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1. Gooch, C.H., W.J. Pardue and D.C. Wade. 1979. Recent mollusk
investigations on the Tennessee River, 1978. Tennessee Valley
Authority, Water Quality and Ecology Branch, 126 pp.
2. Ortmann, A.E. 1925. The naiad fauna of the Tennessee River
system below Walden Gorge. The American Midland Naturalist,
9:321-372.
3. Richardson, T.D. 1993. Colonization of Tennessee River bivalves
by the invading zebra mussel, Dreissena polymorpha
(Pallas): final report for FY 1993, 38 pp.
4. Scruggs, G.D. 1960. Status of freshwater mussel stocks in the
Tennessee River. U.S. Fish and Wildlife Service, Special
Scientific Report. Fisheries. 370:1-40.
5. Stansbery, D.H. 1964. The Mussel (Muscle) Shoals of the
Tennessee River revisited. Annual Reports for 1964 of the American
Malacological Union: 25-98.
6. Van der Schalie, H. 1931. Additional notes on the naiades
(fresh-water mussels) of the lower Tennessee River. The American
Midland Naturalist, 22: 452-457.
Obovaria retusa: Confirmation of an extant population in the upper Green River, Kentucky
Robert S. Butler, Ronald R. Cicerello, and Ellis L. Laudermilk
U.S. Fish and Wildlife Service
160 Zillicoa Street
Asheville, NC 28801 (RSB)
and
Kentucky State Nature Preserves Commission
801 Schenkel Lane
Frankfort, KY 40601 (RRC & ELL)
Obovaria retusa (Lamarck, 1819) was described from the Ohio River at Cincinnati. Historically, it occurred in large river shoals throughout the Ohio River basin. Widespread population losses from habitat alteration led to its Federal listing as endangered in 1989. Only four populations remain: two each in Kentucky and Tennessee. According to the 1991 recovery plan, it is doubtful that any of them are experiencing successful reproduction and recruitment.
The upper Green River harbors one of the few populations of this critically endangered species. Obovaria retusa was first collected from the Green River at Mammoth Cave by R.E. Call (ca. 1900). The 34+ specimens Call collected (Cicerello & Hannan 1990), coupled with Ortmann's (1926) assertion that it was "not rare" at a nearby site. would seem to indicate that it was relatively common over 75 years ago. Although several freshly dead specimens have been reported since, the last verified live specimens were collected in the 1960's.
The Kentucky State Nature Preserves Commission (KSNPC) is conducting an assessment of the mussel populations in the Green River between Green River Reservoir and Mammoth Cave National Park (MCNP) in conjunction with a riparian habitat stress analysis and impending watershed protection effort by the Kentucky Chapter of The Nature Conservancy. In September 1997, KSNPC discovered a live specimen of Obovaria retusa completely exposed in a shallow gravel shoal upstream of MCNP. After the specimen was measured (63 mm), aged (16+ years), and photographed, it was returned to the substrate. Two other federally endangered species, Cyprogenia stegaria (Rafinesque, 1820) and Pleurobema plenum (Lea, 1840), were found during the recent assessment. Several specimens of C. stegaria were found live at several sites in the project area, while a single specimen of P. plenum was found live in Green County, which represents the upstream-most record for this globally rare species.
There are records for 71 species from the Green River system (Cicerello & Hannan 1990), including 59 species in the project area. Thirty-four live or freshly-dead species were located this year, 17 of which were represented by at least one specimen deemed a juvenile or sub-adult. An additional six species were found only as weathered or subfossil shells. This information indicates that the Green River continues to harbor a relatively healthy and diverse mussel fauna. Seven federally listed mussel species and 14 other species considered rare in Kentucky are known from the project area underlying the importance of the upper Green River as a mussel refugium.
Ortmann, A.E. 1926. The naiades of the Green River drainage in Kentucky. Annals of the Carnegie Museum 17:167-188.
Report: Missisquoi National Wildlife Refuge Native Mussel Quarantine Facility - 1997
Authors: Madeleine Lyttle and Megan Gibson
Address: Lake Champlain Fish and Wildlife Resources Office
U.S. Fish and Wildlife Service
11 Lincoln Street
Essex Junction, VT 05452
Numbers: Phone: (802) 951-6313 Fax: (802) 951-6315
E-mail: R5FFA_LCFWRO@FWS.GOV
The Lake Champlain Native Mussel Working Group identified Lewis Creek Delta, located on the Vermont side of Lake Champlain, as an area with a unique native mussel population. The Delta is highly colonized by zebra mussels (Dreissena polymorpha). This document summarizes removal and quarantine of several rare species from Lewis Creek and provides information on the quarantine results.
The quarantine facility, located on the Missisquoi NWR, consists of a 17x13.5 ft. fenced-in area large enough to hold a holding tank, three drainage barrels, and any periphery equipment needed for the project. The five foot diameter, 12" deep tank was equipped with a small fountain aerator. The water used in the quarantine was taken from the Missisquoi River.
On July 1, 1997, with a crew of 11 people, rare native mussels were recovered from the Lewis Creek Delta. The native mussels were cleaned three times - on the boat, before loading them into the truck, and when they arrived at the quarantine facility. The mussels collected were: Leptodea fragilis (62), Pyganodon grandis (2), Potamilus alatus (144), Lampsilis ovata (3), and Alasmidonta undulata (14).
Over the next month, the mussels were inspected weekly for five weeks. The water was changed in conjunction with the inspections. Periodically, the tank water was drained through a filter and examined for any evidence of zebra mussel veligers. The water temperature in the holding tank was maintained at approximately 21oC to promote the growth of zebra mussels and help sustain the native mussels. Additionally, algae, cultured by the Vermont Department of Environmental Conservation, was regularly added to the tank.
No adult zebra mussels or veligers were found on the native mussels, or in the water samples taken from the tank drainage. However, some mortalities did occur. Of the 225 collected, 16 died while in quarantine.
On August 11, 1997, biologists from the U.S. Fish and Wildlife Service and the Vermont Department of Environmental Conservation returned the native mussels to Lewis Creek, above the zebra mussel infested delta. These sections were selected because the mussels could be easily monitored and the areas have a low potential for zebra mussel infestation. The mussels will be monitored in Spring 1998.
