| Species | Number tested | Glochidia attachment period (days) | Species | Number tested | Glochidia attachment period (days) |
| T. verrucosa |   |   |   |   |   |
| northern pike | 10 | 7-10 | brook stickleback | 14 | 4-11 |
| central mudminnow | 15 | 5-8 | banded killifish | 14 | 2-5 |
| black bullhead | 42 | 10-37 | mottled sculpin | 3 | 8-13 |
| brown bullhead | 5 | 16-19 | blackside darter | 6 | 4-7 |
| yellow bullhead | 4 | 16-20 | fantail darter | 9 | 4-7 |
| channel catfish | 9 | 1-8 | Iowa darter | 11 | 4-24 |
| tadpole madtom | 8 | 8-21 | Johnny darter | 13 | 1-4 |
| eelpout | 3 | 4-8 | logperch | 7 | 4-7 |
| trout-perch | 2 | 1-4 | walleye | 7 | 8-12 |
| C. monodonta |   |   |   |   |   |
| black bullhead | 15 | 1-9 | mottled sculpin | 6 | 6-8 |
| yellow bullhead | 6 | 1-6 | eelpout | 6 | 3-6 |
| stonecat | 1 | 1-4 | freshwater drum | 3 | 1-6 |
| tadpole madtom | 6 | 1-4 |   |   |   |
Host suitability trial results to date suggest most Ictalurids tested are only marginal hosts for the pistolgrip. Only six juveniles were collected from brown bullheads in this study. Past studies have shown yellow bullheads will serve as hosts (Pepi and Hove 1997) but very few juveniles were collected and yellow bullheads did not facilitate metamorphosis this year. However, flathead catfish facilitated metamorphosis of 'many' juveniles in a study by Howells (1997). Additional studies should be conducted to determine if other species serve as hosts for T. verrucosa and C. monodonta glochidia.
Partial funding for this study was provided by the Minnesota's Natural Heritage & Nongame Research Program and Bell Museum of Natural History. The Minnesota Environmental and Natural Resources Trust Fund provided additional funds. We gratefully thank Dave Heath, Ron Benjamen, and Mark Endris of the Wisconsin Dept. of Natural Resources for collecting gravid mussels.
Literature Cited
Howells, R. G. 1997. New fish hosts for nine freshwater mussels (Bivalvia: Unionidae) in Texas. Texas Journal of Science. 49(3): 255-258.
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(l): 13-19.
Pepi, V. E. and M. C. Hove. 1997. Suitable fish hosts and mantle display behavior of Tritogonia verrucosa. Triannual Unionid Report. 11: 3.
At extinction's edge: Margaritifera auricularia (Bivalvia: Unionoida)
Cristian R. Altaba
Institut Mediterrani dEstudis Avanqats (CSIC-UIB)
Ctra. de Valldemossa, Km 7.5, 07071 Palma de Mallorca (Illes Balears, Spain)
tel-fax: 34 - 971 - 24 88 44
e-mail: ieacra4@ps.uib.es
One of the most endangered naiads (unionoid bivalves) in the world is Margaritifera (Pseudunio) auricularia (Spengler, 1793), originally distributed in large rivers of Western Europe and the Maghrib. Once considered extinct, a living population was rediscovered in 1985 in the lower reaches and adjoining channels of the river Ebro in Spain.
An intensive sampling along 47 Km, triggered by public works aimed at recovering riverine navigation, has allowed an evaluation of the status of this population. Individuals between less than 2 and more than 14 cm long have been located, the latter having an age (assessed by examination of thin sections of empty shells) close to 100 years. Their total number was initially estimated at 27,000 ± 4,000, although a statistical recalculation showed that it is probably 8,400 ± 3,100. The spatial distribution is very irregular, with over 80% of them confined to less than 2% of the river bottom, and half of the study area unoccupied due to pollution and impoundment.
It is possible to save this last, fragmented population of M. auricularia with an effective protection embracing the river itself. Water authorities have responded to the pledge, and popular activities have resulted in a growing awareness among the area's residents. Without this species, the riverine ecosystem would lack an emblematic species, and would remain impoverished in terms of biodiversity, structural complexity, and interaction richness.
This research program started in February 1996, and has been the subject of previous contributions to the Triannual Unionid Report. In this context, the claim made by Araujo, Jimenez and Ramos in this newsletter (T.U.R. 14: 15) that nobody had seen the species alive since 1917 seems most strange. Indeed, last February they attended an official meeting on the current status of the species, hosted by the Ebro Delta Natural Park, where our research was fully exposed. I believe it is most unfortunate that their desire of notoriety conflicts with conservation action for this species. At any rate, we continue to work, and a large ecological project, funded by the Spanish Ministry of the Environment, is due to start next January.
Altaba, C.R. 1990. The last known population of Margaritifera auricularia; a conservation
priority. Biological conservation, 52 (4): 271-286.
