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Behavior

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Mussels in general are responsive to tactile and chemical stimulation. Many sensory organs are on the middle lobe of the mantle edge. In the foot, mussels have paired statocysts, fluid filled chambers with a solid granule or pellet. The mussels use the statocysts to orient themselves.

Unionids in general may have some form of chemical reception to recognize fish hosts.

Glochidia respond to both touch, light and some chemical cues. In general, when touched or a fluid is introduced, they will respond by clamping shut.

Communication Channels: chemical

Perception Channels: tactile ; vibrations ; chemical

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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Renee Mulcrone, Special Projects
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Conservation Status

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The dwarf wedgemussel, Alasmidonta heterodon, was list as federally endangered on March 14, 1990. The dwarf wedgemussel was added to the federally endangered list primarily because of human impacts on its habitat and water quality. Some factors include: agriculture, construction, pollution, silt deposits, low oxygen levels, water level fluctuation, temperature fluctuations, flooding, erosion, and siltation.

US Federal List: endangered

CITES: no special status

State of Michigan List: no special status

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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Renee Mulcrone, Special Projects
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Life Cycle

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Dwarf wedgemussel females carry eggs in their gills and receive sperm (released from males) through the gills. After eggs have been fertilized, they develop into parasitic bivalved larvae called glochidia. The time needed to develop from fertilized eggs to glochia is unknown. The newly formed glochidia are released from the female and into the water where they need to attach to a host fish to survive. The glochidia develop into juveniles while attached to a host. After metamorphosis, a juvenile mussel will be sloughed from its host, where it further develops on the stream/river bottom.

The parasitic larvae have been found to metamorphose on the following host species: mottled sculpin, tessellated darter, and johnny darter.

Development - Life Cycle: metamorphosis

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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Renee Mulcrone, Special Projects
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Benefits

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There are currently no known adverse effects of the dwarf wedgemussel on humans.

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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Renee Mulcrone, Special Projects
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Benefits

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Freshwater mussels in general are important water quality indicator for streams and rivers.

Positive Impacts: research and education

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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Renee Mulcrone, Special Projects
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Associations

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Freshwater mussels in general occupy many tropic guilds by feeding on detritous. The mussels may also aid in the biodegradation of plant matter.

Ecosystem Impact: parasite

Species Used as Host:

  • mottled sculpin, Cottus bairdii
  • tessellated darter, Etheostoma olmstedi
  • johnny darter, Etheostoma nigrum
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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Renee Mulcrone, Special Projects
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Trophic Strategy

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The glochidia of the species are parasitic on its fish host. Once an adult, the dwarf wedgemussel is a filter feeder, feeding on phytoplankton and detritous.

Plant Foods: phytoplankton

Other Foods: detritus

Foraging Behavior: filter-feeding

Primary Diet: planktivore ; detritivore

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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Renee Mulcrone, Special Projects
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Distribution

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The dwarf wedgemussel, Alasmidonta heterodon, has a discontinuous range on the Atlantic coast of the United States. Twenty-four populations of dwarf wedgemussels are found within 12 states from Maine to North Carolina. This species may have occurred in Canada but is likely extirpated.

Biogeographic Regions: nearctic (Native )

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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Renee Mulcrone, Special Projects
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Habitat

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Dwarf wedgemussels are usually found in waters with slow to moderate current that have muddy sand to sand and gravel substrate.

Habitat Regions: freshwater

Aquatic Biomes: rivers and streams

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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Renee Mulcrone, Special Projects
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Life Expectancy

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The average lifespan of a dwarf wedgemussel is approximately 15 years.

Average lifespan
Status: wild:
15 years.

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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Morphology

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This freshwater mussel has a trapezoidal shell usually less than 45 mm long and 25 mm high. The anterior end of the shell is thick and the posterior end is usually thinner. The periostracum, or the outer layer of the shell, is a brown color. In juveniles reddish brown colored rays of differing widths are visible. The most distinguishing characteristic of this species is the hinge teeth, with the right valve having two and the left having only one. These mussels are slightly sexually dimorphic, with the female shell swollen posteriorly and more trapezoidal than the male, and the male shell being more compressed, ovate and elongated.

Average length: 45 mm.

Other Physical Features: ectothermic ; heterothermic ; bilateral symmetry

Sexual Dimorphism: sexes shaped differently

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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Renee Mulcrone, Special Projects
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Associations

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Young dwarf wedgemussels are often consumed by birds, such as ducks and herons. Young mussels are also eaten by fish. Mature dwarf wedgemussels can be consumed by some mammals, such as raccoons and muskrats.

