Evaluating impacts of emerald ash borer Agrilus planipennis on forest vegetation in eastern North America Jason S Kilgore Washington amp Jefferson College Benjamin J Dolan The University of Findlay ID: 167397
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Getting ahead of the frontEvaluating impacts of emerald ash borer (Agrilus planipennis) on forest vegetation in eastern North America
Jason S. Kilgore, Washington & Jefferson CollegeBenjamin J. Dolan, The University of FindlaySlide2Slide3
Introduction to North AmericaSlide4
Introduction to North AmericaSlide5
Current distribution of EABSlide6
Impacts thus far
Altered light regimeIncreases PAR and sapling growth (Burr & McCullough 2014)
Altered nutrient cycling & carbon storage
Increase
in non-ash productivity, particularly maples and elms
Productivity does not offset loss of regional ash productivity (Flower et al. 2013)
Inconsistent response by species
Blue ash has higher survival rates than green ash
(Tanis & McCullogh 2012)Slide7
EAB Impacts Study: hypotheses
Rate of ash decline (from EAB detection to mortality) is positively related to water stress via low precipitation and soil particle size across a continental-scale gradient.
Loss of ash from the overstory will allow more light to penetrate to the forest floor, resulting in an increase in density of seedlings and growth rate of saplings.
Light availability in high ash plots is sufficient to shift understory composition from shade-tolerant to more shade-intolerant tree species (Dolan et al., in prep; but see Flower et al. 2013).
Loss of ash will lead to increases in non-native invasive herbaceous and shrub species and cover (Hausman et al. 2010).
The presence and abundance of certain invasive plants (e.g.,
Alliaria petiolata
, non-native
Lonicera
sp.,
Rosa multiflora
,
Rhamnus cathartica
, and
Ailanthus altissima
) have a disproportionate effect on post-invasion diversity, growth rate of native trees, and time to canopy closure.
Slide8Slide9Slide10
Trees:≥2.5 cm DBH at 1.37 mTags, species
Inventory statusDBH, soundness, crown class (opt), height (opt)
Tree damage
PFPP variables (Plot)
20 m
20 mSlide11
Small Stems:
>1.37 m tall, <2.5 cm DBHSpecies, tally
PFPP variables (Subplot)
20 m
20 mSlide12
EAB variables (Plot)EAB Indicators:
Ash ratingAsh tree breakupEAB exit holes
http://labs.russell.wisc.edu/eab/files/2011/06/D-shaped-exit-holes.jpeg
http://vil.carpentersville.il.us/images/EAB/Canopy%20Dieback%20of%20an%20Ash%20Tree.jpgSlide13
Understory variables (Subplot)
Understory Community:Canopy cover Shrub/saplings (0.3-1.37 m tall)Species, tallySlide14
Understory variables (Miniplot)
Understory Community:Woody seedlings and herbaceous plantsSpecies, tally, cover classSlide15
Distribution vectors (GIS)
Distances to:Major roads and expresswaysStreams and rivers
Railroads
Shipping ports
Distribution centers and manufacturers receiving goods on foreign palletsSlide16
Data collectionUndergraduate students
Upper-level ecology or research coursesGeneral ecology, field biology, etc.Slide17
UF (Ohio) and W&J (Pennsylvania)Similar mature ash density (67-71 trees/ha) and overstory (22%)EAB documented in Hancock County (2005) and Washington County (2009)
Ash mortality higher at UF (100%) than W&J (0%, but 23% with EAB symptoms)
Initial results: mature ashSlide18
Initial results: understorySlide19
Curriculum and collaboration
Labs Independent studiesCross-institutional collaboration
Presentations
colleges
conferences
abstractsSlide20Slide21
Questions?Ben Dolan - dolan@findlay.edu
Jason Kilgore - jkilgore@washjeff.eduhttp://erenweb.org/new-page/emerald-ash-borer-project/Slide22Slide23
emerald ash borer (Agrilus planipennis
)Slide24Slide25