Amblema plicata

(Say, 1817)

Threeridge

G5Secure Found in 1 roadless area NatureServe Explorer →
G5SecureGlobal Rank
Least concernIUCN
LowThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.118891
Element CodeIMBIV03020
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryInvertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumMollusca
ClassBivalvia
OrderUnionoida
FamilyUnionidae
GenusAmblema
Synonyms
Amblema costata(Rafinesque, 1820)
Other Common Names
Amblème à trois côtes (FR)
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
Analysis of genetic structure (Elderkin et al., 2007) showed low structure among rivers and rainages separated by very large geographical distances, indicating high effedtive population size and/or highly vagile fish hosts. Northern populations were likely founded from at least two glacial refugia following the Pleistocene.
Conservation Status
Review Date2014-01-08
Change Date1996-11-25
Edition Date2014-01-08
Edition AuthorsJackson, D. R. (2013); Cordeiro, J. (2009)
Threat ImpactLow
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences> 300
Rank Reasons
This species is considered common and widespread throughout much of the U.S. and Canada and is considered stable, or in some cases expanding, throughout its range.
Range Extent Comments
This species ranges from the coastal plain portion of Gulf drainages from the Escambia River in Florida west to Texas and northward into the Mississippi River drainage (Mulvey et al,. 1997). Butler (1989) lists the distribution as throughout the Interior Basin and from the San Antonio River, Texas, east to the Choctawhatchee River, but not from the Yellow River. In Canada, it is restricted to southern Ontario, southern Manitoba, and southeastern Saskatchewan, but is widely distributed and often abundant In Canada, this species is restricted to the Lake Erie drainage in Ontario (Metcalfe-Smith and Cadmore-Vokey, 2004). It extends into the Niagara River drainage in western New York (Strayer and Jirka, 1997).
Occurrences Comments
It is in the Cache and White (Christian, 1995; Christian et al., 2005; Gordon, 1982; Gordon et al., 1994), lower Arkansas (Gordon, 1985), St. Francis (Ahlstedt and Jenkinson, 1991), Ouachita (Posey, 1997; Posey et al., 1996), and Poteau (Vaughn and Spooner, 2004) drainages, Arkansas. In South Dakota, it is in the upper and middle Big Sioux and tributaries (Skadsen and Perkins, 2000), James and Vermillion Rivers (Backlund, 2000; Perkins and Backlund, 2003). It is throughout E and SE Texas and San Antonio and Guadalupe systems N and E; Nueces River (Howells et al., 1996); Village Creek (Hardin/Tyler/Polk Cos.) (Bordelon and Harrel, 2004). In Kansas, it is widespread in the E third and relictual N and W (Couch, 1997); also Wakarusa (Tiemann, 2006). It is in the Spring River drainage, Kansas and Oklahoma (Branson, 1966). Oklahoma: Verdigris (Boeckman and Bidwell, 2008), Neosho, Boggy, Clear Boggy, Blue, Kiamichi, Little (Vaughn and Taylor, 1999), Chikaskia, Canadian, Poteau, and Mountain Fork (Spooner and Vaughn, 2007) systems (Branson, 1982; Vaughn, 2000). It is widespread and common in Illinois and most of Wisconsin (Cummings and Mayer, 1992; 1997; Mathiak, 1979; Schanzle et al., 2004; Tiemann et al., 2005). In Indiana: Blue (Sietman et al., 1995), Tippecanoe (Cummings and Berlocher, 1990), E Fork White (Harmon, 1992), Muscatatuck (Harmon, 1989), St. Joseph (Pryor, 2005). In Minnesota, it is in the W and S but absent from Lake Superior, Rainy River, and most of Mississippi drainage above St. Anthony Falls (Sietman, 2003); including Red River (Cvancara, 1970). It was widespread and common in Ohio (Watters, 1992; 1995; Lyons et al., 2007; Grabarkiewicz, 2008; Hoggarth et al., 2007); but range has decreased in the past decade (Watters et al., 2009). In Tennessee, it is in most drainages (Parmalee and Bogan, 1998). It is statewide in Kentucky (Cicerello and Schuster, 2003; Evans, 2008); Red (Clark, 1988), Middle Green (Gordon, 1991) and Barren Rivers (Cochran and Layzer, 1993). In West Virginia, it is in the Middle and lower Ohio (Zeto et al., 1987), Mud Rivers (Guyandotte drainage) (Schmidt and Zeto, 1986), Kanawha (Morris and Taylor, 1992); and Copper Creek in Virginia (relict) (Fraley and Ahlstedt, 2000). It is common and widespread throughout Louisiana (Vidrine, 1993). In Mississippi, it is in the Mississippi River N and S, Big Black, Yazoo, Tennessee, Pearl, Pascagoula, and Tombigbee drainages (Jones et al., 2005). It is reported from the Escambia and Yellow (Picket Wretch Lake) drainages in Florida and Alabama (also Choctawhatchee River, Walton Co.) (Butler, 1989) but now extirpated (Blalock-Herod et al., 2005). In the Alabama and Mobile basin, it is in the Tennessee and Mobile basins except upper Tallapoosa and possibly Coosa drainage (Williams et al., 2008). It is historic from the Black Warrior River, but was in the upper Tombigbee in Sumter and Greene Cos., Alabama (Williams et al., 1992; McGregor et al., 1999); also Bear Creek drainage, AL/MS (McGregor and Garner, 2004). In the Big Blue system (NE Nebraska and Kansas) it was only in the Kansas portion (6 sites), and 1 subfossil N of the border (Hoke, 2005). In the Little Blue basin weathered shells are in the Kansas portion (Hoke, 2004). I is in Tonawanda Creek (Niagara drainage), western New York (Marangelo and Strayer, 2000) and in Muddy Creek (French Creek drainage), Crawford Co., Pennsylvania (Mohler et al., 2006). It occurs in the St. Clair/Detroit drainage in Michigan (Strayer, 1980; Trdan and Hoeh, 1993) and S upper peninsula (Goodrich and Van der Schalie, 1939; Badra and Goforth, 2003). In Canada, it is widespread from southern Manitoba (incl. Assiniboine- Watson, 2000), northern (Churchill River, Stony Rapids east of Lake Athabasca) and southeastern Saskatchewan (Frenchman, Assiniboine, Qu'Appelle, North and South Saskatchewan, Carrot Rivers; Moose Jaw, Swift Current Creeks); and the Lake Erie drainage in Ontario (Metcalfe-Smith and Cadmore-Vokey, 2004).
Ecology & Habitat