Known Predators:

  • Ducks
  • Herons
  • Fish
  • Racoons, Procyon lotor
  • Muskrats, Ondatra zibethicus
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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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pat dziamba, Rutgers University
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David V. Howe, Rutgers University
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Reproduction

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This species is a long term brooder that spawns in late summer. The male releases sperm out into the water, which float down stream and enter the females gills for fertilization. Females can receive sperm from multiple males. The resulting glochidia are then released by the female into the water.

Mating System: polygynandrous (promiscuous)

The dwarf wedgemussel is a long term brooder that spawns in late summer and then becomes gravid in the fall and releases the glochidia anywhere from late March to early June. Starting around August, the males release their sperm into the water which is then carried towards the females. The females take the sperm in through their gills and they fertilize the eggs. Once fertilized, the eggs are held in the marsupia of the female which becomes swollen and dark when occupied. The eggs are held in the marsupia and recieve parental care through the winter until they are ready to be released as glochida anywhere from March to June.

Breeding interval: The dwarf wedgemussel spawns once a year.

Breeding season: Males release sperm into the water around August.

Average gestation period: 8.5 months.

Key Reproductive Features: iteroparous ; seasonal breeding ; gonochoric/gonochoristic/dioecious (sexes separate); sexual ; fertilization (Internal )

Females brood fertilized eggs in the marsupia from seven to 10 months. The larvae (glochidia) are released in the spring.

Parental Investment: pre-fertilization (Provisioning); pre-hatching/birth (Provisioning: Female, Protecting: Female)

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Bowne, j. and p. dziamba 2012. "Alasmidonta heterodon" (On-line), Animal Diversity Web. Accessed April 27, 2013 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Alasmidonta_heterodon.html
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jill Bowne, Rutgers University
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David V. Howe, Rutgers University
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Comprehensive Description

provided by Smithsonian Contributions to Zoology
Alasmidonta (Pressodonta) heterodon (Lea, 1830)

Unio heterodon Lea, 1830:428, pl. 8:fig. 11 [Type-locality: “Schuylkill [River] and Derby [sic] Creek, P[ennsylvani]a.” Figured specimen and other original material not in Smithsonian Institution. Syntypes in mollusk collection of Academy of Natural Sciences of Philadelphia, catalog numbers 41004 and 41005 (Johnson, 1970:347; Johnson and Baker 1973:157).]

THE SHELL

DESCRIPTION.—Shell small, subtrapezoidal or “hump backed,” with unusual hinge teeth, up to 56 1/2 mm long, 31 mm high, and 18 1/2 mm wide, slightly thickened anteriorly (up to about 2 mm thick) and thinner, but not fragile, posteriorly. Anterior margin sharply curved; ventral margin broadly and flatly curved, predominantly straight, or slightly concave centrally; posterior margin roundly pointed near the base and broadly and obliquely truncated above; and dorsal margin of medium length and slightly curved. Maximum inflation a little above the center of the shell. Beaks low, rounded, located slightly more than 1/4 the distance from anterior to posterior, and projecting only a little above the hinge line. Posterior ridge rounded, somewhat inflated, and rather prominent. Posterior slope of medium width, concave above, and in some specimens traversed below by a low, rounded, radial ridge above the posterior ridge. Growth increments marked by concentric wrinkles and lines, especially in northern specimens. Except for lines of growth, additional post-juvenile sculpturing is lacking. Periostracum yellowish, olive brown, or blackish brown and, in some specimens, with narrow and wide reddish brown rays.

Hinge teeth small but well developed and unusual. Pseudocardinal teeth elevated, compressed, serrated, and numbering 1 or 2 in the right valve and 2 in the left. Interdental projection in left valve well-marked and articulating with a corresponding depression in the right valve. Lateral teeth narrow but strong, extending posteriorly to the end of the ligament or a little beyond, and characteristically 2 in the right valve and 1 in the left, the reverse of all other North American species having lateral teeth. Beak cavity rather narrow and not very deep. Anterior muscle scars impressed, pallial line well marked anteriorly but becoming somewhat obscure posteriorly, posterior muscle scars shallow but clearly marked, and scars within beak cavity consisting of a small ovate, elongate pit on the back of the hinge plate. Nacre bluish or silvery white, iridescent posteriorly, and with pinkish or salmon suffusions near the beak cavity.

Beak sculpture strong and composed of about 4 or 5 moderately heavy, blunt bars, the first 2 concentric and simple, the following ones broadly double-looped and forming sharp angles on the posterior ridge. Ridges visible only in well-preserved young specimens.