University of Alabama's Malacological Research
Chuck Lydeard, Asst. Professor
University of Alabama, Dept. Biological Sciences
Box 870345
Tuscaloosa, AL 35487
Phone: 205-348-1792
FAX: 205-348-6460
email: clydeard@biology.as.ua.edu
Ph.D. Students:
Wallace Holznagel
Russ Minton
Kevin Roe
Malacology-Related Publications:
Lydeard, C., and R.L. Mayden. 1995. A diverse and endangered aquatic ecosystem of the Southeast United States. Conservation Biology 9:800-805.
Lydeard, C. 1996. U.S. Biodiversity Status Report. Conservation Biology 10:1480-1482.
Lydeard, C., M. Mulvey, and G.M. Davis. 1996. Molecular systematics and evolution of reproductive traits of North American freshwater unionacean mussels (Mollusca:Bivalvia) as inferred from 16S rRNA gene sequences. Philosophical Transactions of the Royal Society of London Series B 351:1593-1603.
Lydeard, C., W.E. Holznagel, J. Garner, P. Hartfield, and J. Malcolm Pierson. 1997. A molecular phylogeny of Mobile River drainage basin pleurocerid snails (Caenogastropoda: Cerithioidea). Molecular Phylogenetics and Evolution 7:117-128.
Mulvey, M., C. Lydeard, D.L. Pyer, K.M. Hicks, J.C. Brim-Box, J.D. Williams, and R.S. Butler. 1997. Conservation genetics of North American freshwater mussels Amblema and Megalonaias. Conservation Biology 11:868-878.
Roe, K.J., A.M. Simons, and P. Hartfield. 1997. Identification of a fish host of the inflated heelsplitter Potamilus inflatus (Bivalvia: Unionidae) with a description of its glochidium. American Midland Naturalist 138:48-54.
Spiny Riversnail (Io fluvialis)
Steven Ahlstedt
U. S. Geological Survey
1820 Midpark Drive
Knoxville, TN 37921
PH: (423) 545-4140 Ext. 17
FAX: (423) 545-4496
Spiny riversnail reintroduction sites in the lower French Broad (Campbell Island) and upper Holston River (Surgoinsville) were searched in July 1997 for adult survival of specimens transplanted in 1996. Thirty-three live specimens were found in the French Broad and none were found in the Holston. No reason could be given for the disappearance of the snails in the Holston because other pleurocerid riversnails were abundant.
During August 1997, 600 more measured and marked spiny riversnails were reintroduced into the French Broad and Holston River at the same 1996 locations. Both sites will be evaluated in FY 1998 for adult survival. Evidence of reproduction is a long-term process and may be 4-6 years away from determining if transplants were successful. The disappearance of the snails in the Holston is not unusual because they could have been distributed downstream during high flows and/or the small number transplanted makes finding them difficult.
Funding for this project was provided by Dick Biggins, USFWS, Endangered Species Field Office, Asheville, North Carolina. Help in collecting specimens was provided by students of Dr. Jim Lazer, Tenn. Tech University, Fisheries Coop Unit, TVA, TWRA, and TNC.
First Release of Cultured Juvenile Mussels in Tennessee
Author(s): Richard J. Neves
Address: Virginia Cooperative Fish & Wildlife Research Unit
Biological Resources Division
Department of Fisheries and Wildlife Sciences
Virginia Polytechnic Institute and State University
Blacksburg, VA 24061-0321
Phone Number(s): (540) 231-5927
Fax Number(s): (540) 231-7580
Email: mussel@vt.edu
The first release of juvenile freshwater mussels, cultured at the Mussel Research Center at Virginia Tech, occurred on September 24, 1997. A total of 52 endangered tan riffleshells (Epioblasma f. walkeri) and 360 wavy-rayed lampmussels (Lampsilis fasciola) were released immediately upstream of the Route 68 crossing of the Hiawassee River, within Cherokee National Forest, North Carolina. Other participants in this first release included Ed Stiles and Leigh McDougal (USFS), Janice Cox (TVA), Dick Biggins (FWS), and Steve Ahlstedt (USGS). The tan riffleshells were 2-3 months old and less than 1 mm in length. The wavy-raved lampmussels were 6-12 months old and ranged from 2-5 mm in length. These mussels were surplus from culture experiments completed in summer 1997. The State of Tennessee has recently funded a project for us to produce juvenile mussels of a suite of species for release into historic habitats within the state. Cooperators in this project include the Tennessee Wildlife Resources Agency (TWRA), U.S. Fish and Wildlife Service, and Virginia Cooperative Fish and Wildlife Research Unit. A listing of potential release sites for each species is being prepared for TWRA approval.
Cyclonaias tuberculata glochidia transform on catfish barbels
Mark Hove and Jennifer Kurth
University of Minnesota
1980 Folwell Avenue
Saint Paul, MN 55108
(612) 624-3019
email addresses: Mark.Hove@fw.umn.edu
kurt0007@gold.tc.umn.edu
Ictalurids probably encounter glochidia as they search for food on the river bed when mussels are releasing their young. A preliminary study suggests Cyclonaias tuberculata glochidia can transform on the barbels of channel catfish. Host suitability teals were conducted this spring using methods similar to those described in Neves et al. ( 1985). Juvenile C. tuberculata were collected from four of seven Ictalurids tested (Tables 1 and 2). One group of channel catfish had only their lower barbels exposed to C. tuberculata glochidia. Although this trial ended prematurely due to an outbreak of Ich, we plan to repeat barbel infestation tests in the future.
Table 1. Attachment period of unsuitable hosts for Cyclonaias tuberculata glochidia.
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Table 2. Fish species that facilitated Cyclonaias tuberculata glochidia metamorphosis.
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Neves, R.J., L.R. Weaver, and A.V. Zale. 1985. An evaluation of fish host suitability for glochidia of Villosa vanuxemi and V. nebulosa (Pelecypoda: Unionidae). American Midland Naturalist 113( 1): 1 3-19.
Northern Minnesota river holds three state-listed mussels
Mark Hove, Shawn Strong, Amy Jacobson, Johanna Schussler. and
Valeri Kurth
University of Minnesota
1980 Folwell Avenue
Saint Paul, MN 55108
(612) 624-3019
(note new) email address: Mark.Hove@fw.umn.edu
The mussel assemblage of the Lake of the Woods watershed in northern Minnesota is among the least studied unionoid faunas in the state (Graf 1997). The Big Fork River, a subdrainage in the watershed, flows north over rolling moraines, across the flat bed of Glacial Lake Agassiz, to the Rainy River; Minnesota's border with Canada. Much of the Big Fork River watershed is relatively pristine. Most of the land is covered by second growth aspen and pine forests, and a small number of ranches (Waters 1977).
