Fraxinus latifolia

Benth.

Oregon Ash

G5Secure Found in 39 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
Near threatenedIUCN
HighThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.134625
Element CodePDOLE040A0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
IUCNNear threatened
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderScrophulariales
FamilyOleaceae
GenusFraxinus
Other Common Names
Frêne d'Orégon (FR) Oregon ash (EN)
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 MethodLegacy Rank calculation - Biotics v1
Review Date1990-01-16
Change Date1990-01-16
Edition Date2020-04-17
Edition AuthorsTreher (2020)
Threat ImpactHigh
Range Extent200,000-2,500,000 square km (about 80,000-1,000,000 square miles)
Number of Occurrences> 300
Rank Reasons
Fraxinus latifolia occurs from California north to British Columbia. While the species may be secure presently, it is highly threatened by the arrival of the Emerald Ash Borer, which is steadily making its way across North America. This nonnative pest has caused serious declines in the eastern ashes
Range Extent Comments
Fraxinus latifolia occurs from California north to British Columbia.
Threat Impact Comments
A serious potential 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 eastern ash populations. it is spreading across North America making it as far as Colorado, and while not yet on the west coast, there is a strong possibility it will make it there (Emerald Ash Borer Information Network 2020). 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 eastern ash species (Knight et al. 2013, Klooster et al. 2014, McCullough et al. 2008, Steiner et al. 2019). While an infested tree are observed to push out root sprouts for one to two years, it 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.
Ecology & Habitat
Other Nations (2)
CanadaNU
ProvinceRankNative
British ColumbiaSUYes
United StatesN4
ProvinceRankNative
OregonSNRYes
WashingtonSNRYes
CaliforniaSNRYes
Threat Assessments
ThreatScopeSeverityTiming
8 - Invasive & other problematic species, genes & diseasesLarge (31-70%)Extreme - seriousHigh - low
8.1 - Invasive non-native/alien species/diseasesLarge (31-70%)Extreme - seriousHigh - low
8.1.2 - Named speciesLarge (31-70%)Extreme - seriousHigh - low

Plant Characteristics
Economic Value (Genus)No
Roadless Areas (39)
California (30)
AreaForestAcres
Bell QuinbyShasta-Trinity National Forest11,556
Black Mtn.Sequoia National Forest15,102
Castle Crags AShasta-Trinity National Forest113
Castle Crags BShasta-Trinity National Forest1,619
Cow CreekShasta-Trinity National Forest22,627
Dennison PeakSequoia National Forest6,293
Devil GulchSierra National Forest30,490
Elk CreekMendocino National Forest23,182
Ferguson RidgeSierra National Forest6,104
KangarooKlamath National Forest40,617
KellySix Rivers National Forest5,195
Kettle Mtn.Shasta-Trinity National Forest4,589
Lake EleanorShasta-Trinity National Forest397
Little French CShasta-Trinity National Forest11,529
Monkey CreekSix Rivers National Forest9,017
MosesSequoia National Forest22,077
North Fork SmithSix Rivers National Forest37,898
Orleans Mtn. CSix Rivers National Forest15,589
PantherShasta-Trinity National Forest12,016
Red MountainAngeles National Forest8,034
RinconSequoia National Forest54,610
San Gabriel AddAngeles National Forest2,527
Siskiyou BSix Rivers National Forest18,871
Skeleton GladeMendocino National Forest9,237
Snow MountainMendocino National Forest14,457
South ForkShasta-Trinity National Forest16,786
Timbered CraterLassen National Forest4,096
UnderwoodSix Rivers National Forest6,591
West GirardShasta-Trinity National Forest37,516
WestforkAngeles National Forest4,407
Oregon (9)
AreaForestAcres
Cougar BluffUmpqua National Forest5,574
EagleMt. Hood National Forest16,841
French Pete (a)Willamette National Forest1,668
LarchMt. Hood National Forest12,961
Limpy RockUmpqua National Forest6,782
Mclennon MountainWillamette National Forest8,085
North KalmiopsisSiskiyou National Forests91,560
Shasta CostaSiskiyou National Forests14,420
South KalmiopsisSiskiyou National Forests104,477
References (5)
  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. 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.
  5. Munz, P.A., with D.D. Keck. 1959. A California flora. Univ. California Press, Berkeley. 1681 pp.