VARIATION.—Ortmann (1919:174) observed sexual differences in the shell, i.e.: “The male as a rule has a more compressed, and more ovate and elongate shell, with the lower margin gently and uniformly curved, the posterior ridge less sharp, and the posterior slope not truncated; while in the female the shell is more swollen in the region of the posterior ridge and just in front of it; has a more distinct posterior ridge, which renders the posterior slope more truncate, and makes the whole outline of the shell shorter and more trapezoidal. Furthermore in the female the lower posterior angle is more produced downward, so that the lower margin of the shell becomes rather straight, in some cases even concave.” Sexual differences in the shells of young specimens are not apparent.

Aside from this somewhat obscure sexual dimorphism the species is rather uniform in shell features (Table 7). There is some variation in the development of the hinge teeth. Specimens from some canals also tend to become larger and paler than those from other localities. The largest specimen seen, 56.5 mm long, is from a medium-sized river (Ashuelot River) near Keene, New Hampshire. Some of the largest specimens are also more conspicuously rayed than small, dark-colored specimens. The latter appear to be more characteristic of fine substrates containing organic material. This condition often occurs near river banks and coincides in part with the general trend seen in other unionids: that at a given river site small, dark-colored specimens tend to occur in mud near river banks whereas larger, paler specimens of the same species tend to occur in sandy substrates farther from the river banks when the current is more rapid.

TOPOGRAPHIC ANATOMY

SPECIMEN DESCRIBED.—From Petitcodiac River, Riverglade, 19 mi (30.4 km) WSW of Moncton, N.B., collected 22 June 1960 (NMC 46074, A. H. Clarke station C50); preserved directly in 70% ethyl alcohol; shell length 31.6 mm, presumed sex male.

DESCRIPTION.—Mantle pale brown but covered in the central portion with a network of fine, short, white, filamentous muscle fibers coalesced into spots and strands and in the posterior region by beautiful silvery radial muscle strands. Adductor muscles orange and contrasting with the mantle. A brown pigmented band runs just within the edge of the mantle from the posterior part of the ventral region to the posterior region and dorsally (touching the mantle edge) to a point above the posterior adductor. The incurrent opening is 5 mm long and surrounded just within the edge by about 3 ranks of small, narrow, reddish brown, pyramidal papillae, the inner papillae the longer (about 1.0 mm). Separation of incurrent and anal openings achieved by the diaphragm and by a narrow (0.5 mm) zone on each mantle edge that is held in contact with its opposite member during life. Anal opening 4 mm long and with crenulate edges and with a dark, reddish brown color band just within the opening. Mantle connection between anal and supra-anal opening of medium length (3.5 mm). Supra-anal opening narrow, slit-like, bordered within by a brown band, and 3 mm in length.

Demibranchs pale brown in preserved specimen. Outer demibranch 19.7 mm long, 5.9 mm high, with tapering ends and convex, ventral edge and with wavy radial wrinkles. Surface tissue with about 12 double radial filaments per mm and about 4 cross filaments; water tubes about 2.0 per mm. Inner demibranch about 26 mm long, 13 mm high, also with rounded ends and convex ventral edge, and extending well beyond the outer demibranch anteriorly and ventrally but only slightly overlapping it posteriorly. Surface tissue as in outer demibranch but cross filaments more obscure; water tubes also about 2.0 per mm. Inner lamina of inner demibranch not attached to visceral mass. Diaphragm split near the anal opening and perforated by the ends of the water tubes.

Labial palps narrow; slightly overlapping the inner demibranch; with long convex ventral edge; shorter, flatly sigmoid dorsal edge; sharp, centrally located posterior point; and with dorsal edges rolled outward. The outer surfaces are smooth and the inner opposing surfaces of each member are radially furrowed (about 7 furrows per mm at the margin); the furrows are also visible through the outer palp surfaces. The outer palpus is fused to the mantle and, for about 2/3 of its length, to the inner palpus.

Ortmann (1912:295) states: “Color of soft parts whitish; charged marsupium brown.” In live specimens collected from Ashuelot River near Keene, New Hampshire, the foot was orange.

