(DRAFT) - Taxonomy
                       Species MUSSEL, PEARLY, CUMBERLAND BEAN
                                Species Id ESIS404011
                                   Date 13 MAR 96



TAXONOMY

NAME - MUSSEL, PEARLY, CUMBERLAND BEAN OTHER COMMON NAMES - MUSSEL, PEARLY and CUMBERLAND BEAN;CUMBERLAND BEAN ELEMENT CODE - CATEGORY - Aquatic Molluscs PHYLUM AND SUBPHYLUM - MOLLUSCA, CLASS AND SUBCLASS - BIVALVIA, ORDER AND SUBORDER - UNIONOIDA, FAMILY AND SUBFAMILY - UNIONIDAE, GENUS AND SUBGENUS - VILLOSA, SPECIES AND SSP - TRABALIS, SCIENTIFIC NAME - VILLOSA TRABALIS AUTHORITY - TAXONOMY REFERENCES - COMMENTS ON TAXONOMY - Cumberland Bean Pearly Mussel Villosa trabalis (Conrad, 1834) KINGDOM: Animal GROUP: Clam PHYLUM: Mollusca CLASS: Bivalvia ORDER: Unionoida FAMILY: Unionidae V. trabalis is a small Cumberlandian species with inflated, elongate, oval valves (01). Beaks are located near the anterior end where the shell is thickest, and sculptured with double-looped ridges (02). The posterior ridge is almost full and rounded, with the surface marked by irregular growth lines. Periostracum is semi-glossy, olive-green to blackish in color, with many narrow, wavy green rays that are numerous on the posterior margin (01). The beak cavity is shallow with impressed anterior muscle scars. Nacre color is white and usually irridescent posteriorly (03). A slight sexual dimorphism exists in this species. The male shell is narrowed centrally and drawn out posteriorly whereas the female shell is higher and more evenly ovate, with an evenly curved basal edge (02,04). This species is readily separated from other species, although eroded valves of V. trabalis and V. perpurpurea are difficult to separate (04,05). Taxonomy - 1 (DRAFT) - Taxonomy Species MUSSEL, PEARLY, CUMBERLAND BEAN Species Id ESIS404011 Date 13 MAR 96 Detailed descriptions and photographs of V. trabalis are included in previous publications (01,02,06). Taxonomy - 2
                                  (DRAFT) - Status
                       Species MUSSEL, PEARLY, CUMBERLAND BEAN
                                Species Id ESIS404011
                                   Date 13 MAR 96



