The emerald ash borer (EAB) (Agrilus planipennis Fairmaire) (Coleoptera: Buprestidae) has killed hundreds of millions of ash (Fraxinus spp.) trees since it was first identified in 2002 in the greater Detroit, Michigan metropolitan area and in nearby Windsor, Ontario, Canada. Inadvertent spread of infested ash trees, logs and firewood, along with natural dispersal of beetles, have resulted in EAB establishment in at least 27 states, and two Canadian provinces to date1. Recent reports indicate the EAB has also invaded Moscow, Russia, where it is killing landscape ash trees2,3, generating additional concern about its potential spread into Europe. Interspecific variation in EAB host preference and resistance among North American ash species has been documented4,5,6,7,8,9, but virtually all ash species in North America are likely to be suitable hosts. Catastrophic levels of ash mortality have been recorded in areas of Michigan and Ohio10,11,12, with associated ecological and economic impacts13,14,15,16.
Effective methods to detect new EAB infestations and monitor low density populations are critical aspects of managing this invasive pest in urban, residential and forested settings. Early detection provides time to develop a strategy, secure funding and implement activities to reduce impacts of the EAB. For example, municipal officials and homeowners can begin treating valuable ash in landscapes with systemic insecticides before damage caused by increasing larval densities limits efficacy of these products17,18. Similarly, identification of a new infestation and reliable information about local EAB distribution gives foresters and property owners the opportunity to implement timber sales, species conversion or other activities to reduce economic costs or ecological effects of ash mortality.
Early detection, delimitation, and effective monitoring of low-density EAB populations, however, remain difficult. Visual surveys to identify newly infested ash trees are not reliable because ash rarely exhibit external signs or symptoms of EAB infestation until larval densities build to moderate or even high levels4,19. The most effective means of detecting very low densities of EAB involve using girdled ash detection trees19,20,21,22. Ash trees are girdled in spring or early summer by removing a band of outer bark and phloem around the circumference of the trunk, which stresses trees, increasing their attraction to adult EAB beetles. Girdled trees can be debarked in autumn or winter to identify EAB larval presence and density. Although girdled ash trees have been used operationally for EAB detection19,23,24,25, they are problematic. Debarking girdled trees can be labor intensive and locating suitable trees for girdling can be difficult, especially in urban or residential areas or when surveys must be conducted for multiple years19.
Artificial traps baited with EAB attractants eliminate many concerns associated with using girdled ash detection trees. In contrast to other important forest pests such as gypsy moth (Lymantria dispar L) and some Scolytinae bark beetles that produce long distance sex or aggregation pheromones, to date, no effective long-distance pheromones have been found for EAB. A short range sex pheromone, cis-lactone, may facilitate mating26,27, but in field trials, cis-lactone lures have not consistently increased EAB attraction to artificial traps28. Adult beetles rely on volatile compounds emitted by ash leaves, bark and wood to identify their host trees29,30,31 and encounter potential mates. Several volatile compounds have been evaluated for use in lures to attract adult EABs to artificial traps27,32. Currently, traps used operationally for EAB detection surveys in the U.S. are baited with lures containing cis-3-hexenol, a common green leaf volatile produced by ash foliage30,33. In previous years, EAB traps used for U.S. surveys have also been baited with Manuka oil, which is extracted from the New Zealand tea tree (Leptospermum scoparium Forst and Forst ) or Phoebe oil, an extract of the Brazilian walnut tree (Phoebe porosa Mez.); both contain several sesquiterpenes that are also present in ash bark29. Problems with inconsistent supplies of these natural oils, however, have restricted their use.
In addition to host-produced volatiles, adult EAB beetles respond to visual stimuli, including color and light20,32,34,35. Early studies showed EAB adults, which are relatively agile fliers, were rarely captured by black funnel traps baited with various ash volatiles (DGM and TMP, unpublished data). Other trap designs, such as cross-vane traps, were evaluated but the aversion of EAB beetles to dark spaces and shadows limited the effectiveness of these traps.
Development of a three-sided prism, which can be coated with clear insect trapping glue35 to capture beetles, was a substantial improvement in trap design. Attraction of adult EABs to color has also been extensively evaluated in field trials and in laboratory studies with a retinograph34. Results show EAB beetles are consistently attracted to specific shades of green and purple32,36. Prism traps fabricated from colored corrugated plastic are now widely used in EAB survey activities in the U.S. and Canada.
Because EAB adults are strongly attracted to light, beetles are much more likely to colonize open-grown trees than shaded trees20,21. Guidelines for EAB detection surveys in the U.S. required individual prism traps to be suspended from a mid-canopy branch in an ash tree growing along a road or the edge of a wooded area37. In theory, this should ensure that at least one panel of the prism is exposed to sunlight. Operationally, however, prism traps may be partially shadowed by overhead branches or by adjacent or nearby trees. Sticky panel surfaces are frequently blown into foliage, resulting in leaves adhering to and obscuring at least a portion of one or more panels.
Double-decker (DD) traps were developed to integrate multiple visual and olfactory cues to enhance attraction of EAB beetles. Each DD trap is comprised of one green and one purple corrugated plastic prism attached to a 3 m tall schedule 40 polyvinyl chloride (PVC) pipe (10 cm diameter), which is supported by sliding the PVC pipe over a t-post. Using both green and purple prisms is designed to attract both sexes of EAB beetles32,36,38,39. Additionally, rather than being suspended from a branch in the canopy of an ash tree, the DD traps are placed in full sun, 5-10 m away from ash trees along the edge of a wooded area or in the midst of scattered, open-grown ash trees.