Habitat

This species can be found in a variety of habitats, ranging from small streams to big rivers, and from locations such as lakes, rivers, and streams with little or no current to areas of very swift current. It is found in a variety of substrates including clay, mud, sand, sand mixed with gravel, and gravel. It is most common on bottoms composed of sand and gravel in one to three feet of water, but has been taken at depths of 30 feet (Parmalee and Bogan, 1998).

Reproduction

Infestation by glochidia confirmed (though transformation not tested) on Hiodon tergisus, Notropis antherinoides, Cyprinella spiloptera, Cyprinella whipplei, Erimystax dissimilis, Moxostoma duquesnei, Moxostoma erythrurum, Hyperntelium nigricans, Ictalurus punctatus (confirmed host), Lepomis macrochirus (confirmed host), Percina caprodes, Aplodinotus grunniens (Weiss and Layzer, 1995).
Other Nations (2)
United StatesN5
ProvinceRankNative
MississippiS5Yes
FloridaS1Yes
West VirginiaS3Yes
New YorkS1Yes
MissouriS5Yes
North DakotaSNRYes
TexasS4Yes
LouisianaS5Yes
AlabamaS5Yes
TennesseeS5Yes
South DakotaS3Yes
PennsylvaniaS2Yes
KentuckyS4Yes
MinnesotaSNRYes
IowaSNRYes
WisconsinS4Yes
IndianaS4Yes
MichiganSNRYes
OhioS5Yes
OklahomaS3Yes
ArkansasS5Yes
KansasS4Yes
NebraskaS1Yes
IllinoisS5Yes
VirginiaS5Yes
CanadaN4
ProvinceRankNative
SaskatchewanSUYes
OntarioS4Yes
ManitobaS3Yes
Roadless Areas (1)
Texas (1)
AreaForestAcres
Winters BayouNational Forests in Texas730
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