VARIATION.—Table 8 shows the extent of variation of most of the features observed in available material. Mantle pigmentation is in a continuous band and is restricted to the posterior region in all specimens, although it differs in intensity between individuals. The incurrent opening is slightly longer than the anal or supra-anal openings (which are about equal in length) and the mantle connection between the anal and supra-anal openings varies from being approximately equal to them in length (6 specimens) to being much shorter (2 specimens). The labial palps overlap or touch the inner demibranch in 7 of the 8 specimens examined. These observations are in only partial agreement with those of Ortmann (1912:295) who reported that in about 30 specimens seen from Pennsylvania, A-SA is shorter than A in all of them, and the labial palps do not touch the inner demibranch.

Other features examined were the presence or absence of crenulation at the margin of the anal opening and relative dimensions of the demibranchs. The Petitcodiac River specimens are all finely crenulated and the Tar River specimen is strongly crenulated. The length and height of the demibranchs were measured and are given below expressed as a percentage of the shell length. Petitcodiac River specimens: outer demibranch, length 57%–63%, height 16%–19% (females) and 23% (male); inner demibranch: length 62%–70%, height 26%–30% (females) and 31% (male). Tar River specimen (gravid): outer demibranch, length 62%, height 34%, inner demibranch, length 68%, height 34%. The inner lamina of the inner demibranch was free from the visceral mass in all specimens.

GLOCHIDIUM

DESCRIPTION.—Glochidium depressed pyriform, with hinge straight, apex protuberant, and valves convex and rounded. Shell 0.255 mm high, 0.325 mm long, and about 0.100 mm in single valve convexity. The posterior margin is longer and more convex than the anterior and the apex is located about 42% of the distance from anterior to posterior (measured parallel to the hinge axis). Except for a band near the margin and near the apex the shell is pockmarked with shallow depressions (about 5–10 μm wide) and tiny pits (1–2 μm wide) within many of the depressions. The hinge is about 0.267 mm in length.

Each apical stylet is flatly recurved, about 0.080 mm long, about 0.028 mm wide at the base, tapering rapidly in the proximal third of its length to about half that width, and tapering gradually in the distal portion. Each stylet is connected on each side, and for most of its length, by a wide membrane which is attached to the valve margin. The exposed surface of each stylet is covered with major microstylets, each about 10 μm long and 5 μm wide, and bluntly pyramidal in shape. On the distal two-thirds of the stylet they are arranged alternately in transverse rows of 2 or 1 microstylets, or in alternate positions in successive rows each with 2 microstylets. The microstylets become more numerous and smaller on the base of the stylet and extend as small micropoints (<0.5 μm) onto the shell surface near the apex and onto the supporting membrane.

The glochidium described is from an adult collected from Canoe River, 2.45 mi (3.9 km) NNE of Norton, Bristol Co., Massachusetts by H. D. Athearn on 2 June 1969 (OSUM 25106). Other glochidia from the same adult were similar although minor variations in valve shape and convexity were apparent.

LIFE HISTORY

GRAVID PERIOD.—Ortmann (1919:174) gives the month of February and 24 April as gravid dates for A. heterodon. Additional dates provided now are 2 June 1969 for a specimen from Canoe River near Norton, Massachusetts (mature glochidia) and 27 August 1977 for a specimen from Tar River near Creedmore, North Carolina (immature glochidia). In the species as a whole the gravid period therefore spans at least the period from late August to the following early part of June.

NATURAL HOST.—Not recorded.

HABITAT.—”This is a rather rare and inconspicuous species…[It] occurs in medium or rather slow-flowing rivers of varying size on gravel, sand, or muddy sand bottoms and sometimes among submersed aquatic plants” (Clarke and Berg, 1959:25). In the Ashuelot River 4 mi (6.4 km) west of Keene, New Hampshire, on 8 August 1978, I found A. heterodon in muddy sand in 12 to 18 inches of water depth near the river bank under overhanging tree limbs. It shows markedly clumped distribution there and in the Petitcodiac River, the only localities from which I have collected it in abundance. Ortmann (1919:173) has also reported it as abundant in a canal. Its usual associate is Elliptio complanata and, occasionally, Strophitus undulatus or other riverine species.

GEOGRAPHICAL RECORDS

PETITCODIAC RIVER SYSTEM, NEW BRUNSWICK.—North River, 5 mi (8.0 km) NW of Salisbury, Westmoreland Co. (Athearn, 1953). Petitcodiac River at River Glade, 19 mi (30.0 km) WSW of Moncton, Westmoreland Co., (1960, A. H., A. R., and Louise R. Clarke! (NMC)).

MERRIMAC RIVER SYSTEM, MASSACHUSETTS.—Merrimac River, Andover, Essex Co. (MCZ).

