scholarly journals Ecological Impacts of Emerald Ash Borer in Forests at the Epicenter of the Invasion in North America

Forests ◽  
2018 ◽  
Vol 9 (5) ◽  
pp. 250 ◽  
Author(s):  
Wendy Klooster ◽  
Kamal Gandhi ◽  
Lawrence Long ◽  
Kayla Perry ◽  
Kevin Rice ◽  
...  
Forests ◽  
2020 ◽  
Vol 11 (9) ◽  
pp. 949
Author(s):  
Jordan M. Marshall

Emerald ash borer is an invasive pest in North American forests. Ecological impacts of ash mortality from emerald ash borer are wide-ranging, including shifts in insect communities and wildlife behavior. Additionally, loss of ash from forests may have important implications regarding plant succession. Surveys of overstory, midstory, and understory trees within forests in northeastern Indiana, Lower Peninsula of Michigan, and northwestern Ohio were conducted to quantify the change in forest composition over a 10 year period. Interpolation of ash dominance illustrated inversion of live and dead ash values between 2007 and 2017. Even though more than 83% of overstory live ash basal area was lost across the study area, green ash was the most abundant midstory and understory species representing regeneration. Additionally, loss of ash from many of the sites resulted in compositional changes that were greater than merely the subtraction of ash. Due to the relatively large number of forest types with which ash species are associated, loss of ash will have broad ecological consequences, including on community composition.


2005 ◽  
Vol 51 (3) ◽  
pp. 152-165 ◽  
Author(s):  
David Cappaert ◽  
Deborah G. McCullough ◽  
Therese M. Poland ◽  
Nathan W. Siegert

Author(s):  
Deborah G McCullough

Abstract Emerald ash borer (EAB) (Agrilus planipennis Fairmaire), discovered in southeastern Michigan, USA in 2002, has become the most destructive and costly invasive forest insect in North America. This phloem-boring beetle has also invaded Moscow, Russia and continued spread of EAB potentially threatens European ash (Fraxinus spp.) species. This review summarizes EAB life history, including interspecific variation in host preference, invasion impacts and challenges of detecting new infestations and provides an overview of available management tactics. Advances in systemic insecticides, particularly emamectin benzoate products applied via trunk injection, have yielded effective and practical options both to protect individual trees and to slow EAB population growth and ash decline on an area-wide basis without disrupting natural enemies. Economic costs of treating ash are substantially lower than removal costs, retain ecosystem services provided by the trees, reduce sociocultural impacts and conserve genetic diversity in areas invaded by EAB. Girdled ash trees are highly attractive to EAB adults in low-density populations and debarking small girdled trees to locate larval galleries is the most effective EAB detection method. An array of woodpeckers, native larval parasitoids and introduced parasitoids attack EAB life stages but mortality is highly variable. Area-wide management strategies that integrate insecticide-treated trees, girdled ash trap trees and biological control can be adapted for local conditions to slow and reduce EAB impacts.


2015 ◽  
Vol 148 (3) ◽  
pp. 361-370 ◽  
Author(s):  
Jean J. Turgeon ◽  
Jeffrey G. Fidgen ◽  
Krista L. Ryall ◽  
Taylor A. Scarr

AbstractAgrilus planipennis (Coleoptera: Buprestidae), is causing extensive mortality of ash (Fraxinus Linnaeus; Oleaceae) in North America. Once detected in an area, resource managers require methods to obtain estimates that could improve management decisions. We studied the within-crown and within-branch distribution and abundance of A. planipennis feeding galleries by sampling 3-m-long branches from asymptomatic urban ash trees and subdividing each branch into 12 sections of 25 cm each. We found galleries in all 12 sections of some, but not all, branches. Section was a significant source of variation in A. planipennis gallery density/m2 of branch surface area. A comparison of predictive power and efficiency of estimates for samples of increasing length, and for samples of the same length but consisting of different combinations of sections, revealed that those based on the two basal 25-cm sections of a branch from the lower-crown or mid-crown of an asymptomatic tree were less accurate and precise than those based on more sections, but were the most cost effective. Whittling more sections per branch, irrespective of the combinations of branch sections per length, improved predictive power but reduced cost effectiveness. We also observed that crown level was not important, and aspect was only marginally so, when estimating gallery abundance per sampled branch.