STATUS

Coded Status Alabama; Federal Endangered Georgia; Federal Endangered Georgia; State Recognized Kentucky; Federal Endangered Kentucky; State Recognized Tennessee; Federal Endangered Tennessee; State Recognized Virginia; Federal Endangered Virginia; State Recognized E: Federal Endangered COMMENTS ON STATUS - U.S. STATUSES AND LAWS: The Cumberland bean pearly mussel (Villosa trabalis) has been designated an Endangered species pursuant to the Endangered Species Act of 1973 (50 CFR 17.11; P.L. 93-205, 87 Stat. 884; 16 U.S.C. 1531-1540), as amended. The species has this status wherever found including the States of Alabama, Georgia, Kentucky, Tennessee and Virginia. This species is protected by the Lacey Act (P.L. 97-79, as amended; 16 U.S.C. 3371 et seq.) which makes it unlawful to import, export, transport, sell, receive, acquire, or purchase any wild animal (alive or dead including parts, products, eggs, or offspring): (1) in interstate or foreign commerce if taken, possessed, transported or sold in violation of any State law or regulation; or (2) if taken or possessed in violation of any U.S. law, treaty, or regulation or in violation of Indian tribal law. It is also unlawful to possess any wild animal (alive or dead including parts, products, eggs, and offspring) within the U.S. territorial or special maritime jurisdiction (as defined in 18 U.S.C. 7) that is taken, possessed, transported, or sold in violation of any State law or regulation, foreign law, or Indian tribal law. RESPONSIBLE FEDERAL AGENCIES: USFWS -Responsible for the management/recovery, listing, and law enforcement/protection of this species. DOD (COE) -Responsible for the law enforcement/protection of this species with applicable State and Federal laws on public land under their control. Also responsible for management/recovery on Department of Defense lands. All Federal agencies have responsibility to ensure that any action authorized, funded, or carried out by that agency is not likely to jeopardize the continued existence of the species or result in the Status - 1 (DRAFT) - Status Species MUSSEL, PEARLY, CUMBERLAND BEAN Species Id ESIS404011 Date 13 MAR 96 destruction or adverse modification of Critical Habitat (50 CFR 402), and to utilize their authorities to carry out programs for the conservation of the species. STATE STATUSES AND LAWS: STATE: Georgia, Kentucky, Tennessee and Virginia DESIGNATED STATUS: Recognized Endangered ADMINISTRATIVE AGENCY: (GA) Department of Natural Resources; (KY) Dept. of Fish and Wildlife Res.; (TN) Wildlife Resource Agency; (VA) Commission of Game and Inland Fisheries. STATE STATUTES: (GA) Endangered Wildlife Act of 1973, GA Game and Fish Codes, GA Law 1977, Page 396 GA Code Ann., Sec. 45-101, et. seq.; (KY) Fish and Wildlife Codes, 150.183. Importing, transporting, or possessing endangered species or wildlife. (TN) Annotated Code, Title 51, Chapter 9, Section 51-903; (Virginia) Code of VA, Title 29. INTERNATIONAL STATUSES, TREATIES, AND AGREEMENTS: CITES I ECONOMIC STATUSES: No commercial values are known, however, the species' sedentary nature and filter feeding habits may make it useful as a water quality indicator. It has been shown that mussels accumulate such pollutants as heavy metals and pesticides. 74/10/17:39 FR 37078/37079 - Notice of review 75/09/26:40 FR 44329/44333 - Proposed rule 76/06/14:41 FR 24062/24067 - Final rule 76/06/16:41 FR 24367/24378 - Proposal - CITES I 77/02/22:42 FR 10484/10485 - Final - CITES I 81/02/27:46 FR 14652/14658 - Five year review 87/07/07:52 FR 25523/25528 - Notice of review Status - 2
     

HABITAT ASSOCIATIONS

HABITAT - AQUATIC INLAND AQUATIC LAND USE - Streams and Canals NATIONAL WETLAND INVENTORY CODES NWI NWICLS NWIMOD NWISPEC Riverine, upper perennial UB1 Riverine, upper perennial SB1 COMMENTS ON HABITAT ASSOCIATIONS - V. trabalis is typically found in sand and gravel substrates in medium-sized (3-5 order) streams (03). Habitat is usually riffle and run areas with moderate gradient and clean, stable substrate (01). This species does not occur in the impounded sections of rivers. It is apparently quite sedentary and is buried in shallow water with suitable habitat. V. trabalis appears to be intolerant of silt, and requires ample water flow and stable substrate for survival (01). Habitat of the glochidia is initially within the gills of the female, then in the water column, and finally attached to a suitable fish host. Any alteration of these life stage-specific habitats during its life cycle would likely affect the long term success of a population. Habitat requirements or associations for the juvenile stage are unknown. Specific environmental requirements for the adults are also unknown. Habitat Associations - 1
                                (DRAFT) - Food Habits
                       Species MUSSEL, PEARLY, CUMBERLAND BEAN
                                Species Id ESIS404011
                                   Date 13 MAR 96



FOOD HABITS

TROPHIC LEVEL - OMNIVORE LIFESTAGE FOOD FOOD PART General Detritus General Bacteria General Phytoplankton General Diatoms General Zooplankton General Fish Food Habits - 1
                         (DRAFT) - Environment Associations
                       Species MUSSEL, PEARLY, CUMBERLAND BEAN
                                Species Id ESIS404011
                                   Date 13 MAR 96