Altaba, C.R. 1997. Al limit de l'extincio: Margaritifera auricularia (Bivalvia: Unionoida).
Butlleti de la Institucio Catalana d'Historia Natural, 65: 137-148.
A preliminary report of an investigation of whether brooding pistolgrip and purple wartyback release chemical attractants
Jennifer L. Sieracki, Mark C. Hove, Melissa M. Tenpas, and Peter W. Sorenson
University of Minnesota, 1980 Folwell Avenue, St. Paul, MN 55108
(612) 624-3019
sier0010@tc.umn.edu
Mark.Hove@fw.umn.edu
mtenpas@tc.carroll1.cc.edu
pws@fw.umn.edu
It is widely believed that certain unionids use visual cues to attract fish to their glochidia. For example, many lampsilines wave portions of their mantles that resemble food items (small fish or aquatic insects) to fish. Also, conglutinates produced by mussels appear to resemble food items of fish, sometimes with startling detail (e.g. larval fish-like conglutinates of Ptychobranchus occidentalis). The precise nature of the sensory cues used by mussels to attract their hosts has yet to by fully elucidated, however.
For the past year we have been investigating the possibility that naiades may have evolved to produce chemical attractants to supplement visual cues. This is a preliminary report of this work that is still in its infancy.
We believe that naiades may have evolved to produce chemical attractants simply because chemical cues are generally the primary means by which fish find food items in turbid freshwaters from a distance. Further, chemicals are readily distributed in the water and are detected with great sensitivity and specificity by fishes. The unusual mantle displays of pistolgrip (Tritogonia verrucosa) and purple wartyback (Cyclonaias tuberculata) mussels lead us to investigate the possibility that these species may use chemical cues to attract their catfish hosts. To determine if catfish are attracted to these mussel odor we observed catfish under the following conditions: (1) in the presence of brooding pistolgrip, (2) in the presence of a purple wartyback conglutinate, and (3) while exposed to the water from a container holding brooding purple wartyback or pistolgrip. Here we report our initial findings.
In the first experiment, year-old channel catfish were placed in a 10-gallon aquarium that contained both brooding and non-brooding pistolgrip. After being permitted to acclimate for 15 min., the fishes' behavior was observed. On two occasions a fish was seen to brush against the mantle of a displaying pistolgrip but this did not elicit feeding behavior (vigorous snapping and nosing against object). Although the fish did not appear attracted to the inflated pistolgrip mantle, one fish did nose and nudge the excurrent siphon of a gravid, non-displaying pistolgrip. Although inconclusive, these results are suggestive of a role of chemical cues, leading us to the second experiment.
The second experiment using a purple wartyback conglutinate also produced suggestive but as yet inconclusive results. Feeding behavior was not observed during two trials where young, hatcheryreared channel catfish were placed in a 10-gallon aquarium with a petri dish holding the conglutinate. During a third trial however, a conglutinate was placed in a 40-gallon aquarium with three 3-5 year old, wild-caught channel catfish. One of the fish briefly inhaled and expelled the conglutinate.
Tests are currently underway to address our initial suggestive findings that mussel odor might be important to host attraction. Six trials with different channel catfish and one yellow bullhead have been conducted in a 75-gallon flow-through tank with painted floor lines to form five quadrants. After a 24 hour acclimation period 200 ml of water from an aquarium holding brooding purple wartyback or pistolgrip was introduced to one end of the tank through a plastic tube. The number of times a fish crossed a quadrant line and its orientation to the added water was recorded. During the first four trials fish moved very little. However, in the last two trials, we reduced test chamber light level and a yellow bullhead began exhibiting searching behavior approximately five minutes after water was added to the tank. The fish repeatedly approached the water inlet tube, rubbed against it, and bit it. After 1-3 minutes, it returned to searching behavior, eventually investigating the tube again. These behaviors lasted 5-10 minutes, after which time the bullhead resumed resting.
We plan to continue testing mussel odor to see if we can repeat the last finding. In addition, we hope to expand this study to observe the reaction of different Ictalurids to gravid purple wartyback and pistolgrip, and compare the behavior of wild-caught and hatchery-reared fishes. We welcome suggestions.
Funding for this study was provided by Minnesota's Natural Heritage & Nongame Research Program, Minnesota Environmental & Natural Resources Trust Fund, University of Minnesota, CBS Summer Undergraduate Research Program, and Minnesota Agriculture Experiment Station.