2015 ◽  
Vol 147 (3) ◽  
pp. 349-358 ◽  
Author(s):  
Deborah G. McCullough ◽  
Rodrigo J. Mercader ◽  
Nathan W. Siegert

AbstractPractical and effective strategies to manage emerald ash borer (EAB) (Agrilus planipennis Fairmaire; Coleoptera: Buprestidae) are increasingly important given economic and ecological impacts of this invader. While EAB detection remains challenging, tactics are available to protect individual ash (Fraxinus Linnaeus; Oleaceae) trees and slow EAB population growth, thereby delaying ash mortality. Simulations with a coupled map lattice model, parameterised with data from numerous field studies, showed treating trees with a highly effective systemic insecticide (TREE-äge™; emamectin benzoate), would be more effective in slowing EAB population growth than girdling trees to attract ovipositing females then destroying trees before larvae develop, while harvesting ash to reduce available phloem would have the least effect. From 2008 to 2012, cooperators participated in a pilot project to implement an integrated strategy for an EAB infestation in Upper Michigan, United States of America. Ash was inventoried and EAB density monitored using girdled ash detection trees supplemented with baited artificial traps across the >750 km2 project area. While only a tiny fraction of ash trees in the project area were girdled (444–855 trees annually) or injected with TREE-äge™ (<360 roadside trees annually), and treatment distribution was restricted, both treatments slowed EAB population growth. Coupling TREE-äge™ injections with other tactics will likely yield additive or synergistic outcomes.


2012 ◽  
Vol 88 (02) ◽  
pp. 124-130
Author(s):  
Stacey Bowman ◽  
Sandy M. Smith

This article presents a strategy for managing emerald ash borer (EAB) in the St. Lawrence Islands National Park (SLINP), which is located in the United Counties of Leeds and Grenville in eastern Ontario along 100 km of Lake Ontario shoreline and the St. Lawrence River. Background information about EAB and SLINP is followed by an outline of the possible ecological impacts of an EAB infestation on the Park, predictions of where infestations are more likely to occur and how quickly they could spread, whether there will be interactions between EAB-affected stands and invasive vegetation, and whether visitor safety may be compromised. Recommendations to slow the spread of EAB in the Park, prepare for and attempt to mitigate its impacts, contribute to scientific research to better understand it, and conserve ash genetic material include: 1) implement a ban on outside firewood; 2) develop and implement a seed collection program; 3) prioritize invasive vegetation control activities in areas at risk of EAB infestation; 4) establish an EAB detection program for high-traffic areas of the Park; 5) compile a forest resource inventory of the Park and tree inventories of high-traffic areas; 6) conduct branch sampling to determine if EAB is present on Main Duck Island, and if not, consider closing the island to the public; 7) develop and implement a strategic EAB communications plan; and 8) develop a cross-section committee to oversee EAB management.


2013 ◽  
Vol 146 (1) ◽  
pp. 90-105 ◽  
Author(s):  
Philip Careless ◽  
Stephen A. Marshall ◽  
Bruce D. Gill

AbstractThe beetle-hunting wasp, Cerceris fumipennis Say (Hymenoptera: Crabronidae), native to eastern North America, provisions its subterranean nest almost exclusively with adult metallic wood-boring beetles (Coleoptera: Buprestidae), including the destructive emerald ash borer (Agrilus planipennis Fairmaire, EAB). This wasp provides a unique opportunity to survey indigenous and nonindigenous buprestid diversity. We discuss the accessibility, sustainability, and productivity of C. fumipennis with respect to its application as a buprestid surveying and monitoring tool.


2006 ◽  
Vol 12 (1) ◽  
pp. 71-79 ◽  
Author(s):  
Jim R. Muirhead ◽  
Brian Leung ◽  
Colin Overdijk ◽  
David W. Kelly ◽  
Kanavillil Nandakumar ◽  
...  

2015 ◽  
Vol 105 (5) ◽  
pp. 598-606 ◽  
Author(s):  
D.E. Jennings ◽  
J.J. Duan ◽  
P.M. Shrewsbury

AbstractEmerald ash borer (EAB), Agrilus planipennis, is a serious invasive forest pest in North America responsible for killing tens to hundreds of millions of ash trees since it was accidentally introduced in the 1990s. Although host-plant resistance and natural enemies are known to be important sources of mortality for EAB in Asia, less is known about the importance of different sources of mortality at recently colonized sites in the invaded range of EAB, and how these relate to host tree crown condition. To further our understanding of EAB population dynamics, we used a large-scale field experiment and life-table analyses to quantify the fates of EAB larvae and the relative importance of different biotic mortality factors at 12 recently colonized sites in Maryland. We found that the fates of larvae were highly dependent on EAB life stage and host tree crown condition. In relatively healthy trees (i.e., with a low EAB infestation) and for early instars, host tree resistance was the most important mortality factor. Conversely, in more unhealthy trees (i.e., with a moderate to high EAB infestation) and for later instars, parasitism and predation were the major sources of mortality. Life-table analyses also indicated how the lack of sufficient levels of host tree resistance and natural enemies contribute to rapid population growth of EAB at recently colonized sites. Our findings provide further evidence of the mechanisms by which EAB has been able to successfully establish and spread in North America.


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