Twenty-five sites were surveyed in the Big Fork River basin.
Lampsilis siliquoidea, Pyganodon grandis, and L. cardium
were regularly found throughout the watershed. Lasmigona
compressa was found in the lower two-thirds of the basin.
Utterbackia imbecillis, Anodontoides Jerussacianus, Lasmigona
complanata, Strophitus undulatus, and Ligumia recta had
scattered distributions. L. costata was represented by a
single valve from a headwater tributary. Lasmigona compressa, L.
costata, and Ligumia recta are listed as special concern
species in Minnesota. Mussel densities ranged between 0-32
mussels/m2 (Figure 1).
Figure 1. Mussel densities in the Big Fork River, Minnesota.
During the survey we observed an interesting color variant of Ligumia recta. Most L. recta in the St. Croix and upper Mississippi rivers have gray and black mantles with white-tipped papillae. However, two displaying L recta in the Big Fork River had a much lighter, yellow-gray mantle. These mussels, like other brooding L recta we've witnessed, were lying out on top of the river bed occasionally waving their mantles.
This survey was made possible with support from: the Legislative Comm. on Minnesota Resources, Chantel Cook and Richard Buech of the National Park Service, Jay Hatch, Joanne Iskerka, Cindy Lee, and Susan Weller of the Bell Museum of Natural History, Dan Hornbach of Macalester College, and Anne Kapuscinski of the University of Minnesota.
Graf, D. L. 1997. Distribution of unionoid (Bivalvia) faunas in Minnesota, USA. The Nautilus 110(2): 45-54.
Waters, T. F. 1977. The streams and rivers of Minnesota. University of Minnesota Press, Minneapolis. Minnesota. 373 pp.
1997 Mississippi River Research Consortium abstracts
Mark Hove
University of Minnesota
1980 Folwell Avenue
Saint Paul, MN 55108
(612) 624-3019
email address: Mark.Hove@fw.umn.edu
The following abstracts were selected from presentations made at the 29th annual meeting of the Mississippi River Research Consortium (April 24-25, 1997). The next meeting will take place at LaCrosse, WI on April 23-24, 1998.
SECONDARY PRODUCTION OF HYALELLA AZTECA AS INFLUENCED BY DREISSENA POLYMORPHA, LARVAL FISH, AND NUTRIENTS.
Kari Marley1*, W.B. Richardson1,2, and M.B.
Sandheinrich1 1Dept. of Biology and
Microbiology, University of Wisconsin, La Crosse, La Crosse, WI
54601
2Upper Mississippi Science Center, U.S. Geological Survey,
La Crosse, WI 54601
*Research supported by Wisconsin Seagrant.
Beds of zebra mussels typically contain greater densities of benthic macroinvertebrates than adjacent areas, but little data exists on the effect of zebra mussels on benthic secondary production. We tested the hypotheses that (1) benthic production would increase where zebra mussels and elevated nutrients were present, but decrease in the presence of a vertebrate predator; and (2) the presence of both zebra mussels and elevated nutrients would offset the negative effects of fish on benthic production. In a 35-d mesocosm experiment we manipulated the presence or absence of (1) Dreissena (1500/m2), (2) larval fathead minnows (Pimephales promelas: 250/m3), and (3) nutrients at 2x supply water concentrations (0.44 mg/L N and 0.035 mg/L P). These factors were cross-classified, resulting in 8 treatment combinations; N=3. Benthic samples were collected weekly, and the amphipodHyalella azteca removed from the samples to estimate secondary production (cohort growth increment summation method). We also measured chlorophyll concentration, zooplankton density, and fish diet and growth. Production of Hyalella increased in the presence of zebra mussels, nutrients, and larval fish in comparison to controls, however production decreased in the combined treatment of zebra mussels and larval fish. The results suggest that (1) secondary production is elevated in the presence of zebra mussels, and (2) because zebra mussels effectively outcompete the larval fish for zooplankton prey, the fish are forced to feed on the benthos more intensely than when zebra mussels were not present.
EFFECTS OF DREISSENA POLYMORPHA (PALLAS 1771), ZEBRA MUSSEL, ON 1996 UNIONID MOLLUSK TRANSLOCATION PROCEDURES: MISSISSIPPI RIVER MILE 697.5, HWY 14/16/61, CASS STREET BRIDGE, LA CROSSE, WI.
Marian E. Havlik
Malacological Consultants, 1603 Mississippi Street, La Crosse, WI
54601-4969.
E-mail: havlikme@aol.com
In July and August 1996, prior to routine riprap placement around three bridge piers, 12698 unionids (27 species) including five endangered Lampsilis higginsi (Lea 1857), and 580 other Wisconsin special status unionids, such as 39 Ellipsaria lineolata (Rafinesque 1820), 29 Arcidens confragosus (Say 1829), and 234 Pleurobema sintoxia (Rafinesque 1820) were translocated, mostly from about 900 m2 around each of two piers. Densities and number of species per pier were: Pier 6, 2.81/m2 (22 species); Pier 7, 0.07/m2 (12 species); and Pier 8, 10.65/m2 (27 species). The mean density was 4.65 mussels/m2. This unionid translocation was probably the first to have been conducted in an area seriously impacted by Dreissena polymorpha, 6-44 mm long. Some unionids, mainly from sand substrata, were devoid of this exotic, although many showed evidence of previous D. polymorpha attachment (byssal threads). At Piers 6 and 7 there were a small number of D. polymorpha on most unionids, but at Pier 8, on the left descending bank and 320 m downstream of a barge facility, the river substrata was blanketed with zebra mussels 25-75 mm deep, and up to 120 or more adults on 80% of the unionids. Depths at Pier 8 were 6-9 m with very strong currents, and a cobble, gravel, and sand substrata. The number of D. polymorpha greatly slowed unionid collection by experienced divers. Many unionids were nearly covered with D. polymorpha, but few appeared to have been killed by this exotic. The saving factor may be the strong current at Pier 8, on outside of a large, river bend. Processing time was doubled because visible D. polymorpha were hand stripped, like shucking popcorn, before unionids were marked or numbered on each lower anterior valve. A local waste management company required D. polymorpha to be bagged, and advance disposal notice given to facilitate immediate landfill burial. The first records for La Crosse since 1907, and for the Upper Mississippi River since 1930, included three Alasmidonta marginata Say 1818 and four Lasmigona costata (Rafinesque 1820). Depths of 6-9 m were probably records for these two generally small stream species. Amblema p. plicata (Say 1817) was 39.75% of the fauna. The most suitable translocation area for special status unionids was 4 miles upstream. A nearby site was used as the translocation area for some common species. Several species reported alive nearby by Havlik (1983) were not found, including Anodonta suborbiculata Say 1831, however the habitat was not typical for this species. All special status specimens appeared to be doing well on 6 October 1996, except that #131, Ligumia recta (Lamarck 1819) (160 mm long) was found dead with about 50 - 5 mm long juvenile D. polymorpha attached to this shell. These small D. polymorpha represented the 1996 August-September cohort.