TAUNTON RIVER SYSTEM, MASSACHUSETTS.—Canoe River, 2.45 mi (3.9 km) NNE of Norton, Bristol Co. (1969, H. D. Athearn! (OSUM)).

AGAWAM RIVER SYSTEM, MASSACHUSETTS.—Agawam River (MCZ).

CONNECTICUT RIVER SYSTEM.—Connecticut River at Bloomfield, Essex Co., Vt. (MCZ); Northumberland, Coos Co., N.H. (ANSP and MCZ); Ryegate, Caledonia Co., Vt. (MCZ); 2 mi (3.2 km) N of Monroe, Grafton Co., N.H.; Hanover, Grafton Co.; Northfield, Franklin Co., Mass. (all MCZ); Canal, Westfield, Hampden Co., Mass. (ANSP, MCZ, USNM); Springfield, Hampden Co.; and Granby, Hartford Co., Conn. (both USNM). Ashuelot River, 2.5 mi (4.0 km) N of Keene, Cheshire Co. and 2 mi (3.2 km) NW of Keene (both 1954, A. H., A. R. and Louise R. Clarke! (NMC). Philo Brook, Suffield, Hartford Co., Conn. (1959, S.L.H. Fuller! (MCZ)). Scantic River, 0.5 mi (0.8 km) above Hampden, Hampden Co., Mass. (1951, H. D. Athearn! (MCZ)).

QUINNIPIAC RIVER SYSTEM, CONNECTICUT.—Ten Mile River, Mixville, New Haven Co. (ANSP, MCZ). Quinnipiac River, Meriden, New Haven Co. (MCZ). Wilmot Brook, New Haven, New Haven Co. (MCZ).

HACKENSACK RIVER SYSTEM.—Brook flowing W from Closter to Hackensack, Bergen Co., N.J. (ANSP).

DELAWARE RIVER SYSTEM, PENNSYLVANIA.—Delaware River Drainage: Delaware River, Shawnee, Monroe Co. (Ortmann, 1919). Princess Creek, Kunkleton, Monroe Co. (Ortmann, 1919). Pohopoco Creek, 6 mi (9.6 km) E of Leighton, Carbon Co. (USNM). Delaware River, Bucks Co. (MCZ).

Schuylkill River Drainage: Big Neshaminy Creek near Edderson, Bucks Co. (ANSP; Ortmann, 1919). Schuylkill River at Hazellea, Chester Co. (ANSP); also at junction with Darby Creek, Delaware Co. (Ortmann, 1919); Canal, Manayunk, Philadelphia Co. (ANSP; Ortmann, 1919); below Fairmont Dam, Philadelphia Co. (Ortmann, 1919).

SUSQUEHANNA RIVER SYSTEM.—Susquehanna River, Columbia, Lancaster Co., Pa. (ANSP).

POTOMAC RIVER SYSTEM.—Potomac River near Washington, D.C. (USNM). McIntosh Run, 4 mi (6.4 km) N Leonardstown, St. Mary's Co., Md. (Johnson, 1970).

RAPPAHANOCK RIVER SYSTEM, VIRGINIA.—Rappahanock River Drainage: Mountain Run, Culpeper Co. (Ortmann, 1919). Marsh Run, 3 mi (4.8 km) SE of Remington, Fauquier Co. (Ortmann, 1919).

Rapidan River Drainage: Blue River, Orange Co. (USNM; Johnson, 1970).

JAMES RIVER SYSTEM, VIRGINIA.—North River, Lexington, Rockbridge Co. (ANSP and USNM).

PAMLICO RIVER SYSTEM, NORTH CAROLINA.—Tar River, Hwy 15, 5 mi (8 km) N of Creedmore, Granville Co. (1977, A. H. and J. J. Clarke! (USNM)).

NEUSE RIVER SYSTEM, NORTH CAROLINA.—Neuse River at Poolec Bridge, Wake Co. (MCZ); Raleigh, Wake Co. (MCZ); 6 mi (9.6 km) E of Raleigh (Johnson, 1970); and NE of Wendell, Wake Co. (USNM). Little River at Tarpley's Mill, 2 mi (3.2 km) NE of Wendell, Wake Co., (1950–51, W. Walter! (MCZ); Walter, 1956).

TYPE-SPECIES.—Alasmidonta mccordi Athearn, here designated.