Report: Abstract of a dissertation, University of Tennessee, Department of Ecology and Evolutionary Biology: Multi-scale analysis of unionid freshwater mussel community structure in the upper Tennessee River Basin
Author: Brenda Rashleigh
Address: U.S. Geological Survey, 1820 Midpark Drive, Knoxville, TN 37921
Phone/Fax: (423) 545-4140 (phone) (423) 545-4496 (fax)
Email address: rashleig@usgs.gov, brenda@tiem.utk.edu
Populations of freshwater mussels of the family Unionidae are experiencing a decline in the upper Tennessee River basin. An understanding of the processes by which the structure of mussel communities is created and sustained may aid conservation efforts. Here, modeling is used to explore the patterns that are generated in local, mesoscale, and regional communities when particular biotic or abiotic processes are specified, and to generate predictions to which actual mussel data are compared.
Locally competing mussel species can coexist under equilibrium conditions only when each is sufficiently more successful on a different resource in terms of either resource use, life history characteristics, or a combination of the two. Temporal variability in fecundity promotes coexistence of a poorer competitor, particularly when variability is high and uncorrelated between species. Neither resource partitioning nor the influence of temporal variability explained coexistence of two similar freshwater mussel species.
At the mesoscale, competition can reduce species number and lead to spatially nested composition, whereas long-distance dispersal consistent with metapopulation dynamics has the opposite effect. Patterns in three mussel communities in the upper Tennessee River were most consistent with structuring by competition, however, at the low species number exhibited in real communities, competitive interactions were relatively weak in generating patterns.
Regional species richness in model communities increased with decreasing critical fitness values for colonization and extinction. High richness reduced average individual species, fitness, which inhibited colonization and further promoted richness through speciation. High-richness communities exhibited low variability among replicate scenarios and high resource specialization among species, consistent with structuring by biotic processes. Data from the upper Tennessee River basin appeared to be structured by biotic processes.
Different processes appear to structure freshwater mussel communities at different spatial scales: communities appear increasingly structured by biotic processes with increasing spatial scale. In general, biotic processes generate simple rules that guide a system's development, while abiotic processes control expression of pattern. The results of this study can be used to develop predictive models, and to interpret observed patterns of decline.
Author: Tom Augspurger
Address: U.S. Fish and Wildlife Service, PO Box 33726,
Raleigh, NC 27636-3726
Phone Number: 919/856-4520 x.21
Fax Number: 919/856-4556
E-mail: tom-augspurger@fws.gov
This office has partnered with a number of individuals on projects related to water quality and the conservation of freshwater mussels. Specific projects are outlined here; more detail is available upon request:
I. The University of Georgia has been funded to conduct acute and sub-chronic toxicity tests on early lifestages of three non-endangered mussels that will serve as surrogates for three of North Carolina's five endangered mussels: the Carolina heelsplitter (Lasmigona decorata), dwarf wedgemussel (Alasmidonta heterodon), and Tar spinymussel (Elliptio steinstansana). Proposed surrogates are the green floater (Lasmigona subviridis), the Atlantic pigtoe (Fusconaia masoni), and a species to be selected from the FWS / NBS Surrogate Species for Freshwater Mussels list.
ii. We entered into an agreement with the U.S. Environmental Protection Agency's Science and Ecosystem Support Division in Athens, Georgia, to conduct fluoride toxicity testing on the endangered Appalachian elktoe (Alasmidonta raveneliana) and a surrogate species. Fluoride is a known contaminant in habitat for the Appalachian elktoe, but there are currently no pertinent data to evaluate the significance of this pollutant on freshwater mussel survival or reproduction. Acute and sub-chronic toxicity tests on glochidia and juvenile stages will provide data to help evaluate existing fluoride exposure and provide a foundation for reviewing proposed additional loadings.
iii. The North Carolina State University College of Veterinary Medicine received a grant to conduct an assessment of the health of the Carolina heelsplitter (Lasmigona decorata). We funded their proposal with the expectation of realizing a first ever report of observed prevalences of diseases detected in a surrogate species for Carolina heelsplitter. Because of the small size of these organisms and the number of tests to be performed, a significant ancillary benefit will be the development of health assessment protocols suitable for other listed fish and molluscs. Parameters to be assessed include overall condition, histology of major organ systems, and the prevalence of specific bacterial, viral, fungal, protozoan, and metazoan disease agents.
Distribution and habitat of freshwater mussels in Colorado
James Cordeiro
American Museum of Natural History, Dept. of Invertebrates
Central Park West @ 79th Street
New York, NY 10024
cordeiro@amnh.org, (212) 769-5720
North America has the greatest diversity of freshwater mussels in the world, yet members of the superfamily Unionacea are the most highly threatened group of organisms in the United States. Colorado represents the westernmost range of some plains species. With the exception of the generalist Anodonta grandis grandis, freshwater mussel populations are in decline in Colorado, both at the species level and at the population level. Eight former Colorado species have been reduced to only three, one of which is represented by only one dead shell. Of 26 documented localities from museum and published records, only eight remain. This study adds another five. Only one of the ten previously documented lotic habitats still contains mussels. Surviving populations are largely confined to human-created reservoirs of recent origin.