CHANGES IN DENSITY AND SIZE DEMOGRAPHY OF THREERIDGE MUSSELS (Amblema plicata plicata) IN LAKE PEPIN, MINNESOTA, AND WISCONSIN
Rick Alan Hart1 and Mike Davis2
1North Dakota State University, Department of Zoology,
Fargo, ND 58105. 701/231-7030, rhart@prairie.nodak.edu
2Minnesota Department of Natural Resources, Ecological
Services Section, Lake City, MN 55041. 612/345-3331
Density and size demography of unionid mussel populations were quantitatively sampled at several mussel beds in Lake Pepin, beginning in 1990. Densities of the commercially harvested threeridge mussel, Amblema plicata plicata (Say, 1817), declined at 5 of the 7 mussel beds sampled. The most dramatic decline occurred at the Hok Si La, MN, bed where average densities ofA. p. plicata equaled 21.7/m2 during 1993, declining to 6.0/m2 in 1995 and 5.0/m2 in 1996 (F=8.820, P=0.0001). Densities of non-harvested mussel species increased or remained stable at all seven beds. Average shell height ofA. p. plicata significantly decreased at 4 beds, remained stable at 2, and increased at 1. These data implicate commercial harvesting as a contributing factor in the decline of this mussel species. During this study, zebra mussels, Dreissena polymorpha, became established in Lake Pepin. The greatest density of zebra mussels was found at the King's Coulee bed in 1995 (1750/m2), decreasing to 971/m2 in 1996 (T=2.366, P=0.021). Although densities of zebra mussels decreased at this bed, infestations of zebra mussels uponA. p. plicata did not. The average number of live zebra mussels per liveA. p. plicata equalled 44 in 1995 and 48 in 1996. With the large percentage of infested A. p. plicata at the King's Coulee bed in 1996 (91%), an increase in zebra mussel induced mortality could soon become evident. While zebra mussels can not be controlled by resource agencies, the impacts of commercial harvesting can. An attempt is being made to model safe levels of harvesting, thus ensuring a sustainable yield ofA. p. plicata.
SUITABLE FISH HOSTS FOR GLOCHIDIA OF THREE FRESHWATER MUSSELS: SQUAWFOOT, ELLIPSE, AND SNUFFBOX
Katie Rose Hillegass and Mark C. Hove
University of Minnesota, Department of Fisheries and Wildlife, St.
Paul, MN 55108.
Of 297 freshwater mussel species living in North America, 213 are either endangered, threatened, or of special concern. The identification of fish hosts is listed in the National Strategy for Freshwater Mussel Conservation as an urgent research objective. We conducted laboratory studies to determine suitable fish hosts for three species of freshwater mussels: squawfoot (Strophitus undulatus), ellipse (Venustaconcha ellipsiformis), and snuffbox (Epioblasma triquetra). Various fish species were exposed to mussel larvae via artificial infestation. A fish was considered a suitable host when larval metamorphosis to the juvenile stage was observed. Juvenile squawfoot were collected from five of seven species tested: largemouth bass, green sunfish, black bullheads, bluegills, and yellow perch. Of nine fish species exposed to ellipse glochidia, only blackside darters were suitable hosts. Snuffbox glochidia metamorphosed on logperch and blackside darters. Host requirements for squawfoot glochidia appeared to be quite general, whereas ellipse glochidia were more selective. Species-specific molecular markers are being developed for use in the identification of glochidia collected from naturally infested fish.
EFFECT OF INCREASED ZEBRA MUSSEL DENSITIES ON MACROINVERTEBRATE COMMUNITY STRUCTURE OF SNAGS IN THE UPPER MISSISSIPPI RIVER
Todd R. Birkle and Michael D. Delong
Large River Studies Center, Biology Dept., Winona State University,Winona,
MN 55987
Studies of the zebra mussel Dreissena polymorpha, in Europe suggest that we can expect this exotic species to reach an equilibrium with native invertebrates in the upper Mississippi River, but at a cost. Some documented on native invertebrates include a decrease in the availability of hard substrata and lower phytoplankton abundance. We collected samples of woody debris (snags) from backwater and main channel habitats of the upper Mississippi River to determine if increasing zebra mussel densities were affecting the density and diversity of native benthic invertebrates. Our data were compared to those of a similar study conducted in 1993, prior to any substantial snag colonization by zebra mussels. Samples were collected from two sites (near RK 1155 and 1172) in September 1996 using a DTH snag sampler. Zebra mussel densities on snags were low in both the main channel and backwaters in 1993. By 1996, densities in excess of 200 individuals/m2 were not uncommon. Of particular note were the densities observed in backwaters, which were in the same general locations were zebra mussels were first observed in 1993. The invertebrate community in 1996 was characterized by an abundance of Chironomidae and small to marked reductions in the abundance of heptageniid mayflies and several groups of Trichoptera. Comparison of data from 1993 to 1996 suggest that the same trends observed in other areas, including the Great Lakes, will hold true for the upper Mississippi River. Benthic invertebrates which can use zebra mussel byssus and pseudofeces as habitat and possible food source, respectively, (e.g., Chironomidae) will take advantage of the new conditions, whereas, organisms competing with mussels for space (e.g., some Trichoptera and Ephemeroptera) will see a reduction in overall densities.
USE OF A DYNAMIC POPULATION MODEL TO EVALUATE MANAGEMENT STRATEGIES FOR NATIVE MUSSELS.