Alasmidonta (Alasmidens) mccordi is principally distinguished by its weak beak sculpturing which does not extend more than 6 mm beyond the umbonal apex, by the presence of a lunule, and by the pseudocardinal teeth in the right valve that are curved, placed one above the other, and oriented parallel with the lunule. Other members of Alasmidonta (sensu lato) have stronger beak sculpturing, do not possess a lunule, and the pseudocardinal teeth in the right valve, if well-developed, are placed beside each other and are approximately perpendicular with the dorsal margin. Alasmidonta (Alasmidens) mccordi is probably now extinct.
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Clarke, Arthur Haddleton. 1980. "The tribe Alasmidontini (Unionidae, Anodontinae), Part I: Pegias, Alasmidonta and Arcidens." Smithsonian Contributions to Zoology. 1-101. https://doi.org/10.5479/si.00810282.326.1

Dwarf wedgemussel

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The dwarf wedgemussel (Alasmidonta heterodon) is an endangered species of freshwater mussel, an aquatic bivalve mollusk in the family Unionidae, the river mussels.

Distribution and conservation status

This is a rare species found solely in North America's Atlantic coast streams and rivers of various sizes and moderate current.

The dwarf wedge mussel's current range extends from New Hampshire to North Carolina. The dwarf wedge mussel is federally listed as endangered and state-listed as endangered in Connecticut, Massachusetts, Maryland, North Carolina, New Hampshire, New Jersey, New York, Pennsylvania, Virginia, and Vermont.

It previously lived in New Brunswick, but it is locally extirpated in Canada since 1968.[4] The Canadian Species at Risk Act listed the dwarf wedgemussel in the List of Wildlife Species at Risk as being extirpated in Canada.[5]

Biotope

This mussel may be found in small creeks to deep rivers in stable habitats with substrates ranging from mixed sand, pebble and gravel, to clay and silty sand. In the southern portion of its range, it is often found buried under logs or root mats in shallow water (USFWS 1993), where in the northern portion of its range, it may be found in firm substrates of mixed sand, gravel or cobble, or embedded in clay banks in water depths of a few inches to greater than 20 feet (Fichtel and Smith 1995; Gabriel 1995; Gabriel 1996; Nedeau and Werle 2003; Nedeau 2004a, 2004b, 2006).

Description

The dwarf wedgemussel is possibly the only freshwater mussel from North America that has two lateral teeth on the right valve and only one on the left side.[3]: 9447  The dwarf wedgemussel is a small mussel, whose shell size rarely exceeds 45 millimetres (1.8 in) in length and 25 millimetres (0.98 in) high. The trapezoidal-shaped shells are colored brown or yellowish-olive, with reddish brown or greenish rays in young or pale specimens. The nacre is bluish or silvery white, and is iridescent on the posterior.

Biology and ecology

Its reproductive cycle is typical of other freshwater mussels, requiring a host fish on which its larvae (glochidia) parasitize and metamorphose into juvenile mussels. The dwarf wedgemussel is not a long-lived species as compared to other freshwater mussels; life expectancy is estimated at 10 to 12 years (Michaelson and Neves 1995).

A number of fish species have been positively identified as hosts for the dwarf wedgemussel. Michaelson and Neves (1995) confirmed the tessellated darter (Etheostoma olmstedi), Johnny darter (Etheostoma nigrum), and mottled sculpin (Cottus bairdi) as host fish for dwarf wedgemussels in the southern part of its range. Wicklow (in New Hampshire Wildlife Action Plan 2005) confirmed the slimy sculpin (Cottus congatus) and juvenile and parr of the Atlantic salmon (Salmo salar) as host fish for dwarf wedgemussels in New Hampshire.

The dwarf wedgemussel is considered to be a long-term brooder. In general, dwarf wedgemussel glochidia may be released between March and June, with peak release times varying from south to north. Michaelson and Neves (1995) documented the reproductive cycle of the dwarf wedgemussel from North Carolina and observed that this species spawns in late summer, becomes gravid in September, and releases glochidia in April. Wicklow (in New Hampshire Wildlife Action Plan 2005) observed glochidia release beginning in March and continuing through June in the Ashuelot River in New Hampshire. In a study of dwarf wedgemussel reproduction in the Mill River, Massachusetts, McLain and Ross (2005) observed that most glochidia were released in April and May.

Reproductive output appears to be correlated with local population abundance. McLain and Ross (2005) documented that sites with the highest abundance of adult dwarf wedgemussels also demonstrated the highest proportion of gravid females, glochidial density, host infection, and density of juvenile mussels.

