Fraxinus nigra

Marsh.

Black Ash

G5Secure Found in 9 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Critically endangeredIUCN
Very highThreat Impact
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 Names
black ash (EN) Frêne noir (FR)
Concept Reference
Kartesz, 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 Reasons
Fraxinus 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 Comments
Fraxinus 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 Comments
The 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).
Ecology & Habitat
Other Nations (2)
CanadaN4
ProvinceRankNative
Island of NewfoundlandS2Yes
Nova ScotiaS1Yes
QuebecS3Yes
ManitobaS2Yes
OntarioS4Yes
New BrunswickS3Yes
Prince Edward IslandS2Yes
United StatesN5
ProvinceRankNative
IllinoisS1Yes
MaineSNRYes
PennsylvaniaS5Yes
VirginiaS3Yes
WisconsinS3Yes
MarylandS3Yes
MassachusettsSNRYes
OhioSNRYes
MinnesotaSNRYes
IndianaS2Yes
New JerseyS3Yes
New YorkS5Yes
IowaS4Yes
District of ColumbiaSHYes
North DakotaS2Yes
ConnecticutSNRYes
MichiganSNRYes
DelawareS2Yes
New HampshireSNRYes
VermontS5Yes
West VirginiaS1Yes
Rhode IslandS2Yes
Threat Assessments
ThreatScopeSeverityTiming
8 - Invasive & other problematic species, genes & diseasesPervasive (71-100%)Extreme or 71-100% pop. declineHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesPervasive (71-100%)Extreme or 71-100% pop. declineHigh (continuing)
8.1.2 - Named speciesPervasive (71-100%)Extreme or 71-100% pop. declineHigh (continuing)

Plant Characteristics
Economic Value (Genus)No
Roadless Areas (9)
Michigan (1)
AreaForestAcres
DeliriumHiawatha National Forest190
Minnesota (1)
AreaForestAcres
Brule Lake - Eagle MountainSuperior National Forest12,380
Pennsylvania (1)
AreaForestAcres
Minister ValleyAllegheny National Forest1,417
Vermont (2)
AreaForestAcres
Bread LoafGreen Mountain and Finger Lakes National Forests1,768
Griffith Lake 09084Green Mountain and Finger Lakes National Forests1,833
West Virginia (3)
AreaForestAcres
Canaan LoopMonongahela National Forest7,867
Cranberry AdditionMonongahela National Forest11,123
Cranberry Glades Botanical AreaMonongahela National Forest785
Wisconsin (1)
AreaForestAcres
09159 - ThornappleChequamegon-Nicolet National Forest9,744
References (11)
  1. Emerald Ash Borer Information Network. 2020. Available. Online: www.emeraldashborer.info/index.php (accessed 9 Apr 2020).
  2. Haack, R., E. Jendek, H. Liu, K. Marchant, T. Petrice, T. Poland, and H. Ye. 2002. The emerald ash borer: a new exotic pest in North America. Newsletter of the Michigan Etymological Society 47(3-4):1-5.
  3. Kartesz, 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.
  4. Klooster, W., D. Herms, K. Knight, C. Herms, D. McCullough, A. Smith, K. Gandhi, and J. Cardina. 2014. Ash (<i>Fraxinus</i> spp.) mortality, regeneration, and seed bank dynamics in mixed hardwood forests following invasion by emerald ash borer (<i>Agrilus planipennis</i>). Biological Invasions 16: 859-873.
  5. Knight, K., J. Brown, and R. Long. 2013. Factors affecting the survival of ash (<i>Fraxinus</i> spp.) trees infested by emerald ash borer (<i>Agrilus planipennis</i>). <i>Biological Invasions</i> 15: 371-383.
  6. Little, E.L., Jr. 1979. Checklist of United States trees (native and naturalized). Agriculture Handbook No. 541. U.S. Forest Service, Washington, D.C. 375 pp.
  7. McCullough, D.G., N.F. Schneeberger, and S.A. Katovich. 2008. Emerald ash borer pest alert. NA-PR-02-04. USDA Forest Service.
  8. <p>Aubin, I., F. Cardou, K. Ryall, D. Kreutzweiser, and T. Scarr. 2015. Ash regeneration capacity after emerald ash borer (EAB) outbreaks: Some early results. <i>The Forestry Chronicle</i> 91(3): 291-298.</p>
  9. Poland, T. M., and D. G. McCullough. 2006. Emerald Ash Borer: Invasion of the urban forest and and the threat to North America's ash resource. Journal of Forestry 104(3):118-124.
  10. Robinett, M.A., and D.G. McCullough. 2019. White ash (<i>Fraxinus americana</i>) survival in the core of the emerald ash borer (<i>Agrilus planipennis</i>) invasion. Canadian Journal of Forest Research 49:510-520.
  11. Steiner, K.C., L.E. Graboski, K.S. Knight, J.L. Koch, M.E. Mason. 2019. Genetic, spatial, and temporal aspects of decline and mortality in a Fraxinus provenance test following invasion by the emerald ash borer. Biological Invasions 21:3439–3450.