K. Douglas Blodgett 1, James A. Stoeckel 2,
Scott D. Whitney 1, and Richard E. Sparks2
1 LTRMP Field Station, Illinois Natural History Survey, 704 N.
Schrader Ave., Havana, IL 62644
2 Forbes Biological Station, Illinois Natural History
Survey, P.O. Box 590, Havana, IL
62644
Currently, management of native mussels is hampered by our inability to quantitatively assess the impacts of natural and anthropomorphic stresses, such as natural and harvest mortality, on populations of this economically and ecologically important resource. Sound science-based management requires a tool that combines data on current populations with knowledge of population dynamics to predict future conditions under various management scenarios. Using Stella II software running on a personal computer, we developed a dynamic, single-species population model that can be used as one tool to help evaluate effects of different management strategies on native mussel populations. Input parameters include initial mussel density (number per m2), age-frequency distribution, growth rate, age or size at maturity, and age-specific mortality rates. In our model, recruitment is density dependent and can be calculated either as a percentage of the reproductive population or by using a submodel which incorporates fecundity rate, sex ratio, density-dependent fertilization rate, and glochidial attachment, transformation, and survival rates. The primary output from the model is live mussel standing stocks (numbers per m2) of different age classes over time. In our model, harvest can be regulated by various management strategies including minimum shell height (the current management practice in Upper Mississippi River [UMR] states), harvest allowed only when a specific mussel density is exceeded, maximum harvest rate (number per m2), assorted closure regimes, or combinations of these. Model outputs include annual and cumulative harvest (numbers and/or pounds per m2). The model also can use mussel weight- or size-dependent price estimates to calculate dollar values for standing stocks and annual, mean, and cumulative harvest. We used data for the threeridge mussel (Amblema plicata) collected from Reach 15 of the UMR near Rock Island, IL, and compared 100-year simulation runs of the model using two types of regulation strategy. The first strategy produced a set of five runs with harvest regulated by minimum harvest heights of 1.50, 1.90, 2.50, 2.75, and 3.00 inches. The second strategy used a constant minimum harvest height of 2.75 inches (the limit in most UMR states) and five different minimum harvest densities, allowing harvest of legal-size mussels only when their densities exceeded 0.5, 1.0, 2.5, 5.0, or 10.0 per m2. Using the minimum harvest height regulations alone, the total 100-year harvest ranged from 5.3 to 5.8 live mussels harvested per m2, and the 100-year mean mussel density (standing stock) ranged from 0.8 to 2.8 mussels per m2. Regulation by minimum harvest density resulted in total 100-year harvests from 4.0 to 12.9 mussels per m2 and mean densities of 1.5 to 12.8 mussels per m2. Use of this or similar models should aid in the development and implementation of improved management strategies to protect or even enhance our native mussel resources (e.g., provide higher standing stocks) while contributing to a sustained harvest at an increased rate and/or value.
BELL MUSEUM OF NATURAL HISTORY: ORGANIZING MINNESOTA'S FRESHWATER MOLLUSKS INTO A GIS-COMPATIBLE DATABASE
Mark Hove1, Mark Nelson2, Susan
Weller1, Richard Buech2, and Robert
Bright1
1 James Ford Bell Museum of Natural History, University of
Minnesota, St. Paul, MN 55108
2 US Forest Service, North Central Forest Experiment
Station, St. Paul, MN 55108
The Bell Museum of Natural History is Minnesota's repository for freshwater mollusks. The museum collection includes 5737 lots; 5146 from states surrounding and including Minnesota. Freshwater bivalves constitute 92% of the collection, including 250 lots collected before 1910. Specimens collected beyond Minnesota and adjacent states include freshwater mussels from 22 states (n=188 lots) and 2 other countries (n=2 lots), and snails from 31 states (n=369 lots) and 11 other countries (n=32 lots). Most of these collection records are entered into a computer database (Filemaker Pro customized by Daniel Graf). In addition to active acquisition of specimens, we are expanding our computer database on Minnesota mollusks to include a review of species locality data collected from journal articles and federal reports. In collaboration with the US Forest Service, we are in the process of converting our literature database to a GIS-friendly format. With GIS capability, it is possible to visualize collection needs, changes in fauna over time, and the correlation of mussel species' distributions with geoclimatic and vegetation records. This database and GIS capability will provide distribution information in an accessible format to resource managers, and facilitate efforts to identify and conserve rare species.
CURRENT STATUS OF THE BENTHIC COMMUNITY OF POOL 19, MISSISSIPPI RIVER.
Robert Kennedy, Richard V. Anderson, and Melissa Morgan
Dept. of Biological Sciences, Western Illinois University, Macomb, IL
61455.
Benthic samples have been collected at standard sites in Pool 19, Mississippi River for over 25 years. During this period benthic density and diversity has fluctuated substantially. During this period sedimentation, extreme droughts and floods have also occurred. When evaluating the benthic data in terms of habitat changes brought about by these extreme events some specific relationships are apparent. Burrowing forms of benthic organisms occur in the channel border habitat of most of the lower reach of Pool 19. Dense populations (1-10 X 104/m2) of some of these burrowing benthic organisms, particularly fingernail clams (Musculium) and burrowing mayflies (Hexagenia), occur in soft sediments in association with vegetation but not directly in vegetated habitats. When areas of soft substrate develop vegetation, such as during droughts or when sedimentation decreases water depths, populations of these benthic organisms are greatly reduced (>100/m2). However, if flooding removes the vegetation the Musculium, Hexageniadominated benthic community is quickly reestablished an appears to persist until dense stands of aquatic macrophytes again develop. The aquatic macrophytes produce unsuitable conditions in the substrate below the plants but provide a good food source in adjacent benthic habitat. Once sedimentation rates stabilize in an impounded reach of a navigation pool, density of fingernail clams and burrowing mayflies may fluctuate in relation to flooding or drought events of sufficient magnitude to alter patterns of aquatic macrophyte development.
EFFECTS OF FOOD LIMITATION BY ZEBRA MUSSELS (DREISSENA POLYMORPHA) AND FISH PREDATION ON LIFE HISTORY CHARACTERISTICS OF DAPHNIA PULEX.
Michael Kinsella1, Mark B. Sandheinrich1,
and William B. Richardson2
1River Studies Center, Department of Biology &
Microbiology, University of Wisconsin-La Crosse, La Crosse, WI
54601.
