Marsh.
Identity
Unique IDELEMENT_GLOBAL.2.160163
Element CodePDOLE040B0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
IUCNCritically endangered
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderScrophulariales
FamilyOleaceae
GenusFraxinus
Other Common Namesblack ash (EN) Frêne noir (FR)
Concept ReferenceKartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
Conservation Status
Rank MethodExpertise without calculation
Review Date2016-06-30
Change Date1984-05-16
Edition Date2020-04-29
Edition AuthorsTreher (2020)
Threat ImpactVery high
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences> 300
Rank ReasonsFraxinus nigra occurs in eastern Canada, from southern Manitoba east to Prince Edward Island, and the northeastern and central U.S.A., from Minnesota, Wisconsin, and Illinois eastward to the Mid-Atlantic, as far south as Maryland and Delaware. While the species is wide ranging and has many occurrences, it is suffering serious mortality due to the Emerald Ash Borer and has poor regeneration post infestation. Within six years of an invasion, the species can experience a nearly 100% decline with minimal regeneration. The Conservation Status of this species is under review and expected to be completed by the Fall of 2020.
Range Extent CommentsFraxinus nigra occurs in eastern Canada, from southern Manitoba east to Prince Edward Island, and the northeastern and central U.S.A., from Minnesota, Wisconsin, and Illinois eastward to the Mid-Atlantic, as far south as Maryland and Delaware.
Threat Impact CommentsThe primary threat to this species is mortality and reduced regeneration associated with the Emerald Ash Borer, a phloem-feeding beetle native to Asia. The invasive Emerald Ash Borer (EAB), Agrilus planipennis Fairmaire, 1888, was introduced in Detroit, Michigan from Asia in the 1990s (Haack et al. 2002) and has since caused rangewide declines in ash populations. The beetles feed on the leaves and lay their eggs in crevices of the bark. Larvae feed in the vascular structures during the summer, creating serpentine shaped galleries. They typically prepupae overwinter in the trees with pupation lasting from April-May, when adults emerge. Emerald Ash borers cause significant damage to the foliage of the tree and the vascular tissues. The tree will typically die within two years of the infestation (Poland and McCullough 2006). Within six years of an infestation, up to 99% mortality was observed in ash species (Knight et al. 2013, Klooster et al. 2014, McCullough et al. 2008, Steiner et al. 2019). Green ash appears to suffer the greatest mortality and least regeneration post-invasion (Robinett and McCullough 2019). Tree saplings with 2 or more cm dbh can be infested (McCullough et al. 2008, Aubin et al. 2015). While an infested tree may push out root sprouts for one to two years, the tree usually dies (Klooster et al. 2014). The mass mortality of reproductively mature plants that would replenish the seed bank and the relatively short persistence in the seed bank (2-3(7) years) (Klooster et al. 2014), causes concern about the species ability to regenerate post-infestation. Emerald Ash Borer has been reported in most states and provinces where this species occurs (Emerald Ash Borer Information Network 2020).