ENVIRONMENTAL ASSOCIATIONS

G = General A = Adult LIM = Limiting RA = Resting Adult J = Juvenile FA = Feeding Adult RJ = Resting Juvenile BA = Breeding Adult FJ = Feeding Juvenile P = Pupae L = Larvae E = Egg RL = Resting Larvae FL = Feeding Larvae
LIFESTAGE ENVIRONMENTAL ASSOCIATIONS G Aquatic Features: Pool areas Environment Associations - 1
                               (DRAFT) - Life History
                       Species MUSSEL, PEARLY, CUMBERLAND BEAN
                                Species Id ESIS404011
                                   Date 13 MAR 96



LIFE HISTORY

FOOD HABITS: There are no known interspecific differences in feeding among freshwater mussels (07). The glochidia are probably obligate parasites on the gills or fins of fish (01). Adult mussels are filter-feeders and consume particulate matter suspended in the water column. Identifiable stomach contents almost invariably include mud, desmids, diatoms, other unicellular algae, protozoa, and zooplankters (16,17). No study of the food habits of V. trabalis has been conducted; required/preferred foods are therefore unknown. HOME RANGE/TERRITORY: Non-territorial. The species is sedentary during its adult life and generally occurs in streams with others of its kind. PERIODICITY: Observations on other Villosa spp. indicate that species of this genus exhibit a seasonal periodicity (18). During the spawning period in spring, specimens are near or on the surface of the stream bottom. After the spawning period, Villosa spp. occur deeper in the substrate with only siphons exposed. MIGRATION PATTERNS: Non-migratory. COVER/SHELTER REQUIREMENTS: The species occurs primarily in shallow water with stable, mixed substrate types and moderate current (01,18). No species-specific information on cover/shelter is available in the literature. REPRODUCTIVE SITE REQUIREMENTS: V. trabalis is a riffle and run species that occurs in free-flowing streams with moderate flow (01). Habitat is typically shallow water with stable, mixed substrate. Since this species appears to be sedentary and movement is inconsequential, this is the type of environment where all life processes are carried out, including reproduction. REPRODUCTIVE CHARACTERISTICS: The reproductive cycle of V. trabalis is presumed to be similar to other Villosa spp. (19). During spawning, males discharge sperm into the water column, and the sperm are taken in by the females during siphoning (01). Eggs are fertilized in the female's suprabranchial cavity or gills which serve as marsupia for embryos developing to the parasitic stage (glochidia). Glochidia are released by the female and must attach to a suitable fish host for metamorphosis to the free-living juvenile stage. V. trabalis is probably a long-term breeder (02), spawning in late summer, retaining glochidia through fall and winter, and releasing glochidia the following spring/summer. Glochidia are rather large, subovate, and hookless (20). The fish hosts for V. trabalis are unknown, but fish host studies for V. vanuxemi and V. nebulosa Life History - 1 (DRAFT) - Life History Species MUSSEL, PEARLY, CUMBERLAND BEAN Species Id ESIS404011 Date 13 MAR 96 have identified the banded sculpin, rock bass, and smallmouth bass as hosts (21). PARENTAL CARE: Except for retention of the glochidia within the gills of the female prior to release, no parental care occurs. POPULATION BIOLOGY: No information exists on the population biology of this species. SPECIES INTERRELATIONSHIPS: The required fish hosts for the parasitic glochidia of this species are unknown (01). OTHER LIFE HISTORY DESCRIPTORS: None. Life History - 2
                           (DRAFT) - Management Practices
                       Species MUSSEL, PEARLY, CUMBERLAND BEAN
                                Species Id ESIS404011
                                   Date 13 MAR 96