2 U.S. Geological Survey, Upper Mississippi Science
Center, La Crosse, WI 54602
Life history strategies of organisms have evolved to maximize the fitness of the individual and may be influenced by the environment of the species. Competition and predation are interspecific interactions that may alter life history characteristics. Zooplankton (e.g., Daphnia spp.) subject to intense fish predation, generally shunt energetic resources into reproduction rather than growth and produce large clutches of small eggs at an early age. In contrast, Daphnia subject to invertebrate predation and competing for food with other filter feeders grow quickly, delay reproduction, and produce small clutches with large eggs. Since its introduction into the Laurentian Great Lakes in 1986, the zebra mussel (Dreissena polymorpha)has spread throughout the Great Lakes region and now occurs within the upper Mississippi River. Although several studies have demonstrated that zebra mussels effectively filter phytoplankton and compete with zooplankton, no studies have assessed the effects of this exotic mussel on the life history characteristics of native zooplankton. The objectives of this mesocosm study were to determine the effect of resource depression due to filter-feeding zebra mussels and the effect of fish predation on life history characteristics of Daphnia pulex. A two factor cross-classified experimental design was used to assess the main and interactive effecs of the presence or absence of zebra musssels and fish. There were four treatment combinations, with three units per treatment. Intrinsic rate of increase, instantaneous birth and death rates, clutch size, size at first reproduction, and population size of the Daphnia were estimated weekly during the eight-week study. Preliminary results suggest that zebra mussels increased clutch size and increased death rates. Fish increased death rates and decreased population size and size at first reproduction of Daphnia. When co-occurring, zebra mussels and fish decreased population size and increased the average clutch size of Daphnia. These results suggest that zebra mussels may alter zooplankton life history characteristics and depress population growth in Daphnia.
MODIFICATION OF THE ALKALINE DIGESTION AND PHENOL-SULFURIC ACID METHOD FOR THE DETERMINATION OF GLYCOGEN IN AQUATIC INVERTEBRATES.
Emy M. Monroe1, Teresa J. Naimo1, and Ron G.
Rada2 1
U.S. Geological Survey, Biological Resources Division, Upper Mississippi
Science Center, La Crosse, WI 54602 and
2University of Wisconsin-La Crosse, River Studies Center, La
Crosse, WI 54601.
The amount of glycogen in animal tissue is often used as an indicator of energetic status of the organism. In long-lived invertebrates, such as unionid mussels, where short-term measures of growth are unrealistic, repeated analysis of glycogen content may provide a valuable tool to assess changes in physiological condition of individuals. Recently developed biopsy techniques make it possible to repeatedly remove from an individual organism small tissue samples (10-30 mg) that can be analyzed for constituents such as glycogen. Methods for measuring glycogen, however, are numerous, and the method detection limits are usually unreported or unknown. Our objectives were to modify the alkaline digestion and phenol-sulfuric acid spectrophotometric method for the analysis of glycogen in small (10 mg) samples and to determine the accuracy and method detection limit of the modified method. Based on 10 batches of analyses, the method is rapid, has high precision (mean RSD of triplicate analyses=9.4%), low bias (mean percent recovery of known additions=109%), and has a method detection limit of 0.02 mg glycogen. Thus, the modified method can accurately measure glycogen in small tissue samples, allowing the repeated measurement of glycogen in individual organisms over time.
SPATIAL AND TEMPORAL VARIABILITY IN GLYCOGEN CONTENT IN HEXAGENIA MAYFLIES AND FINGERNAIL CLAMS IN THE UPPER MISSISSIPPI RIVER.
Teresa J. Naimo, Erika D. Damschen, and Emy M. Monroe
U.S. Geological Survey, Biological Resources Division, Upper
Mississippi Science Center, La Crosse, WI 54602.
Recently, physiological indicators of condition, such as glycogen concentration, have been used to assess the relative health of benthic invertebrates in laboratory studies. However, data on the spatial and temporal variability in glycogen concentration from field populations are lacking. We assessed the glycogen concentration in 5 male and 5 female mayflies (Hexagenia spp.) and 5 fingernail clams (Musculium transversum) obtained monthly (May-Oct.) from 4 sites in Navigation Pool 8 of the Upper Mississippi River in 1994 and 1995. In fingernail clams, glycogen concentration ranged from 0.3 to 51.8 mg/g wet weight (mean 11.8) and did not differ significantly between years, or among sites or months. In mayflies, glycogen concentration ranged from 1.1 to 14.0 mg/g wet weight (mean 4.9) and differed significantly among months (p=0.001), but not between sexes or years, or among sites. In mayflies, glycogen was highest in late spring and declined throughout the summer and fall. In both organisms, glycogen content (mg) was positively correlated with length and weight. These data suggest that the variability in glycogen concentration is driven by temporal, rather that spatial, patterns. Thus, glycogen concentration may be a useful indicator of physiological and reproductive condition in field and laboratory studies if temporal variation is accounted for.
CHARACTERIZATION OF DREISSENID MUSSELS FROM THE MISSISSIPPI RIVER USING SPECIFIC DNA MARKERS FROM MITOCHONDRIAL CYTOCHROME C OXIDASE.
Michael A. Romano, Angela D. Byers, Richard V. Anderson, and N. Carol Krumanocker Dept. of Biological Sciences, 1 University Circle, Western Illinois University, Macomb, IL 61455.
In a recent study of Dreissenid mussels in the Mississippi River, Krumanocker (1996) reported that, in addition to Dreissena polymorpha (zebra) and D. bugensis (quagga), Mytilopsis leucophaeata (dark false mussel) has become established in the Mississippi. Identification of the three purported taxa based upon morphology and electrophoretic studies of those specimens appeared to corroborate the identification of those species. In an attempt to confirm the presence of all three species, a different molecular technique has been utilized to establish whether the three species are present. Baldwin et al. (1996) utilized the Polymerase Chain Reaction (PCR) to amplify an approximately 710 bp fragment of the cytochrome c oxidase subunit I gene (COI0 from D. polymorpha, D. bugensis and M. leucophaeata. They demonstrated three very distinct restriction fragment lenght polymorphic (RFLP) patterns when the PCR product was digested with the restriction endonuclease NlaIV. We have successfully extracted DNA from all three of the morphologically identified Dreissenids and have amplified a DNA fragment utilizing the same set of PCR primers reported in Baldwin et al. (1996). The RFLP results of PCR product from all three morphological types will be presented.
FIVE YEARS OF MACROINVERTEBRATE SAMPLING ON THE UPPER MISSISSIPPI RIVER
Jennifer S. Sauer
Environmental Management Technical Center, 575 Lester Avenue,
Onalaska, WI 54650
The temporal variability in mayflies (Ephemeridae), fingernail clams (Sphaeriidae), and midges (Chironomidae) in six study reaches of the Upper Mississippi River System was examined. Spatial distribution also is discussed for these organisms along with the Asiatic clam, Corbicula fluminea, and the zebra mussel (Dreissena polymorpha). Sample allocation was based on a stratified random design which was based on aquatic area. No significant linear trends across years were determined in estimated mean number of organisms. However, the overall test for differences in intercepts among study reaches was statistically significant (P<0.05) for mayflies, fingernail clams, and midges. Overall, the impounded aquatic areas and silt/clay substrates tended to support higher numbers of the select macroinvertebrates.
