Gornish Elise S, Lennox Michael S, Lewis David, Tate Kenneth W, Jackson Randall D
Department of Plant Sciences, University of California Davis, Davis, CA, United States of America.
University of California Cooperative Extension, Marin/Sonoma/Mendocino Counties, Novato, CA, United States of America.
PLoS One. 2017 Apr 27;12(4):e0176338. doi: 10.1371/journal.pone.0176338. eCollection 2017.
Understanding the efficacy of passive (reduction or cessation of environmental stress) and active (typically involving planting or seeding) restoration strategies is important for the design of successful revegetation of degraded riparian habitat, but studies explicitly comparing restoration outcomes are uncommon. We sampled the understory herbaceous plant community of 103 riparian sites varying in age since restoration (0 to 39 years) and revegetation technique (active, passive, or none) to compare the utility of different approaches on restoration success across sites. We found that landform type, percent shade, and summer flow helped explain differences in the understory functional community across all sites. In passively restored sites, grass and forb cover and richness were inversely related to site age, but in actively restored sites forb cover and richness were inversely related to site age. Native cover and richness were lower with passive restoration compared to active restoration. Invasive species cover and richness were not significantly different across sites. Although some of our results suggest that active restoration would best enhance native species in degraded riparian areas, this work also highlights some of the context-dependency that has been found to mediate restoration outcomes. For example, since the effects of passive restoration can be quite rapid, this approach might be more useful than active restoration in situations where rapid dominance of pioneer species is required to arrest major soil loss through erosion. As a result, we caution against labeling one restoration technique as better than another. Managers should identify ideal restoration outcomes in the context of historic and current site characteristics (as well as a range of acceptable alternative states) and choose restoration approaches that best facilitate the achievement of revegetation goals.
了解被动(减少或消除环境压力)和主动(通常涉及种植或播种)恢复策略的效果对于设计退化河岸栖息地的成功植被恢复至关重要,但明确比较恢复结果的研究并不常见。我们对103个河岸地点的林下草本植物群落进行了采样,这些地点的恢复时间(0至39年)和植被恢复技术(主动、被动或无)各不相同,以比较不同方法对各地点恢复成功的效用。我们发现,地形类型、遮荫百分比和夏季流量有助于解释所有地点林下功能群落的差异。在被动恢复的地点,草和杂类草的覆盖度和丰富度与地点年龄呈负相关,但在主动恢复的地点,杂类草的覆盖度和丰富度与地点年龄呈负相关。与主动恢复相比,被动恢复的本地植物覆盖度和丰富度较低。各地点入侵物种的覆盖度和丰富度没有显著差异。虽然我们的一些结果表明,主动恢复最能增强退化河岸地区的本地物种,但这项工作也突出了一些已被发现介导恢复结果的背景依赖性。例如,由于被动恢复的效果可能相当迅速,在需要先锋物种迅速占据主导地位以阻止通过侵蚀造成的大量土壤流失的情况下,这种方法可能比主动恢复更有用。因此,我们提醒不要将一种恢复技术标记为比另一种更好。管理者应根据历史和当前的地点特征(以及一系列可接受的替代状态)确定理想的恢复结果,并选择最有助于实现植被恢复目标的恢复方法。