The cylindrical papershell, Anodontoides ferussacianus (Lea), was once the most common species in the state (15 localities). It is currently found only in a slow-moving foothills stream with sand/cobble substrate and a small foothills lake with high turnover and mud/cobble substrate. Neither habitat is subject to large-scale annual changes in flow or water level. A. ferussacianus has never been documented to occur in the Republican or Arkansas River drainages and this study confirms its absence there. A single dead shell of Uniomerus tetralasmus (Say), the pondhom, found in Queen's Reservoir is the only recent evidence of the pondhom in Colorado. This specimen was found in a southeastern plains lake with a thick mud/clay bottom subject to periodic dessication. Anodonta grandis grandis Say, the giant floater, has maintained steady populations in Colorado, but no longer occurs in streams. It occurs on mud substrates in recent, human-created, plains reservoirs with hard, alkaline water, and calcium contents greater than 46 mg/l. The spread of the species into reservoirs along the Arkansas River drainage testifies to its adaptability.
Management of these species in Colorado requires knowledge of the location of population sources, the status of those populations, and the habitat conditions under which the populations exist provided in this study as well as a reintroduction program to prevent further decline. The success of the introduced Pueblo Reservoir population lends testimony to the fact that reintroduction can be successful, at least for Anodonta grandis grandis. Potentially stable population sources for reintroduction along the South Platte River drainage include Boulder Reservoir and Cherry Creek Reservoir for Anodonta grandis grandis and Valmont Reservoir for Anodontoides ferussacianus. Stable population sources along the Republican River drainage no longer exist. The Flagler Reservoir population is in rapid decline and can no longer be considered stable. Stable population sources along the Arkansas River drainage include Pueblo Reservoir and CF&I Reservoir Nos. 1-3. It is likely already too late for Uniomerus tetralasmus as all former populations seem to have disappeared.
Cleveland Island Mussel Survey, 1997
Don W. Gowan
The Nature Conservancy, Clinch Valley Bioreserve
151 W. Main Street, Abingdon, VA 24210
(540)676-2209, dgowan@tnc.org
Introduction
In December 1997 Don Gowan, The Nature Conservancy, and Leroy Koch, U.S. Fish and Wildlife Service, visited the Cleveland Island mussel site at Clinch River Mile 271. This site is a series of three forested islands located 0.6 miles below the Virginia Route 82 bridge at Cleveland, Virginia. These islands split the river into four distinct channels which form a large area of good mussel habitat. Church (1992) reported 21 species of mussels, including five federally endangered species, at the site.
The purpose of the survey was to assess the status of the unionid fauna following installation of an ultraviolet light disinfection system at the town of Cleveland's wastewater treatment plant, which discharges to the Clinch River 0. 1 miles above Cleveland Island. This plant was upgraded from a chlorination/dechlorination disinfection system to an ultraviolet light disinfection system in 1994 to protect the mussels at Cleveland Island from an accidental release of chlorine, or failure of the dechlorination system at the plant. Laboratory bioassays have demonstrated the sensitivity of unionids to chlorine and other halogen based compounds (Goudreau, et al., 1993).
Results of Survey
Sampling consisted of the collection of fresh dead mussel shells from muskrat middens at the site and limited instream sampling with view scopes. A total of nine species and 43 fresh dead individuals were collected in the middens (Table 1). The most abundant species collected was Actinonaias pectorosa (pheasantshell), with 18 fresh dead individuals, followed by Elliptio dilatata (spike), with nine fresh dead individuals. One individual of the federally endangered species Fusconaia cor (shiny pigtoe) was collected. Four specimens collected were less than four years old.
Recommendations
The mussel population at Cleveland Island appears to be reproducing as evidenced by the presence of specimens less than four years old. However, it is recommended that additional survey work be conducted to fully establish the health and reproductive status of the mussel population at the site.
References
Church, C.W. 1992. An assessment of the mussel fauna at Cleveland Islands, Russell County, Virginia. Report to The Nature Conservancy, Abingdon, Virginia.
Goudreau, S.E., R.J. Neves, & R.J. Sheehan. 1993. Effects of wastewater treatment plant effluents on freshwater mollusks in the upper Clinch River, Virginia. USA. Hydrobiologia 252: 211-230.
Steven Ahlstedt
U. S. Geological Survey
1820 Midpark Dr.
Knoxville, TN 37921
Phone: (423) 545-4140 Ext. 17
FAX: (423) 545-4496
E-Mail: ahlstedt@usgs.gov
I wish to thank Dick Biggins (USFWS, Reg. 4), Roberta Hylton (USFWS Reg. 5), Wayne Poppe (TVA), Leslie Colley (TN Nature Conservacy), Don Hubbs (TWRA), Don Gowan (VA Nature Conservancy), Steve Roble (VDCR), and Monty McGregor (VCGIF), for funding the poster "Mussels - Upper Clinch River Tennessee and Virginia." Posters can be obtained from Don Gowan (540) 676-2209 or USFWS, Region 5, Abington Field Office (540) 623-1233.