PREDATION OF ZEBRA MUSSELS, DREISSENA POLYMORPHA, BY RIVERINE FISHES IN THE UPPER MISSISSIPPI RIVER
Renae B. Servaty and Michael D. Delong
Large River Studies Center and Biology Dept., Winona State
University, Winona, MN 55987.
Previous studies of zebra mussels, Dreissena polymorpha, in the upper Mississippi River have indicated that fish are actively feeding on this exotic species. Furthermore, these studies suggest that fish are selectively removing zebra mussels larger than 8-mm. The objective of this study was to analyze gut contents of fish to determine what fish are consuming zebra mussels and to verify size selectivity of mussels larger than 8-mm. Samples were taken by boat with an electroshocker along three 400-m transects from backwater and main channel shoreline habitats in Pool 6 of the upper Mississippi River. Fish were identified, weighed, measured, and the stomachs were examined for the presence of zebra mussel shells. Septum width and total length, when possible, were measured. A regression model was developed to estimate total length using septum length when damage to the shell made it impossible to measure the former. Several species of fish were found to consume zebra mussels. Major predators in the main channel included redhorse (Moxostoma spp.), carp (Cyprinus carpio), and freshwater drum (Aplodinotis grunniens). All three species were also found to consume zebra mussels in addition to bluegill (Lepomis macrochirus). Bluegill exhibited a preference for zebra mussels of 4 - 7 mm total length whereas other predators consumed zebra mussels most frequently of 5 - 20 mm total length. Fish predators in the main channel appeared to prefer zebra mussels > 6 mm. The results of this study suggest that differences in size preference exist between main channel and backwater habitats, with the composition of fish assemblages being a major factor. As a result, zebra mussel population dynamics may differ in main channel and backwater areas of the upper Mississippi River.
FRESHWATER BIVALVES OF TENNESSEE, in Press
Paul W. Parmalee, McClung Museum, University of Tennessee,
Knoxville, TN 37996 and
Arthur E. Bogan, North Carolina State Museum of Natural Sciences,
P.O. Box 29555, Raleigh, NC 27626
This volume presents basic biological information on freshwater bivalves of the family Unionidae in Tennessee, including shell structure, growth, development, general ecology, distribution (prehistoric and present), aboriginal and historic commercial utilization, and current status. The synonymy, general and Tennessee distribution, shell description, life history and ecology, and status are presented for each of the 129 native species reported from the state. A color plate showing two specimens of each species and a Tennessee distribution map with an insert map showing the total species distribution, accompanies the discussion of each mussel species.
This volume is being published by the University of Tennessee Press, Knoxville, Tennessee. The volume is expected to be published in Fall 1998. No price has been set at this time.
AGE AND SIZE STRUCTURE OF COMMERCIAL UNIONIDS, WITH EMPHASIS ON Megalonaias nervosa (Rafinesque 1820), UPPER MISSISSIPPI RIVER, REACH 9-19, LANSING - FORT MADISON, IOWA, JULY - SEPTEMBER, 1997.
HAVLIK, MARIAN E.
Malacological Consultants
603 Mississippi Street
La Crosse, WI 54601-4969
Phone/Fax: 608-782-7958
E-mail: havlikme@aol.com
In 1997 the Shell Exporters of America Inc. (SEA) began the most extensive survey ever done on commercial unionids. From 1 July-14 Sept. we sampled 8 Reaches (Pools) of the Mississippi River, Mile 663.0-386.0, Reaches 9-12, 14-16, 19, with emphasis on M. nervosa. Sites were identified by divers, the malacologist and clammer/buyer's experiences, and a Resource Inventory. I designed a modified 0.25 m2 Surber sampler with an attached mesh bag, a 15 m rope, and an inflatable buoy. 11 quads were made by Tennessee Shell, Camden, TN. One or 2 major and several minor sites were sampled in most Reaches. The Sylvan Slough Sanctuary, Moline, IL, was sampled in both Reaches 15 and 16. 252 random timed dives were done starting near shorelines; results are given as a CPU. If this was productive, we did quadrats (N = 692) in transects across the width of the unionid bed. Over 20,400 live and dead unionids were processed from 944 dive sites. Mean density of M. nervosa/Reach = 2.7-7.6/m2; quad densities ranged from 0.0-68.0/m2. 4800 living M. nervosa were measured and aged after being scrubbed with steel bristled paint stripping brushes to remove Dreissena polymorpha byssal debris. Few M. nervosa were fresh-dead from D. polymorpha. The youngest M. nervosa was 2 yrs (10 mm ht). The apparent lack of young M. nervosa reported in 1986 was not real as evidenced by large numbers of 10 to 13 year old age classes in 1997, apparently a response to the 1982-1986 Mississippi River die-off. In some areas 5-7 year age classes were well represented. Nearly all age classes were quite well represented from ages 5-early 20's. Age does not equal size. Growth varies from Reach to Reach, and within a bed, especially from upstream to downstream in the Mississippi. Growth rates generally increase further south, but Reach 9 (WI) also had good growth. The youngest commercial M. nervosa was 9 yrs, the oldest 38 yrs. In most Reaches 2.4-10.8% (mean 7.8%) of a bed is of commercial size (101.6 mm). The highest number of legal sized unionids were in Sylvan Slough (18.5%) indicating little illegal harvest; sanctuary status is working. 2200 dead M. nervosa were measured for height. The smallest and largest Amblema p. plicata (Say 1817) from each sample were also measured and aged. Few malacologists have ever had the opportunity to observe unionid age and growth in such a long reach of a large river.
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A UNIONID MOLLUSK SURVEY IN AN UPPER MISSISSIPPI RIVER SIDE CHANNEL NEAR GREY CLOUD ISLAND, MILE 820.0 - 821.5, COTTAGE GROVE, MN.
HAVLIK, MARIAN E.
Malacological Consultants
603 Mississippi Street
La Crosse, WI 54601-4969
Phone/Fax: 608-782-7958
E-mail: havlikme@aol.com
No federally endangered unionids were found at the above site, during a survey done 22-24 September 1997 just downstream of the metropolitan St. Paul, MN area. However, the first two random dives, each covering about 3 m X 15 m, yielded one Minnesota endangered Quadrula nodulata (Rafinesque 1820) and one Minnesota threatened Tritogonia verrucosa (Rafinesque 1820) among 130 unionids (11 species). Both of these special status unionids are probably the first live representatives of these species in the Minnesota portion of the Upper Mississippi River for many years. The source of Q. nodulata is unknown, but T. verrucosa lives in the nearby St. Croix River. Random dives throughout the site yielded seven more Q. nodulata, each representing different age classes (3, 4, 6, 7, 8, 9, 10, 13 years old) indicating nearly yearly reproduction of Q. nodulata in the area.
