assessed how potential soil legacy effects of plant invasion and simulated drought influenced plant performance and competition in the longleaf pine ecosystem. We collected soil from a 4‐year factorial invasion (cogongrass Imperata cylindrica ) by drought (simulated with rainout shelters) field experiment and used it as live or sterilized soil inoculum in a greenhouse experiment that included two native foundation species, longleaf pine Pinus palustris and wiregrass Aristida stricta , and cogongrass, grown individually or in competition. There was no evidence of biotic soil legacy effects of invasion or drought for any plant species, but microbes played a significant role in competition. When plants were grown alone, the invader had 12% greater biomass in live soil than sterile soil but both native species had 25% less biomass in live soil. When grown in competition, these effects were reversed for cogongrass (37% smaller in live soil) and pine (17% larger in live soil). In competition, the three species grown in sterile soil produced similar amounts of biomass, whereas live soil created a competitive hierarchy where pine was more competitive than wiregrass and cogongrass. Synthesis . These results emphasize the importance of soil biota in native plant restoration because, although the invader was highly successful when grown alone, plant–microbe interactions influenced the outcome of competition between native and invasive species by promoting native longleaf pine. There was little evidence that invasive cogongrass inhibited native plants via biotic soil legacies, instead, results suggested that plant–soil interactions can be highly resilient to global change such that the biotic legacy of invasion and drought may not promote or inhibit invasion.
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