Epioblasma capsaeformis

(I. Lea, 1834)

Oyster Mussel

G1Critically Imperiled Found in 1 roadless area NatureServe Explorer →
G1Critically ImperiledGlobal Rank
EndangeredIUCN
Very highThreat Impact
Oyster mussel (Epioblasma capsaeformis). Photo by U.S. Fish & Wildlife Service, Public Domain (U.S. Government Work), via ECOS.
U.S. Fish & Wildlife Service, https://www.usa.gov/government-works
Identity
Unique IDELEMENT_GLOBAL.2.118984
Element CodeIMBIV16040
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryInvertebrate Animal
IUCNEndangered
Endemicendemic to a single nation
KingdomAnimalia
PhylumMollusca
ClassBivalvia
OrderUnionoida
FamilyUnionidae
GenusEpioblasma
Synonyms
Dysnomia capsaeformis(I. Lea, 1834)Plagiola capsaeformis(I. Lea, 1834)
Concept Reference
Turgeon, D. D., J. F. Quinn, Jr., A. E. Bogan, E. V. Coan, F. G. Hochberg, W. G. Lyons, P. M. Mikkelsen, R. J. Neves, C. F. E. Roper, G. Rosenberg, B. Roth, A. Scheltema, F. G. Thompson, M. Vecchione, and J. D. Williams. 1998. Common and scientific names of aquatic invertebrates from the United States and Canada: Mollusks. 2nd Edition. American Fisheries Society Special Publication 26, Bethesda, Maryland. 526 pp.
Taxonomic Comments
There is a problem related to misidentification and priority concerning Epioblasma and Plagiola. Epioblasma is used in anticipation of a decision in its favor by the ICZN. It has been suggested that this species may be a senior synonym of Epioblasma florentina walkeri (see Buhay et al., 2002), but molecular, morphological, and life history data from Jones (2004) and Jones et al. (2006) suggest they are distinct. Based on molecular, morphological, and life history data, the population from the Duck River, Tennessee, is tentatively proposed as a separate species from Epioblasma capsaeformis populations in the Clinch River because of distinctiveness of molecular genetic markers, differences in mantle pad coloration and texture, greater height of marsupial expansion of the female shell, smaller glochidial size, differing host fish specificity, and behavioral differences in movement of micro-lures (Jones, 2004; Jones et al., 2006).
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2023-12-05
Change Date2003-10-28
Edition Date2023-12-05
Edition AuthorsCordeiro, J. (2011); rev. T. Cornelisse (2023)
Threat ImpactVery high
Range Extent5000-200,000 square km (about 2000-80,000 square miles)
Number of Occurrences1 - 20
Rank Reasons
This species has a moderate range but due to long and short-term population declines and many ongoing threats, it has few viable occurrences.
Range Extent Comments
This species occurs in the Clinch and Nolichucky Rivers, with remnant or reestablished populations in the Cumberland River and upper Tennessee River systems, in Tennessee, Kentucky, and Virginia, USA (USFWS 2019).
Occurrences Comments
This species is known from two stream reaches in 5-6 populations, including those from reintroduction efforts (USFWS 2019).
Threat Impact Comments
This species is threatened by oil and gas exploration, coal mining, and the heavy metal and chemical pollutants that result from those activities, agriculture and urbanization, as well as sedimentation and pollutants due to runoff from development and agriculture, dams or other barriers that alter its habitat, host fish distribution, and prevent habitat connectivity and recolonization, and drought conditions that reduce habitat, elevate water temperature, and reduce dilution of pollutants and sediment runoff (USFWS 2004; 2019).
Ecology & Habitat

