Utilizing symbiotic relationships and assisted migration in restoration to cope with multiple stressors, and the legacy of invasive species

Lisa M. Markovchick, Abril Belgara‐Andrew, Duncan Richard, Tessa Deringer, K. Grady, K. Hultine, G. Allan, T. Whitham, J. Querejeta, C. Gehring
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Abstract

Climate change has increased the need for forest restoration, but low planting success and limited availability of planting materials hamper these efforts. Invasive plants and their soil legacies can further reduce restoration success. Thus, strategies that optimize restoration are crucial. Assisted migration and inoculation with native microbial symbiont communities have great potential to increase restoration success. However, assisted migrants can still show reduced survival compared to local provenances depending on transfer distance. Inoculation with mycorrhizal fungi, effective if well-matched to plants and site conditions, can have neutral to negative results with poor pairings. Few studies have examined the interaction between these two strategies in realistic field environments where native plants experience the combined effects of soil legacies left by invasive plants and the drought conditions that result from a warming, drying climate.We planted two ecotypes (local climate and warmer climate) of Populus fremontii (Fremont cottonwoods), in soils with and without legacies of invasion by Tamarix spp. (tamarisk), and with and without addition of native mycorrhizal fungi and other soil biota from the warmer climate.Four main results emerged. 1) First year survival in soil legacies left behind after tamarisk invasion and removal was less than one tenth of survival in soil without a tamarisk legacy. 2) Actively restoring soil communities after tamarisk removal tripled first year cottonwood survival for both ecotypes, but only improved survival of the warmer, assisted migrant ecotype trees in year two. 3) Actively restoring soil communities in areas without a tamarisk history reduced first year survival for both ecotypes, but improved survival of the warmer, assisted migrant ecotype trees in year two. 4) By the second year, inoculated assisted migrants survived at five times the rate of inoculated trees from the local ecotype.Results emphasize the detrimental effects of soil legacies left after tamarisk invasion and removal, the efficacy of assisted migration and restoring soil communities alongside plants, and the need to thoughtfully optimize pairings between plants, fungi, and site conditions.
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在恢复过程中利用共生关系和辅助迁移来应对多重压力和入侵物种遗留问题
气候变化增加了对森林恢复的需求,但种植成功率低和种植材料供应有限阻碍了这些努力。入侵植物及其土壤遗留物会进一步降低恢复的成功率。因此,优化恢复的策略至关重要。辅助迁移和接种本地微生物共生群落具有提高恢复成功率的巨大潜力。然而,与本地原产地相比,辅助迁移的存活率仍会因迁移距离而降低。接种菌根真菌,如果与植物和地点条件匹配良好,则会有效,但如果配对不当,则可能产生中性或负面结果。在现实的野外环境中,本地植物会受到入侵植物留下的土壤遗留物以及气候变暖、干燥带来的干旱条件的共同影响,很少有研究对这两种策略之间的相互作用进行研究。我们在有和没有柽柳入侵遗留物的土壤中,以及在有和没有添加本地菌根真菌和其他来自气候温暖地区的土壤生物群的土壤中,种植了两种生态型(当地气候和气候温暖地区)的弗里蒙特木棉(Populus fremontii)。1) 在柽柳入侵和移除后遗留下来的土壤中,第一年的存活率不到没有柽柳遗留的土壤中存活率的十分之一。2)移除柽柳后积极恢复土壤群落,使两种生态型木棉树的第一年存活率提高了两倍,但只提高了较温暖的、协助迁移的生态型树木在第二年的存活率。3) 在没有柽柳历史的地区积极恢复土壤群落,降低了两种生态型树木第一年的存活率,但提高了较温暖的辅助迁移生态型树木第二年的存活率。4) 到了第二年,接种辅助迁移的树木的存活率是接种当地生态型树木的五倍。研究结果强调了柽柳入侵和移除后留下的土壤遗产的有害影响,辅助迁移和恢复土壤群落与植物一起生长的功效,以及深思熟虑地优化植物、真菌和场地条件之间配对的必要性。
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