Common pleurocerid snails (4 species) collected from the Nolichucky River the past two years and reintroduced into the Pigeon River are surviving. Mark Fagg (Tennessee Wildlife Resources Agency) and I moved another 5,000 snails this spring into the Pigeon. This project will continue at two sites until reproducing populations are established.
Spiny riversnails will be monitored in the Holston and French Broad rivers late July or early August. Those populations will be further augmented in cooperation with the TWRA until reproduction is found. Spiny riversnails will also be reintroduced into the Little River at a site where they occurred historically. If anyone would like to help with this please contact me.
Don Hubbs
P.O. Box 70 Camden, TN 38320
e-mail - TNMussels@aol.com
New phone/fax # (901-8548)
Tennessee's commercial mussel industry is again experiencing low demand for shell. As of the first week of July, TWRA has sold approximately 300 musseling licenses compared to - 650 for all of 1997, and 1,200 in 1996. This lull in harvest has allowed the mussel resource of Kentucky Lake to begin recovering from almost a decade of increasing harvest pressure. Samples taken thus far indicate that in some areas, as much as 50% or more of the resource is at or above legal size. This compares favorably to estimates of 5 to 10% legal size from previous years. Tennessee mussel shell prices are : ebony - 2 3/8" $0.35/lbs (if buyers are purchasing), threeridge/mapleleaf -2 5/8" $0.50/lbs, 2 3/4" $1.80/lbs, washboards 3 3/4" (have not been buying since April), washboards 5" or at least shell 5/8" thick - $5.50/lbs (all prices are for "live" meat in shell).
TWRA mussel program personnel have been busy assessing mussel population status and harvester activity during this time of decreased harvest pressure. We have yet to see evidence of the exotic zebra mussel increasing on the lower TN River, although we did collect a couple of blue crabs from TVA's New Johnsonville steam plant. We have also continued attempts to culture common mussel species and are working on an improved collection method for juvenile (1 + year class mussels). This new method employs a 4" suction dredge capable of moving up to 4 cu. Yards of material per hour. We hope to use this new method to collect sufficient numbers of juvenile mussels from high density areas for restocking in preselected habitats.
Tennessee and Alabama have received funding for a joint project to collect endangered mussel brood stock from the Tenn. River in TN and AL later this summer/fall. We will also be locating habitat to release cultured juvenile mussels for future monitoring.
Copper residuals in fish hatchery pond sediments: possible associations to freshwater mussels
Robert G. Howells
Texas Parks and Wildlife Department, HC07, Box 62, Ingram, TX 78025
(830) 866-3356; fax 866-3549; rhowells@ktc.com
and Dan E. Webb
Angelo State University, Biology Dept., San Angelo, TX 76909
(915) 942-2189; fax 942-2184; aab281@angelo.edu
Freshwater mussels (Family Unionidae) are among the fastest declining faunal groups in North America (Neves 1993; Williams et al. 1993) with impacts from environmental modification and pollution, introduced exotic species like zebra mussels, over harvest, and a host of other threats. Subsequently, scientific attention to this group has increased dramatically over the past 10 years. One area of study has included establishing captive populations, often at fish hatcheries, as a source of specimens for future reintroduction and to protect from invading zebra mussels (Dunn and Layzer 1997; and others).
Shortly after Texas Parks and Wildlife Department initiated work with unionids at Heart of the Hills Research Station (HOH) in 1992, over 100 specimens of each of four species and additional specimens of other taxa were stocked into holding cages in research station ponds in 1992-93 and again in 1993-94. An apparently introduced disease caused losses during the first effort, but otherwise, mussels generally survived well. Dissections confirmed feeding in all species and reproduction in several. However, virtually no growth was documented. In an effort to examine possible explanations for this apparent lack of growth, chemical composition of pond sediments was considered. HOH was constructed in the mid-1920s as a fish hatchery. It continued to function as a hatchery until 1969 when it became a fisheries research station. Throughout its use, ponds at HOH were treated frequently with copper in the form of copper sulphate or copper acetate to control parasites on fishes and algal growths in the ponds. Further, copper readily precipitates out of solution in hard-water alkaline environments typical of HOH ponds. Copper is also particularly toxic to invertebrates.
Samples of sediments were obtained from the spring which feeds water to HOH and from two HOH ponds. These were sent to Angelo State University where they were subjected to energy dispersive x-ray fluorescence to examine levels of copper present. Techniques followed Webb and Dawkins (1998) where labware was washed with nitric acid and distilled water and oven dried. Triplicate subsamples were ground and placed on Formvar film slides then irradiated for 1,000 live seconds with 35 kV primary x-rays generated by a Rh target with a target current of 30 mA. Calculations to determine copper concentration (Webb and Dawkins 1998) found levels at the spring of 15.1 ± 2.0 ppm, but found levels in the two research station ponds of 48.4 ± 7.1 and 36.8 ± 6.0 ppm.
