Oenothera argillicola

Mackenzie

Shale Barren Evening-primrose

G3Vulnerable (G3G4) Found in 6 roadless areas NatureServe Explorer →
G3VulnerableGlobal Rank
Identity
Unique IDELEMENT_GLOBAL.2.160404
Element CodePDONA0C020
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single nation
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderMyrtales
FamilyOnagraceae
GenusOenothera
Other Common Names
shale barren evening-primrose (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
Review Date2000-06-22
Change Date2000-06-22
Edition Date1994-11-03
Edition AuthorsOstlie, W.R. (WRO, 1991), rev. L. Morse (1994)
Range Extent250-20,000 square km (about 100-8000 square miles)
Number of Occurrences81 to >300
Rank Reasons
Relatively common within its limited range, especially in Virginia. Endemic to the Appalachian shale barrens of Virginia, West Virginia, Maryland and southern Pennsylvania; approximately thirty counties total.
Range Extent Comments
Endemic to the Appalachian shale barrens of Virginia, West Virginia, Maryland and southern Pennsylvania; approximately thirty counties total.
Occurrences Comments
Unknown; approximately forty in Maryland; 100+ sites in Virginia.
Threat Impact Comments
A significant threat to the insect pollinators of O. argillicola is presented by the spraying of Dimilin and BT insecticides for the introduced Spongy Moth (Lymantria dispar) control. Because of the open habitat, shale barren insects are maximally exposed to pesticides (Dix 1990). Dimilin is a broad-spectrum biocide that persists until leaf fall and up to a few years in the duff and would have a long-term impact of shale-barren slopes. All insect occurrences on shale-barrens sprayed with Dimilin should be considered extirpated (Schweitzer in litt). BT is lepidopteran-specific and only persists for roughly one week (Dix 1990). Application during larval development may have devastating impacts on the fauna, however.

Five shale barrens in West Virginia and three in Virginia have been partially destroyed by road construction. Two additional barrens in Virginia were partially destroyed by railroad construction and one was crossed by a hiking trail (USFWS 1989). One barren has been destroyed through inundation caused by the damming of a stream (Dix 1990). Similar concerns have been expressed for barrens along the South Fork Valley of West Virginia where flood control measures are planned (Bartgis in litt.).

Moderately xeric sites may be subject to encroachment of exotic plant species such as Centauria maculata and a host of grass species (Dix 1990). Such encroachment may negatively impact the vigor of O. argillicola individuals. Threatened by succession due to suppression of fire (Southern Appalachian Species Viability Project 2002).
Ecology & Habitat

Diagnostic Characteristics

Flowers yellow, buds erect, petals 2-4 cm, anthers 8-12 mm, ovary terete or nearly so; fruit terete, obscurely and roundly 4 angled or sulcate; stamens equal; seeds horizontal, very angular; sepal appendages separate from the base, subterminal.

Habitat



Oenothera argillicola is an endemic of the Appalachian shale barrens, occurring in the states of Virginia, West Virginia, Maryland and southern Pennsylvania (Stinson 1953).

The term "shale barren" is a general reference to certain mid-Appalachian slopes that possess the following features: 1) southern exposures, 2) slopes of 20-70 degrees and 3) a covering of lithologically hard and weather-resistant shale or siltstone fragments (Dix 1990). These barrens support a sparse, scrubby growth of Quercus ilicifolia, Q. prinus, Q. rubra, Pinus virginiana, Juniperus virginiana, Prunus alleghaniensis,, Rhus aromatica, Celtis tenuifolia, Kalmia latifolia, Bouteloua curtipendula, Andropogon scoparius, Phlox subulata var. brittonii, Silene caroliniana ssp. pensylvanica, Sedum telephoides, Antennaria spp., Aster spp., and species of Solidago (Dix 1990). Considerable variations in associated flora may occur locally.

Although adequate moisture is available for most plants within the substrata of the shale layers, adverse surface conditions act to restrict germination and establishment success of plants (Platt 1951). It is primarily the effect of high surface temperatures that limits reproductive success in these habitats. Surface soil temperatures are often well above the physiological tolerance of most plant species, reaching maximum temperatures of 63 degrees Celsius (Dix 1990). Such temperatures are high enough to cause direct damage to seedlings. For additional detailed information pertaining to the shale-barren community, see Dix (1990).

Artz (1948) stated that O. argillicola is able to exist in habitats other than shale barrens, but always requires areas with little or no competition. This inability to withstand competition may be one of the chief reasons why O. argillicola is largely restricted to shale barrens (Artz 1948). Typically, shale barren endemics are apparently obligates of high light intensity, a soil adequate for extensive root development, and a low level of competition (Platt 1951). The sparsity of plant life in the shale barrens has been explained as the result of a restriction in seedling establishment imposed by low soil moisture and high soil temperatures (Stinson 1953). Oenothera argillicola is apparently able to withstand and thrive in such conditions.

Ecology



Oenothera argillicola flowers in late summer, typically July through October (Gleason and Cronquist 1963).

Oenothera argillicola is unusual among eastern euoenotherids in its tendency to display only minor cytogenic aberrations typical of the subgenus, as well as its restriction to a specific habitat (Stinson 1954).