Populations

At one time, this species was recorded from 70 localities in 15 major drainages ranging from North Carolina to New Brunswick, Canada. Since the species was first listed as endangered by the U.S. Fish and Wildlife Service in 1990 (55 FR 9447 9451), a number of new locations have been discovered and a number of known locations are possibly no longer extant. Based on preliminary information, the dwarf wedgemussel is currently found in 15 major drainages, comprising approximately 70 “sites” (one site may have multiple occurrences). At least 45 of these sites are based on less than five individuals or solely on spent shells. The only known occurrence in New Brunswick, Canada (Petticodiac River) appears to be historic; no live mussels or spent shells were found during a 1997 survey (Hanson 1998).

The mainstem of the Connecticut River in New Hampshire and Vermont is considered to have the largest remaining dwarf wedgemussel population, consisting of three distinct stretches of sporadically occupied habitat segmented by hydroelectric dams. It is estimated that there are hundreds of thousands of dwarf wedgemussels scattered within an approximate 75-mile stretch of the Connecticut River. The Ashuelot River in New Hampshire, the Farmington River in Connecticut, and the Neversink River in New York harbor large populations, but these number in the thousands only. The remaining populations from New Jersey south to North Carolina are estimated at a few individuals to a few hundred individuals.

Strayer et al. (1996) speculated that many dwarf wedgemussel populations, particularly in the southern portion of the range, may be threatened by low densities, small ranges. and linear structure (i.e., an entire population in one stream with no possibility of refuge from catastrophes or stochastic events). Low-density populations may lead to a loss of productivity due to reproductive impediments (e.g., the distance between mussels being too great) or loss of genetic variability. The Mill River in Hatfield and Whately, Massachusetts is an example of a river with a dwarf wedgemussel population patchily distributed over an approximate 16-mile stretch. The most reproductively robust patch is limited to a small stretch (< 1 mile) making it extremely vulnerable to a catastrophic event. The remainder dwarf wedgemussels are sparsely scattered and may demonstrate a reduced capability to reproduce as indicated by McLain and Ross (2005).

Agricultural run-off has been identified as a significant threat to dwarf wedgemussel populations in Massachusetts, Maryland, and North Carolina. In 2001, more than 25 dwarf wedgemussels and hundreds of other mussels (including state-listed species) were killed in the Mill River, Massachusetts, by waste run-off from a small farm.

Recently, severe flooding in the Baltimore and Neversink Rivers in Pennsylvania and New York, respectively, resulted in the destruction of occupied habitat and loss of dwarf wedgemussels. Surveys conducted at two sites on the Neversink River below a dam in Cuddebackville, New York, derived abundance estimates ranging from 60 to 500 dwarf wedgemussels per site (Cole et al. 2004) prior to 2005. Severe flooding in the spring of 2005 scoured the river channel and deposited cobble in at least one of the sites previously surveyed. Resurveys in 2005 of the two sites conducted after the flood event detected one fresh dead dwarf wedgemussel and no live mussels (Cole and White 2006). Surveys in 2006 indicated that the dwarf wedgemussel population in the Neversink River was adversely affected by flood events, although some live mussels were detected.

Little riverine habitat adjacent to extant populations is protected other than by state shoreline protection regulations or local land use regulations. Development of adjacent uplands continues to be a significant and pervasive threat to southern populations. In summary, it appears that the populations in North Carolina, Virginia, and Maryland are declining as evidenced by low densities, lack of reproduction, or inability to relocate any dwarf wedgemussels in follow-up surveys. Populations in New Hampshire, Massachusetts, and Connecticut appear to be stable, while the status of populations in the Delaware River watershed affected by the recent floods of 2005 is uncertain at this time.

References

Footnotes

  1. ^ Cummings, K.; Cordeiro, J. (2011). "Alasmidonta heterodon". IUCN Red List of Threatened Species. 2011: e.T775A13077570. doi:10.2305/IUCN.UK.2011-2.RLTS.T775A13077570.en. Retrieved 13 November 2021.
  2. ^ "Dwarf wedgemussel (Alasmidonta heterodon)". Environmental Conservation Online System. U.S. Fish & Wildlife Service. Retrieved 23 April 2023.
  3. ^ a b 55 FR 9447
  4. ^ COSEWIC. 2005. Canadian Species at Risk]. Committee on the Status of Endangered Wildlife in Canada. 64 pp., page 8.
  5. ^ "Dwarf Wedgemussel (Alasmidonta heterodon)". Species at risk public registry. Government of Canada. 2 February 2021. Retrieved 23 April 2023.

