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Evaluating pole cutting survival and growth for riparian forest restoration during invasion by polyphagous shot hole borer.

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Title: Evaluating pole cutting survival and growth for riparian forest restoration during invasion by polyphagous shot hole borer.
Authors: Bennett, Shelley K.1 (AUTHOR), Lambert, Adam M.2,3 (AUTHOR) alambert@ucsb.edu, Carey, Sean P.2 (AUTHOR), Braman, Charles A.2 (AUTHOR)
Source: Restoration Ecology. Jul2022, Vol. 30 Issue 5, p1-13. 13p.
Subjects: Forest restoration, Riparian forests, Riparian restoration, Life history theory, Introduced insects, Rooting of plant cuttings, Plant cuttings, Shrubs
Abstract: The investment to restore riparian systems necessitates employing data‐driven planning, implementation, and management. To evaluate the demography/growth of riparian plants established vegetatively, we measured 3 years of survival and biometrics for five tree/shrub species experimentally planted as pole cuttings within a large restoration program in a Mediterranean‐climate riparian system. During the experiment, a recently introduced ambrosia beetle, Euwallacea whitfordiodendrus (polyphagous shot hole borer), colonized pole cuttings, providing an opportunity to evaluate beetle establishment rates among species. Pole cutting survival varied significantly among species and reflected their relative ability to propagate vegetatively. Baccharis salicifolia had over 90% survival, while Salix lasiolepis and S. laevigata had intermediate, and Populus trichocarpa and P. fremontii had low survival. Canopy growth reflected species life histories. The small tree/shrub, S. lasiolepis, had robust early growth, while slower growing, larger tree species (S. laevigata, P. trichocarpa, and P. fremontii) filled in canopy later. Only S. lasiolepis was colonized by E. whitfordiodendrus during the second year and had the greatest infestation rates in all years. All species except B. salicifolia were infested by the third year. Beetles tended to colonize larger trees. Our observed survival and growth trends can serve as a guide for estimating planting density and vegetation structural development over time, and to inform adaptive management of riparian species of Mediterranean‐climate and other arid‐land systems. Ecosystem stressors, such as invasive insects and their impacts to plant growth, must be considered during restoration as introductions are anticipated to continue with increased severity with climate change. [ABSTRACT FROM AUTHOR]
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Database: Engineering Source
Description
Abstract:The investment to restore riparian systems necessitates employing data‐driven planning, implementation, and management. To evaluate the demography/growth of riparian plants established vegetatively, we measured 3 years of survival and biometrics for five tree/shrub species experimentally planted as pole cuttings within a large restoration program in a Mediterranean‐climate riparian system. During the experiment, a recently introduced ambrosia beetle, Euwallacea whitfordiodendrus (polyphagous shot hole borer), colonized pole cuttings, providing an opportunity to evaluate beetle establishment rates among species. Pole cutting survival varied significantly among species and reflected their relative ability to propagate vegetatively. Baccharis salicifolia had over 90% survival, while Salix lasiolepis and S. laevigata had intermediate, and Populus trichocarpa and P. fremontii had low survival. Canopy growth reflected species life histories. The small tree/shrub, S. lasiolepis, had robust early growth, while slower growing, larger tree species (S. laevigata, P. trichocarpa, and P. fremontii) filled in canopy later. Only S. lasiolepis was colonized by E. whitfordiodendrus during the second year and had the greatest infestation rates in all years. All species except B. salicifolia were infested by the third year. Beetles tended to colonize larger trees. Our observed survival and growth trends can serve as a guide for estimating planting density and vegetation structural development over time, and to inform adaptive management of riparian species of Mediterranean‐climate and other arid‐land systems. Ecosystem stressors, such as invasive insects and their impacts to plant growth, must be considered during restoration as introductions are anticipated to continue with increased severity with climate change. [ABSTRACT FROM AUTHOR]
ISSN:10612971
DOI:10.1111/rec.13578