MANAGEMENT PRACTICES

RESULT MANAGEMENT PRACTICE Beneficial Developing/maintaining stream structures Beneficial Maintaining/Controlling Water Flow Beneficial Controlling/Restricting Road Maintainance Actions Beneficial Maintaining undisturbed/undeveloped areas Beneficial Land Acquisition Beneficial Controlling pollution [thermal, chemical, physical] Beneficial Controlling/Restricting Pesticide Use Beneficial Controlling/Restricting Herbicide Use Beneficial Controlling/Restricting Agricultural Practice Beneficial Stocking captive-reared wild-strain animals Beneficial Transplanting wild animals Beneficial Transplanting Wild Eggs/Wild Seeds Adverse Collecting Existing Collecting Adverse Inherent Reproductive Characteristics Existing Inherent Reproductive Characteristics Adverse Low Gene Pool Existing Low Gene Pool Adverse Underground Mines Existing Underground Mines Adverse Surface Mines Existing Surface Mines Adverse Siltation Existing Siltation Adverse Water Temperature Alteration Existing Water Temperature Alteration Adverse Dissolved Oxygen Reduction Existing Dissolved Oxygen Reduction Adverse Water Level Fluctuation Existing Water Level Fluctuation Adverse Reservoirs Existing Reservoirs Adverse Migration barriers Existing Migration barriers Adverse Dredging Existing Dredging Adverse Applying herbicides Existing Applying herbicides Adverse Applying pesticides Existing Applying pesticides Adverse Environmental Contamination/Pollution Existing Environmental Contamination/Pollution Adverse Exotic/Feral/Introducted Species Existing Exotic/Feral/Introducted Species Adverse Erosion Existing Erosion Adverse Existing Management Practices - 1 (DRAFT) - Management Practices Species MUSSEL, PEARLY, CUMBERLAND BEAN Species Id ESIS404011 Date 13 MAR 96 COMMENTS ON MANAGEMENT PRACTICES - The mussel fauna in most streams of the upper Tennessee River drainage has been impacted by dam construction, channelization, siltation, and water pollution, which directly affect all mussel species (01,07). The change from lotic to lentic conditions because of dams has also altered the species composition of the fish community, thus jeopardizing the reproductive success of some mussel species by eliminating required fish hosts. A total of 51 impoundments on the Tennessee and Cumberland Rivers has eliminated large sections of riverine habitat within the historic range of the Cumberland bean. Although siltation has been suggested as the most significant adverse effect of impoundments on mussels (07), other detrimental factors include lowered water temperatures, pH changes, oxygen depletion, and dewatering of mussel beds below dams (07). Mussel deaths can occur in substrate on which 0.6-2.5 cm of silt has accumulated, resulting in interference with feeding and suffocation (08). The siphoning period and metabolic rate of mussels can also be affected by such contaminants as heavy metals and agricultural chemicals (09). Coal waste from mining activities has contributed additional particulate matter to natural sediment loads, particularly in the Cumberland drainage (10). Negative impacts on mussels from coal mining, coal washing, and fly ash waste have been identified as major problems to recovery of this species (01,11). Water pollution is another major factor that has contributed to endangered status of V. trabalis. Numerous streams in the upper Tennessee drainage were polluted already by the early twentieth century, and the mussel fauna was in a decline at that time (12). The decline of this species in the upper Cumberland system has been attributed to pollution from acid mine wastes (03,13). The historic population in the Clinch River was likely affected by chemical spills in 1967 and 1970 at the APCO plant in Carbo, VA (14,15). All of the factors mentioned above (impoundments, siltation, coal mining, and water pollution) are still considered potential threats to remaining populations of V. trabalis. Other factors that may also be affecting this species include collecting by conchologists, the invasion of the Asiatic clam (Corbicula fluminea) into the Tennessee and Cumberland drainages, and the smaller gene pool which may be approaching minimum population size needed for sufficient genetic variation to respond to environmental changes. Substantial mussel die-offs of unknown origin that have occurred in the Tennessee and Cumberland River drainages since 1982 also pose a threat to the species' survival. APPROVED PLAN: U.S. Fish and Wildlife Service. 1984. Cumberland Bean Pearly Mussel Recovery Plan. U.S. Fish and Wildlife Service. Atlanta, GA. 58 pp. Recovery actions for the Cumberland bean pearly mussel include: (1) Utilize existing legislation to preserve populations and presently used habitat with emphasis on Buck Creek, Rockcastle, and Management Practices - 2 (DRAFT) - Management Practices Species MUSSEL, PEARLY, CUMBERLAND BEAN Species Id ESIS404011 Date 13 MAR 96 Little South Fork Cumberland Rivers. The protection of these populations and their habitats including transplanted individuals are essential for the continued survival of the species and will be required to meet the recovery objectives. Habitat restoration or improvement may be necessary to improve conditions for survival of the species (i.e., restoration of stream banks and channels and assuring optimum clean water flow). (2) Determine the status and range of the species by conducting population and habitat surveys. (3) Determine specific threats to the species from impacts such as coal mining and coal related pollution, road construction, dredging, herbicide and pesticide spraying, and chlorinated effluents. (4) Solicit help in the protection of the species and its habitat from local, state and federal developmental agencies. (5) Utilize Scenic River Status, mussel sanctuaries, land acquisitions and/or other means to protect the species where feasible. (6) Determine the feasibility of introducing the species back into its historic range and determine the best methods for doing so (e.g., introduction of adults, juveniles, infected fish, and/or artificially cultured individuals.) Introduce where feasible. Except for enforcement of regulations, there are no specific recovery programs involving this species. Management Practices - 3
                                   (DRAFT) - References
                         Species MUSSEL, PEARLY, CUMBERLAND BEAN
                                  Species Id ESIS404011
                                      Date 13 MAR 96