Whether the copper concentrations found relate to the lack of observed growth in unionids living in these sediments is unclear. However, amounts copper in research station (i.e., hatchery) ponds which had been treated with copper for many decades were clearly higher than local background levels. This suggests the possible presence and potential impacts of copper and other substances in hatchery ponds should be considered when unionids are relocated to these facilities.
References:
Dunn, C.S., and J.B. Layzer. 1997. Evaluation of various holding facilities for maintaining freshwater mussels in captivity. Pages 205-213 inK.S. Cummings et al. Conservation and Management of Freshwater Mussels II: Initiatives for the future. Proceedings of a UMRCC Symposium, St. Louis, Missouri.
Neves, R.J. 1993. A state-of-the-unionids address. Pages 1-10 inK.S. Cummings et al. Conservation and Management of Freshwater Mussels. Proceedings of a UMRCC symposium, St. Louis, Missouri.
Webb, D.E., and R.C. Dawkins. 1998. A comparison of trace element concentrations in Corbiculasp. (Bivalvia: Corbiculidae) and sediment from the Concho River by energy dispersive x-ray fluorescence. The Texas Journal of Science 50(2): 149-154.
Williams, J.D., M.L. Warren, Jr., K.S. Cummings, J.L. Harris, and R.J. Neves. 1993. Conservation status of freshwater mussels of the United States and Canada. Fisheries (Bethesda) 18(9):6-22.
Announcement of a September 9-10, 1998, Meramec River Freshwater Mussel Identification Workshop
"...every scrap of biodiversity is priceless, to be learned and cherished, and never to be surrendered without a struggle."
Edward O. Wilson
Dear unionid novices and enthusiasts,
The Meramec River is one of Missouri's most treasured streams. Among other taxonomic groups associated with stream habitats, the Meramec supports over 100 species of fish and over 40 species of freshwater mussels. Many who have witnessed the awesome scenery and rich biodiversity of this river call it "Missouri's Gem''. Over the last several decades, conservation agencies, environmental groups, stream teams, land owners, and local people have worked hard to preserve this river in its natural state.
To celebrate the diversity of life in the Meramec River, the U.S. Fish and Wildlife Service will be sponsoring a freshwater mussel identification workshop on September 9th and 10th. This workshop is a good opportunity to become acquainted with these unique mollusks and gain hands-on experience with identification. The first day will be held indoors at the Meramec State Park visitor center in Sullivan, Missouri. Invited Malacologists will give several slide presentations and lead group laboratory exercises in identification. We will spend the second day in the Meramec River collecting and identifying shells and live mussels. Many species we will be working with are common throughout the Midwest, so this will be beneficial to those outside Missouri as well.
If you are interested in attending, please provide the information requested below and return by COB Friday, July 17. Unfortunately, there are a limited number of slots available (the first 40 responses will be accepted). Those attending will receive more detailed information and others will be notified accordingly. Feel free to forward this message to others you feel would be interested. If you have any questions please don't hesitate to contact me. Thank you.
Sincerely,
Andy Roberts
U.S. Fish and Wildlife Service
608 East Cherry Street, Room 200
Columbia, MO 65201
(573) 876-1911 ex. 110
Andy_Roberts@mail.fws.gov
Meramec River Freshwater Mussel Identification Workshop
Place: Meramec State Park Visitor Center in Sullivan, Missouri (approximately 1 hour west of St. Louis)
Dates: September 9 (lab exercises) and 10 (field trip) (there will be an optional field survey on the 11th)
Time: 8:00 a.m. to 5:00 p.m.
Lodging: There are several options. Motel rooms are available in the
park that can accommodate up to three persons (1-2 people--$55, 3
people--$60). A variety of hotels are also available in Sullivan,
approximately three miles from the park. U.S. government per diem for
Sullivan, Missouri is $50 for lodging and $30 for food. The room rates
in Sullivan are as follows:
Best Western       (573) 468-3136
Family Motor Inn       (573) 468-3891
Ramada Inn       (573) 468-4172
Sullivan Super 8       (573) 468-8076
Please respond by e-mail or phone and provide the following information. If responding by e-mail, copy and paste the following text to a reply letter and fill out the information requested.
I would like to attend the mussel workshop.