Bibliography

  • Dwarf Wedgemussel Recovery Plan: US Fish and Wildlife Service (PDF document)
  • NatureServe Explorer report
  • Dwarf Wedgemussel Fact Sheet
  • Andrew Moser, G. and the Fish and Wildlife Service. 14 March 1990. Endangered and Threatened Wildlife and Plants; Determination of Endangered Status for the Dwarf Wedge Mussel. Federal Register, 55(50):9447-9451.
  • Cole, J. C., B. S. White and C. Apse. 2004. A quantitative assessment of freshwater mussels (Bivalvia:Unionidae) in the Neversink River prior to the Cuddebackville Dam removal. Report to The Nature Conservancy, Cuddebackville, New York. 16 pp.
  • Cole, J. and B. S. White. 2006. An assessment of freshwater mussels in the Neversink River following removal of the dam at Cuddebackville, NY and a severe spring flood event. Report to The Nature Conservancy, Cuddebackville, NY. 12 pp.
  • Fichtel, C. and D. G. Smith. 1995. The Freshwater Mussels of Vermont. Nongame and Natural Heritage Program, Vermont Fish and Wildlife Department. Technical Report 18. 53 pp.
  • Gabriel, M. 1995. Freshwater mussel distribution in the rivers and streams of Cheshire, Hillsborough, Merrimack and Rockingham, Counties, New Hampshire. Report submitted to U.S. Fish and Wildlife Service, New England Field Office and New Hampshire Fish and Game Department. 60 pp.
  • Gabriel, M. 1996. 1996 Monitoring of the dwarf wedgemussel (Alasmidonta heterodon) in the Ashuelot and Connecticut Rivers, New Hampshire. Report submitted to The Nature Conservancy, Eastern Regional Office, Boston, Massachusetts. 27 pp.
  • Hanson, M. J. 1998. March 24. Re: status of dwarf wedgemussel [personal email]. Accessed March 24, 1998.
  • McLain, D. and M. R. Ross. 2005. Reproduction based on local patch size of Alasmidonta heterodon and dispersal by its darter host in the Mill River, Massachusetts, USA. Jour. N. Am. Benthol. Soc., 24(1):139-147.
  • Michaelson, D. L. and R. J. Neves. 1995. Life History and habitat of the endangered dwarf wedgemussel Alasmidonta heterodon (Bivalvia:Unionidae). Jour. N. Am. Benthol. Soc. 14:324-340.
  • Nedeau, E. J. 2004a. A Fourth Investigation of the Survival of Dwarf Wedgemussels (Alasmidonta heterodon) for the Relocation Project on the Connecticut River, Route 2 Stabilization Project, Lunenburg, Vermont. Unpublished report submitted to the U.S. Fish and Wildlife Service, Concord, New Hampshire. 7 pp.
  • Nedeau, E. J. 2004b. Quantitative survey of dwarf wedgemussel (Alasmidonta heterodon) populations downstream of the Surry Mountain Flood Control Dam on the Ashuelot River. . Unpublished report submitted to the U.S. Fish and Wildlife Service, Concord, New Hampshire. 12 pp.
  • Nedeau, E. 2006. Characterizing the Range and Habitat of Dwarf Wedgemussels in the “Middle Macrosite” of the Upper Connecticut River. Unpublished report submitted to the U.S. Fish and Wildlife Service, Concord, New Hampshire. 6 pp.
  • Nedeau, E. J. and S. Werle. 2003. Freshwater Mussels of the Ashuelot River: Keene to Hinsdale. Unpublished report submitted to the U.S. Fish and Wildlife Service, Concord, New Hampshire. 50 pp.
  • Strayer, D. L., S. J. Sprague and S. Claypool. 1996. A range-wide assessment of populations of the dwarf wedgemussel Alasmidonta heterodon. J. N. Am. Benthol. Soc. 15(3):308-317.
  • U.S. Fish and Wildlife Service. 1993. Dwarf Wedge Mussel Alasmidonta heterodon Recovery Plan. Hadley, Massachusetts. 52 pp.
  • Wicklow, B. 2005. in New Hampshire Wildlife Action Plan. New Hampshire Fish and Game Department, 11 Hazen Dr., Concord, NH, 03301. pp. A26-A35.
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Dwarf wedgemussel: Brief Summary

provided by wikipedia EN
Wikimedia Commons has media related to Alasmidonta heterodon.

The dwarf wedgemussel (Alasmidonta heterodon) is an endangered species of freshwater mussel, an aquatic bivalve mollusk in the family Unionidae, the river mussels.

license
cc-by-sa-3.0
copyright
Wikipedia authors and editors
original
visit source
partner site
wikipedia EN