Description

Shell medium-sized, elliptical (male) to irregularly obovate (female), slightly inflated, subsolid to quite thin posteriorly (female); anterior regularly rounded; ventral margin slightly curved (male) to almost straight (female); posterior margin obliquely sloped from an obtusely angular posterio-dorsal junction to a blunt or biangulate point at the posterio-ventral junction; posterio-ventral are of female broadly expanded to accomodate the branchial marsupia, slightly inflated, demarcated by sulci, margin may be dentate, expansion may appear bilobed in old individuals; dorsal margin rather straight; beaks broad, elevated above hinge line, sculpted by feeble undulations; posterior ridge angular and more-or-less double (male) to slight or imperceptible (female), a slight sulcus occurs anteriorly in male; periostracum dull to subshiny, yellowish to green with numerous dark green rays across surface, marsupial expansion usually dark green to blackish. Pseudocardinals rather heavy, triangular, double in left valve, single in right; interdentum slight, rather short; lateral teeth slightly curved, rather short, double in left, single in right; beak cavity shallow; anterior muscle scars well-impressed, posterior muscle scars shallow; pallial line impressed anteriorly; nacre whitish to bluish-white.

Diagnostic Characteristics

The pronounced development of the posterio-ventral region in females distinguishes EPIOBLASMA from similarly shaped species. Epioblasma capsaeformis is recognizable by the typically dark coloration and fragility of the marsupial expansion and the lack of development of the posterior ridge (e.g., not angular, no knobs). Males in comparison to similar Epioblasma tend to be more elliptical, have a moderately developed posterior ridge and accompanying sulcus, and have a regularly curved ventral margin. The ventral margin in species such as Epioblasma florentina (Lea 1857) and Epioblasma turqidula (Lea 1858) often exhibit an emargination of the ventrum just anterior to the terminus of the posterior ridge. Yellowish specimens of E. capsaeformis have been mistaken for Epioblasma walkeri (Wilson and Clark 1914) (including records in Johnson [1978: as E. florentina]). Males of E. walkeri tend to be broader and have a rounded posterior ridge; females lack the distinctive darkening of the marsupial expansion.

Habitat

This species is found in small to medium-sized rivers, and occasionally in large rivers, in areas with coarse sand to boulder substrates and moderate to swift currents (USFWS 2003, 2004).

Reproduction

This species appears to be a long-term brooder as glochidia have been found in the marsupia during winter months (Gordon and Layzer 1989).
Other Nations (1)
United StatesN1
ProvinceRankNative
VirginiaS1Yes
TennesseeS1Yes
AlabamaSXYes
KentuckyS1Yes
GeorgiaSXYes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentRestricted (11-30%)Moderate or 11-30% pop. declineHigh (continuing)
2 - Agriculture & aquacultureRestricted (11-30%)Serious - moderateHigh (continuing)
2.3 - Livestock farming & ranchingRestricted (11-30%)Serious - moderateHigh (continuing)
2.3.4 - Scale unknown/unrecordedRestricted (11-30%)Serious - moderateHigh (continuing)
7 - Natural system modificationsLarge (31-70%)Serious or 31-70% pop. declineHigh (continuing)
7.2 - Dams & water management/useLarge (31-70%)Serious or 31-70% pop. declineHigh (continuing)
9 - PollutionPervasive - largeExtreme - seriousHigh (continuing)
9.1 - Domestic & urban waste waterLarge (31-70%)Serious or 31-70% pop. declineHigh (continuing)
9.1.2 - Run-offLarge (31-70%)Serious or 31-70% pop. declineHigh (continuing)
9.2 - Industrial & military effluentsLarge (31-70%)Serious or 31-70% pop. declineHigh (continuing)
9.3 - Agricultural & forestry effluentsRestricted (11-30%)Serious or 31-70% pop. declineHigh (continuing)
11 - Climate change & severe weatherRestricted (11-30%)Serious - moderateHigh (continuing)
11.2 - DroughtsRestricted (11-30%)Serious - moderateHigh (continuing)

Roadless Areas (1)
Idaho (1)
AreaForestAcres
Bear CreekCaribou-Targhee National Forest118,582
References (58)
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