Name:
Job Title:
Business Mailing Address:
Business Phone:
Emergency Contact (name and phone):
_ Please reserve a private room for me in Meramec State Park
_ To cut down on expenses, I would be willing to share a room with another participant at Meramec State Park. I will be sharing a room with (name):
_ I will be lodging in Sullivan and will call to reserve a room for myself
Announcement of a new mussel book: The Pearly Mussels of New York State
David Strayer1and Kurt Jirka2 1Institute of Ecosystem Studies, Box AB, Millbrook, NY 12545, (914) 677-5343; strayerd@ecostudies.org 2Ichthyological Associates, 50 Ludlowville Road, Lansing, NY 14882
Our new book "The pearly mussels of New York state" has just been published as Memoir26 of the New York State Museum. This hardcover book (113 pages plus 27 plates) summarizes the distribution of unionoid mussels in New York and discusses the zoogeographic and ecological reasons behind those distributions. The book contains spot maps, descriptions, differential remarks, and illustrations (most in color) for each of the 53 species known or thought to occur in New York. The book also includes keys to the identification of the species, general reviews of mussel biology and zoogeography in New York, notes on collection and identification of mussels, a discussion of 10 species erroneously reported from New York, a brief synonymy, and an extensive list of references. The color illustrations are numerous and of remarkably high quality. Twenty-five plates contain 165 life-size paintings originally prepared in 1906-1925 by Helen Winchester, Wilfred Davison, and George Barkentin for Henry Pilsbry's unpublished monograph on New York's non-marine mollusks. These illustrations, used by the kind permission of the Academy of Natural Sciences of Philadelphia, are of extraordinary fidelity and beauty. They are supplemented by 15 color photographs and many black-and-white drawings.
This book should be useful to anyone interested in the ecology or distribution of unionoid mussels in northeastern North America. It is available for $50 (plus $4 for shipping) from Publication Sales, New York State Museum, Albany, NY 12230 (518-449-1404).
Report: Statewide survey of listed and candidate freshwater mussels in Missouri
Authors: Sue A. Bruenderman and Andrew D. Roberts1
Addresses: Missouri Department of Conservation, Fisheries and Wildlife Research Center, 1110 South College Ave., Columbia, Missouri, 65201
1Present address: U.S. Fish and Wildlife Service, Ecological Services, Columbia
Field Office, 608 E. Cherry Street, Columbia, Missouri, 65201
Phone Numbers:
573-882-9880 (Bruenderman); 573-876-1911 (Roberts)
FAX:
573-882-4517 (Bruenderman); 573-876-1914 (Roberts)
E-mail:
bruens@mail.conservation.state.mo.us; andy_roberts@mail.fws.gov
Between July and November, 1997, we surveyed unionid mussels in the Meramec River Basin to complete the first of a three-year statewide survey to assess Missouri's mussel fauna. Of 79 localities sampled in the Meramec River Basin, fifty-eight (58) were sampled previously by Buchanan (1979). Twenty-one (21) additional localities had never been sampled before, to our knowledge. In total, we examined 11,067 living specimens in 338 person-hours of search time in the basin. Overall catch per unit effort (CPUE) was 32.7 mussels/person-hour. We documented the presence of forty-three (43) extant unionid species in the Meramec River Basin during this study; we collected live specimens of forty-one (41) and freshly dead valves of two (2) additional species. The five most abundant unionid species in the basin were the mucket, Actinonaias ligamentina(29.2% total catch), spectaclecase, Cumberlandia monodonta(20.9%), threeridge, Amblema plicata(11%), round pigtoe, Pleurobema coccineum(4.8%) and pimpleback, Quadrula pustulosa(4.5%). We collected live specimens of one federally endangered (pink mucket, Lampsilis abrupta)and eight unionid species either officially listed or of special concern in Missouri: elktoe (Alasmidonta marginata),rock pocketbook (Arcidens confragosus),spectaclecase (Cumberlandia monodonta),snuffbox (Epioblasma triquetra),ebonyshell (Fusconaia ebena),scaleshell (Leptodea leptodon),sheepnose (Plethobasus cyphyus)and salamander mussel (Simpsonaias ambigua). Comparison of catch-per-unit-effort (CPUE) at localities sampled in Buchanan's (1979) and again in our survey revealed that numbers of unionids declined by 45%, from 39.7 to 21.8 unionids/person hour. Similarly, mean species richness (total number of species) of live unionids at 28 sites in the Meramec, and 17 sites in the Bourbeuse rivers, declined from 13.6 to 8.1, and 18.8 to 6.9 per site, respectively. As judged by the presence of young mussels less than 6 years of age (=recent recruitment) at sampling localities, we documented that reproduction is still occurring at one or more sites of occurrence for 77% (23 of 30) of the species in the Bourbeuse, 30% (6 of 21) of the species in the Big, and 89% (33 of 37) of the species in the Meramec River.
