

The emerald ash borer, Agrilus planipennis Fairmaire, is an invasive insect species that was first found in North America in June 2002. Shortly after the Detroit, Michigan discovery, forest health monitoring staff from the Ontario Ministry of Natural Resources (OMNR) and Canadian Forest Service (CFS) determined the beetle was also present in Windsor, Ontario. The Canadian Food Inspection Agency (CFIA) was immediately notified. Surveys conducted in Canada and the U.S. found the beetle was well-established in the Detroit and Windsor areas.
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The emerald ash borer is an invasive insect which attacks all species of ash trees in North America
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Emerald ash borer is now found throughout much of Essex County and part of Chatham-Kent in Ontario. In Michigan, the beetle is concentrated in the southeastern portion of the state, but has also spread to multiple locations in the Lower Peninsula and as far north as the Mackinac Bridge. Spot infestations have also been found in Ohio and Maryland. Researchers, regulators, and urban foresters are in a race to halt the spread of the insect long enough to develop effective control measures to save native ash trees, an important hardwood species in North America.
Emerald ash borer adults are metallic green, 8.5 to 13.5 mm long, and slender. The head is flattened, with black compound eyes that cover most of the side of the head. Short antennae extend from the face, then curve back to just past the eyes. The upper side of the abdomen is copper to purplish, and is visible when the wings are open.
Eggs are light yellow or cream-coloured, turning yellow-brown prior to hatching. They are approximately 1mm long and 0.6 mm in diameter, and are very difficult to spot on the tree.
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Emerald ash borer larva grow to between 26 to 32 mm in length. The adult beetle measures 8.5 and 13mm |
Larvae are slender, cream-coloured, flattened, with a brown head. Mature larvae are 26-32 mm long and have a pair of brown pinchers at the tip.
Pupae are10-14 mm long, cream-coloured, with terminal abdominal segments that curve upwards. Antennae extend to the base of the wings.
Ash trees in Ontario and much of the north central region of the U.S. have been exhibiting a range of poor tree health conditions, including generalized crown dieback, leaf diseases and drought. Thorough investigation is critical in identifying whether symptoms of ash decline are caused by the emerald ash borer or some other factor.
Tunnels are oriented vertically, shallow, meander under the bark with abrupt turns and are packed with frass (sawdust-like waste). Total length of the tunnels may be 50cm. Galleries are exposed 1-2 years after tree death as bark sloughs off.
Vertical splits in the bark over larval galleries are often present and are usually 7-10 cm long. The cracks are more noticeable on young or pole-sized trees than on older trees with thick bark where close inspection is required to distinguish the bark splits from normal expansion caused by vigorous growth. Removing the bark will expose the galleries and larvae, if present.
Once fully mature, the adult beetle will emerge through an exit hole it has chewed through the bark. These exit holes are distinctly D-shaped and measure 3.5-4.1 mm across. Exit holes may be found anywhere on the tree trunk, root flare, exposed roots or in the crown. Sawdust may be visible in the exit hole or on the bark just outside it, especially in June and July.
Severely attacked trees may exhibit crown dieback from the top down in the first year of infestation. Often, one-third to one-half of the branches die in one year and the entire tree dies the following year. Foliage may wilt or turn yellow during the growing season. New, or epicormic, branches are common on the trunk of dying trees and dense root sprouts are often present at the base of dead trees or around stumps of cut trees.
Woodpeckers are very good at finding larvae under the bark. Look for increased woodpecker feeding activity in the trees or for signs of their probing of the bark.
All ash trees native to North America appear to be susceptible to attack. Anecdotal evidence suggests green ash and red ash appear to be preferred over white ash, followed by blue ash, black ash, or European black ash. There is no clear evidence that these latter species are
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All species of native ash are susceptible to attack by the emerald ash borer
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Ash is an important species because it grows readily in disturbed habitats where it can be a major component of woodlots, fence rows or shelterbelts. They often grow along stream banks where they provide wildlife habitat, shelter, soil protection, and bank stabilization. Ash species are also important to wildlife because of their seed production which serves as an important food source. Commercially, ash wood is used for flooring, furniture, sports equipment, native baskets and items, tool handles and numerous products requiring strong, hard wood with less rigidity than maple.
Although literature from China indicated the insect also attacked a few other hardwood species (elm, walnut, Japanese wingnut), only ash trees have been attacked in North America.
Initial 2002 surveys indicated the emerald ash borer had infested six Michigan counties, but only the western portion of Essex County was thought to be infested in Ontario.
Examinations of the trees indicated the beetle first appeared in Michigan where tree mortality suggested the infestation was 5-7 years old. At the same time in southern Ontario, there was very little, if any, tree mortality associated with the emerald ash borer indicating the Ontario infestation was much more recent.
Surveys have continued since 2002. By the end of 2004, most of Essex County was infested and spot infestations were found in Chatham-Kent in Ontario. In Michigan ’s Lower Peninsula, the infestation covered 20 counties in the southeastern portion, with outlying populations detected in 19 other counties. Spot infestations were also found in northern Indiana, as well as six counties in Ohio and two in Maryland.
The spot infestations clearly demonstrate the need for effective, ongoing surveys and the need to prevent people from spreading the beetle through the movement of infested materials. The US infestations outside Michigan likely originated from the transport of infested firewood and nursery stock. A similar situation has occurred in Ontario where firewood operations and movement of logs is thought to have spread the beetle into Chatham-Kent.
Immediately upon discovering the beetle, the Michigan Department of Agriculture (MDA) imposed a quarantine banning the movement of ash material (logs, trees, branches, firewood) out of the known infested counties. The CFIA imposed a similar quarantine in the western portion of Essex County in September 2002, but went one step further to include restrictions on firewood of all species. Marshalling yards were established for residents and contractors to bring potentially-infested ash material for disposal.
The quarantines have since expanded as new infestations have been found. The MDA’s quarantine in Michigan was expanded from 13 counties in 2003 to 20 counties in 2004. The state-level MDA quarantine was augmented by a federal quarantine by the U.S. Department of Agriculture, Animal and Plant Health Inspection Service (APHIS) in October 2003. State-level quarantines also exist in Ohio, Indiana, and Maryland.
In Ontario, there are three separate areas regulated by the CFIA: Essex County, the Municipality of Chatham-Kent, and the Ash-Free Zone. Essex County and the Municipality of Chatham-Kent are under separate ministerial orders that restrict the movement of ash material and firewood. The Ash-Free Zone (AFZ), created by the CFIA as a barrier to the natural spread of the insect, is under a regulation that restricts the movement of ash material and firewood, as well prohibiting the growing of ash trees.
Scientists in the United States and Canada are collaborating on a comprehensive research program to answer questions about the insect’s life cycle, feeding habits, host tree selection, reproduction, mate selection, dispersal, and impacts on trees in urban and rural forests.
Several studies have examined ways to control the beetle through the use of insecticides applied to the tree foliage or injected into the trees. There has also been research into biological control using predators, parasites, or diseases. One of the most challenging areas of investigation has been the attempt to find a reliable early detection method using symptoms of attack, aerial surveys, host chemicals, or traps to detect adult beetles.
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