     

References

***** REFERENCES FOR ALL NARRATIVES EXCEPT N-OCCURRENCE ***** 01 U.S. Fish and Wildlife Service. 1983. Technical/Agency Draft Recovery Plan for the Cumberland Bean Pearly Mussel Villosa Trabalis (Conrad, 1834). U.S. Fish and Wildlife Service, Region 4, Atlanta, GA. 53 pp. 02 Bogan, A.E. and P.W. Parmalee. 1983. Tennessee's rare wildlife volume II: the mollusks. Tenn. Wildl. Resour. Agency, Tenn. Dep. Conserv., and Tenn. Heritage Prog., Univ. Tenn., Knoxville, TN 123 pp. 03 Clarke, A.H. 1981. Determination of the precise geographical areas occupied by four endangered species of freshwater mollusks. Final Rep., U.S. Fish and Wildlife Service. 226 pp. 04 Simpson, C.T. 1914. A Descriptive Catalogue of the Naiades or Pearly Freshwater Mussels. Bryant Walker, Detroit, MI. 3 Volumes. 1540 pp. 05 Ortmann, A.E. 1925. The naiad fauna of the Tennessee River system below Walden Gorge. Am. Midl. Nat. 9:321-372. 06 Parker, W. and L. Dixon. 1980. Endangered and threatened wildlife of Kentucky, North Carolina, South Carolina, and Tennessee. N.C. Agric. Ext. Serv. 122 pp. 07 Fuller, S.L.H. 1974. Clams and mussels (Mollusca:Bivalvia). Pages 215-273. IN: C.W. Hart and S.L.H. Fuller (eds.), Pollution Ecology of Freshwater Invertebrates, Academic Press, NY. 08 Ellis, M.M. 1931. Some factors affecting the replacement of the commercial fresh-water mussels. U.S. Bur. Fish. Circ. No.7. 10pp. 09 Salanki, J. 1979. Behavioural studies in mussels under changing environmental conditions. Symp. Biol. Hung. 19:169-176. 10 Branson, B.A. 1974. Stripping the Appalachians. Nat. Hist. 83:53-60. 11 Starnes, L.E. and W.C. Starnes. 1980. Discovery of a new population of Pegias fabula (Lea) (Unionidae). Nautilus 94:5-6. 12 Ortmann, A.E. 1918. The nayades (freshwater mussels) of the upper Tennessee drainage with notes on sysonymy and distribution. Proc. Am. Phil. Soc., Phila. 57:521-626. 13 Neel, J.K. and W.R. Allen. 1964. The mussel fauna of the upper Cumberland Basin before its impoundment. Malacologia 1:417-459. 14 Raleigh, R.F., D.H. Bennett, and L.O. Mohn. 1978. Changes in fish stocks after major fish kills in the Clinch River near St. Paul, Virginia. Am. Midl. Nat. 99:1-9. 15 Cairns, J., Jr., J.S. Crossman, K.L. Dickson, and E.E. Herricks. 1971. The recovery of damaged streams. Assoc. Southeast. Biol. Bull. 18:79-106. 16 Coker, R.E., A.F. Shira, H.W. Clark, and A.D. Howard. 1921. Natural history and propagation of fresh-water mussels. Bull. U.S. Bur. Fish. 37:77-181. 17 Churchill, E.P., Jr. and S.I. Lewis. 1924. Food and feeding in freshwater mussels. Bull. U.S. Bur. Fish. 39:439-471. 18 Neves, R.J. 1984. Personal observations. Va. Coop. Fish. Res. Unit, VPI & SU, Blacksburg, VA 24061. 