At total of over 700 unionids were found representing 14 living species at a mean density of about 2.0/m2. An additional 11 species were represented by empty shells, four of which were represented by fresh shells, while the remaining 7 species were represented by sub-fossil shells. All living unionids were measured and aged. There was recent reproduction of most species. Living unionids were in excellent exterior condition with well preserved beak sculpture and no evidence of any erosion, even at 10 to 20 years of age; this phenomena is almost never seen. Only one living Dreissena polymorpha (Pallas 1771) was found attached to a Quadrula quadrula (Rafinesque 1820) One fresh-dead D. polymorpha was also found. The host fish for Quadrula nodulata apparently has not been confirmed in recent times, but the early 1900's literature indicate the host may be the channel catfish, flathead catfish, bluegill, or smallmouth bass (Fuller 1978). Q. nodulata was not found alive in 1996 among over 6,000 unionids we handled at Winona, MN, nor among nearly 13,000 unionids handled at La Crosse, W1, about 100 and 125 river miles downstream respectively of the Grey Cloud Island site. Q. nodulata is nearly unknown from the nearby St. Croix River (Havlik 1987). The Tritogonia verrucosa was 11 years of age. Studies for the host of T. verrucosa have been done recently (Hove 1997). Improvements to the sewage treatment plants in the Twin Cities, MN, area, along with the general cleanup of industrial contamination, have apparently improved water quality conditions to the extent that unionids have begun to re-populate areas downstream of the Pig's Eye Sewage Treatment Plant, including the area near Grey Cloud Island. This site is also near the upstream limits of the commercial navigation channel. Apparently nearby barge traffic has little recent effect on this Mississippi River side channel unionid mollusk population.
Robert Anderson
U.S. Geological Survey
1000 Liberty Ave, Rm 2204
Pittsburgh, PA 15222
PH: (412) 644-2778; FAX: (412) 355-2548; e-mail: rmanders@usgs.gov
In July 1996, a specimen of Toxolasma parva was collected for the first time in the Monongahela River, Allegheny County, Pennsylvania. A composite of five (5) sediment samples were collected with a petit ponar. The samples were taken from depths of 0.5 - 1.5 m. in a mud substrate near river mile 5 within the city of Pittsburgh. The T. parva specimen measured 25 mm long and is therefore larger than is typical for this species. Age has not been determined. The specimen was deposited in the Carnegie Museum of Natural History (Catalog number 47.389).
Toxolasma parvahas been documented only once from Pennsylvania. Several specimens were collected at Conneaut Lake Outlet, Crawford Co., Pa. (Ortmann, 1919). The habitat typically associated with this species has very low stream velocity and silt substrate. The habitat at the collecting site in the Monongahela River has these characteristics.
The Monongahela River has a history of severe degradation but has exhibited recovery in recent years. This river is maintained for commercial navigation for its entire length and is effected by acid mine drainage, extensive industrialization, sewage, and urban runoff. The macro-biotic community has been reduced and was previously virtually eliminated. The loss of the entire unionid community in this river segment occurred a century or more ago (Ortmann, 1909). The re-colonization of the lower Monongahela River by a unionid mussel follows a significant recovery of the fish community of the Monongahela River, Allegheny River, and upper Ohio River since the mid- 1960's.
The sample was collected as part of the National Water Quality Assessment (NAWQA) Program that assesses water quality through the analysis of surface-water and ground-water chemistry, stream habitat, and biotic measurements in numerous basins nationwide. This assessment is designed to intensely focus on relatively few sites in each basin for a period of three years in the initial phase to be repeated in 5-year cycles. The Allegheny-Monongahela Study Unit in western Pennsylvania, West Virginia, Maryland, and New York completed the initial year of sampling in 1996.
Ortmann, A.E., 1909, The destruction of the fresh-water fauna in western Pennsylvania. Proceedings of the American Philosophical Society. v. 48 p. 90- 110.
Ortmann, A.E.. 1919, A Monograph of the Naiades of Pennsylvania. Memoirs of the Carnegie Museum, Pittsburgh, PA. p. 1 - 385.
Authors: Michelle B Steg, Dr. Richard J. Neves
Address: Virginia Cooperative Fish & Wildlife Research Unit
Biological Resources Division
Department of Fisheries and Wildlife Sciences
Virginia Polytechnic Institute and State University
Blacksburg, VA 24061-0321
Phone Numbers: (540) 552-8846 (M.B. Steg); (540) 231-5927 (R.J. Neves)
Fax Number: (540) 231-7580
Email: msteg@vt.edu (M.B Steg); mussel@vt.edu (R.J. Neves)
Report:
Fish hosts were identified for two Virginia state listed freshwater mussel
species, the black sandshell (Ligumia recta) and Tennessee
heelsplitter(Lasmigona holstonia) during 1996 and 1997. Both species
exhibited low degrees of host specificity in laboratory tests. Host fish
identified for the state threatened L. rectawere large mouth bass,
green sunfish, redbreast sunfish, rockbass, white perch, yellow perch,
platy, and convict cichlids. Non-indigenous fish species were tested for
potential use in the captive production of mussels. Host fish identified
for the state endangered L. holstonia were the banded sculpin and
rockbass. Central stonerollers, striped shiners and warpaint shiners were
identified as potential hosts, with numerous encysted glochidia observed on
fish that died at ten days post-infestation. The average water temperature
was 21.5oC. The following table summarizes our results- note that
some species exhibited limited success and may require further testing.
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Fish hosts of the federally endangered pink mucket, Lampsilis abrupta
M. Chris Barnhart, Frank A. Riusech and Andrew D. Roberts
Department of Biology, Southwest Missouri State University
Springfield, MO 65804
417-836-5166; MCB095f@wpgate.smsu.edu
Herein we report the results of laboratory tests for suitable fish hosts of Lampsilis abrupta(Say, 1831). The distribution and taxonomy of this species, [formerly known as Lampsilis orbiculata(Hildreth, 1828)] were reviewed in the Recovery Plan (USFW 1985). Both Lampsilis abrupta and its near relative, Lampsilis higginsi,are federally