According to Stinson (1954), O. argillicola consists of: "ecologically restricted, essentially lethal-free, open-pollinated individuals with all-pairing chromosomes or small circles and several pairs. In natural populations, open-pollination should lead to considerable crossing among individuals occupying the same area. At the same time, as a result of the absence of lethals, one would expect that whenever self-pollination in the circle-bearing forms did take place segregation for chromosomes configuration would occur."

Stinson (1954) further stated that based on segmental end arrangements of chromosomes, O. argillicola is most closely related to O. hookeri of the southwestern United States. The two taxa share a number of similar features, including the presence of mostly-paired chromosomes, alethal complexes, open-pollination and ancestral end arrangements.

Morphologically, however, O. argillicola most closely resembles O. parviflora. Both show similar narrow, thick glabrous leaves, subterminal sepal tips and bent stem tips (Stinson 1954). In addition, O. parviflora is able to occupy the same shale barren habitat as O. argillicola. Based on primitive characters present in O. argillicola, Stinson (1954) surmised that it is a relict of a once widely-distributed taxon that invaded the East from its ancestral home in the Southwest. This belief was also shared by Keener (1970).

It has been suggested that O. argillicola likely played a role in the origin of O. parviflora, through crossing with ancient O. strigosa or O. biennis populations in the East (Stinson 1954).

Reproduction

Easily cultivated and self seeding, this species shows exceptional growth in sandy or heavy soils. Germination percentage high.
Terrestrial Habitats
Bare rock/talus/scree
Other Nations (1)
United StatesN3
ProvinceRankNative
PennsylvaniaS2Yes
VirginiaS3Yes
MarylandS3Yes
West VirginiaS3Yes
Plant Characteristics
DurationBIENNIAL, PERENNIAL, Short-lived
Economic Value (Genus)No
Roadless Areas (6)
Virginia (5)
AreaForestAcres
Crawford MountainGeorge Washington National Forest9,892
Elliott KnobGeorge Washington National Forest9,380
JerkemtightGeorge Washington National Forest16,687
Oliver MountainGeorge Washington National Forest13,090
Price MountainJefferson National Forest9,119
West Virginia (1)
AreaForestAcres
North Mountain HopevilleMonongahela National Forest6,525
References (19)
  1. Artz, L. 1948. Plants of the shale-barrens of the tributaries of the James River in Virginia. Castanea 13:141-145.
  2. Britton, N. L. and A. Brown. 1913. An Illustrated Flora of the Northern United States and Canada. 3 vol. Dover Publications, Inc., N. Y. 2052 pp.
  3. Core, E.L. 1946. Wild Flowers of the Appalachain Shale Barrens. Wild Flowers 22:13-18.
  4. Core, E. L. 1952. The ranges of some plants of the Appalachian shale barrens. Castanea 17:105-116.
  5. Fernald, M.L. 1950 Gray's Manual of Botany, 8th ed. American Book Company, New York. 1632 pp.
  6. Gleason, H.A., and A. Cronquist. 1963. Manual of vascular plants of northeastern United States and adjacent Canada. D. Van Nostrand Company, New York, NY. 810 pp.
  7. Gleason, H.A., and A. Cronquist. 1991. Manual of vascular plants of northeastern United States and adjacent Canada. New York Botanical Garden, Bronx, New York. 910 pp.
  8. Henry, L. K. 1954. Shale-barren flora in Pennsylvania. Proc. Penn. Acad. Sci. 28: 65-68.
  9. 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.
  10. Keener, C.S. 1970. The natural history of the mid-Appalachian shale barren flora. Pages 215-248 in: P.C. Holt, ed. The Distributional History of the Biota of the Southern Appalachians. II. Flora. Virginia Polytechnic Institute, Blacksburg, VA.
  11. Mackenzie, K.K. 1904. Notes on Evening Primroses. Torreya 4 (4): 56-57.
  12. Platt, R.B. 1951. An ecological study of the mid-Appalachian shale barrens and the plants endemic to them. Ecol. Monogr. 21:269-300.
  13. Small, J.K. 1932. <i>Oenothera argillicola</i>. Addisonia 17 (4): 55-56.
  14. Southern Appalachian Species Viability Project. 2002. A partnership between the U.S. Forest Service-Region 8, Natural Heritage Programs in the Southeast, NatureServe, and independent scientists to develop and review data on 1300+ regionally and locally rare species in the Southern Appalachian and Alabama region. Database (Access 97) provided to the U.S. Forest Service by NatureServe, Durham, North Carolina.
  15. Stinson, H. T. 1953. Cytogenetics and phylogeny of Oenothera argillicola Mackenz. Genetics 38: 389-406.
  16. Strausbaugh, P.D. and E.L. Core. 1964. Flora of West Virginia, Series 65, No 3-2. West Virginia University Bulletin.
  17. Weishaupt, C.G. 1971. Vascular Plants of Ohio, Third edition. Kendall/Hunt Publishing Co., Dubuque, Iowa.
  18. Wherry, E. T. 1930. Plants of the Appalachian shale-barrens. J. Washington Acad. Sci. 20(3): 43-52.
  19. Wherry, E. T. 1933. Four shale barren plants in Pennsylvania. Pennsylvania Academy of Science Proceedings 7:160-164.