19 Zale, A.V., and R.J. Neves. 1982. Reproductive biology of four References - 1 (DRAFT) - References Species MUSSEL, PEARLY, CUMBERLAND BEAN Species Id ESIS404011 Date 13 MAR 96 freshwater mussel species (Mollusca:Unionidae) in Virginia. Freshw. Invert. Biol. 1:17-28. 20 Ortmann, A.E. 1912. Notes upon the families and genera of the nayades. Ann. Carnegie Mus. 8:222-365. 21 Zale, A.V., and R.J. Neves. 1982. Fish hosts of four species of lampsiline mussels (Mollusca:Unionidae) in Big Moccasin Creek, Virginia. Can. J. Zool 60:2535-2542. ***** REFERENCES FOR N-OCCURRENCE NARRATIVE ONLY ***** 01 Starnes, L.B. and A.E. Bogan. 1982. Unionid mollusca (Bivalvia) from Little South Fork Cumberland River, with ecological and nomenclatural notes. Brimleyana 8:101-119. 02 Clarke, A.H. 1981. Determination of the precise geographical areas occupied by four endangered species of freshwater mollusks. Final Rep., U.S. Fish and Wildlife Service. 226 pp. 03 Bogan, A.E. and P.W. Parmalee. 1983. Tennessee's rare wildlife volume II: the mollusks. Tenn. Wildl. Resour. Agency, Tenn. Dep. Conserv., and Tenn. Heritage Prog., Univ. Tenn., Knoxville, TN. 123 pp. 04 U.S. Fish and Wildlife Service. 1983. Technical/Agency Draft Recovery Plan for the Cumberland Bean Pearly Mussel Villosa Trabalis (Conrad, 1834). U.S. Fish and Wildlife Service, Region 4, Atlanta, GA. 53 pp. 05 Harker, D.F., M.L. Warren, K.E. Camburn, S. Call, G.T. Fallo, and P. Wigley. 1980. Aquatic biota and water quality survey of the upper Cumberland River basin. Kent. Nat. Preserv. Comm. Tech. Rep. Vol. 1,2. 679 pp. 06 Blankenship, S. and D.R. Crockett. 1972. Changes in the freshwater mussel fauna of the Rockcastle River at Livingston, Kentucky. Trans. Kent. Acad. Sci. 33:37-39. 07 DiStefano, R. 1984. Freshwater mussels (Bivalvia:Unionidae) of Horselick Creek, Rockcastle River, Kentucky. Nautilus 98:110-113. 08 Hinkley, A.A. 1906. Some shells of Mississippi and Alabama. Nautilus 20:34-36,40-44,52-55. 09 Ortmann, A.E. 1918. The nayades (freshwater mussels) of the upper Tennessee drainage with notes on synonymy and distribution. Proc. Am. Phil. Soc., Phila. 57:521-626. 10 Ortmann, A.E. 1925. The naiad fauna of the Tennessee River system below Walden Gorge. Am. Midl. Nat. 9:321-372. 11 Wilson, C.B. and H.W. Clark. 1914. The mussels of the Cumberland River and its tributaries. Bur. Fish. Doc. 781:1-63. 12 Ortmann, A.E. 1912. Notes upon the families and genera of the naiades. Ann. Carnegie Mus. 8:222-365. 13 Neel, J.K. and W.R. Allen. 1964. The mussel fauna of the upper Cumberland Basin before its impoundment. Malacologia 1:417-459. 14 Bakaletz, S. February 10, 1986. [Letter to R.K. Robinson, U.S. Fish and Wildlife Service, Wildlife Permit Office]. References - 2