New publication: Johnson, R.I. 1998. A new mussel, Potamilis metnecktayi(Bivalvia: Unionidae) from the Rio Grande System, Mexico and Texas with notes on Mexican Disconaias.Occasional Papers on Mollusks5 (76) 427-455, pls. 22-27 (January)
Richard I. Johnson
Museum of Comparative Zoology, Harvard University, Cambridge, Massachusetts 02138, Tel. 617-495 2468
ABSTRACT: Potamilis metnecktayi,a new species of Unionidae from the Rio Grande system of Mexico and Texas, is described. It has been mistaken for Lampsilis (Proptera) salinasensisSimpson, 1908, which is a synonym of both Lampsilis fimbriataFrierson, 1907 and Disconaias disca(Lea, 1838) from the Rio Panuco System. Also discussed are Potamilis purpurata(Lamarck, 1819), Cyrtonaias tampicoensis(Lea, 1838), Disconaias walkeri(Baker, 1922), and Lampsilis explicata(Morelet, 1849).
In press: Johnson , R.I. Unionidae of the Rio Grande (Rio Bravo del Norte) system of Texas and Mexico
Richard I. Johnson
Museum of Comparative Zoology, Harvard University, Cambridge, Massachusetts 02138, Tel. 617-495 2468
ABSTRACT. Rio Grande Subprovince is redefined as being limited to only the Rio Grande System of Texas and Mexico. Fifteen species of Unionidae occur in the basin. The recent description Disconaias conchosTaylor and Potamilis metnecktayiJohnson brings the total number of endemic Unionidae to four. Only one of the eleven species which occur north of the Rio Grande also occur in Mexico.
Two years of follow-up after a 1996 unionid translocation from an area with heavy Dreissena polymorpha (Pallas 1771) infestation, Mississippi River mile 695.7, Highway 14-61 Bridge, LaCrosse, Wisconsin
HAVLIK, MARIAN E.
Malacological Consultants, 1603 Mississippi Street, La Crosse, WI 54601-4969. Phone/Fax: 608.782.7958; E-mail: havlikme@aol.com
This translocation was probably the first to be conducted in an area heavily impacted by D. polymorpha6-44 mm long. In July/August 1996, prior to riprap placement around bridge piers, 12698 unionids (27 species) including five endangered Lampsilis higginsiand 575 special status unionids, such as 39 Ellipsaria lineolata,29 Arcidens confragosus,and 234 Pleurobema sintoxia,were translocated. Mean densities were: Pier 6, 2.8/m2 (22 sp.); Pier 7, 0.07/m2 (12 sp.); Pier 8, 10.65/m2 (27 sp.); depths were 4-9 m. Amblema plicatawas 39.75% of the fauna. At Piers 6 and 7 there were a small number of D. polymorphaon most unionids, but at Pier 8, downstream of a grain dock, the substrata was covered with Dreissena 25 to 75 mm deep. Up to 120 or more were on 80% of the unionids which greatly slowed unionid recovery. Many unionids were nearly covered with D. polymorpha,but few were fresh-dead. A saving factor be the strong current at Pier 8, on the outside of a large river bend. Some unionids were devoid of D. polymorphabut had byssal threads. Processing time was doubled by hand stripping D. polymorphabefore each shell was marked on both lower anterior valves; debris was bagged and buried in a landfill. Site I, 0.4 mi downstream of the bridge, was used for translocation of most of the common species. Site II, 4 miles upstream, was used for special status unionids. Recent Mississippi River records included three Alasmidonta marginata,and four Lasmigona costata,found at 6-9 m deep, probably depth records for these small stream species.
Special status unionids were doing well 6 October 1996; 50 small D. polymorphawere on one dead Ligumia recta.On 6-19 September 1997 follow-up was done at both Translocation Sites. Up to 60 small (5 mm) D. polymorphawere removed from most marked shells. Site I marked shell density = 8.1/m2 (93.7% survival); resident density = 14.5/m2. Site II marked shell density = 6.2/m2 (93.6% survival); resident density = 11.6/m2. At Site II 337 (58.8%) of the numbered mussels were found (96.8% survival) including one L. higginsi.Two year follow-up at Site II, 25 June 1998, on 332 special status unionids (57.2%) = 98.5% survival which indicates a 1 -2%/year natural mortality. 40% of L. higginsiwere recovered in 1998. Two species seem most affected by hand-translocation. In 1997 five (of 51) numbered L. rectafound were dead (90.2% survival), plus the one found dead October 1996. At a similar nearby project two of four L. rectawere dead after one year. Others have reported L. rectalaying on the substrata, therefore, L. rectashould be allowed to dig in on its own rather than being hand "planted". Three of 21 A. confragosuswere dead (85.7% survival); only two of 50 M. nervosawere dead (96% survival) after one year, and in 1998 all 56 M. nervosarecovered were alive.
A 'Kinetic' Conglutinate in Strophitus undulatus(Say 1817)
G. Thomas Watters, Scott H. O'Dee & Steve Chordas
Ohio Biological Survey & Aquatic Ecology Laboratory, Ohio State University, 1314 Kinnear Rd., Columbus, OH 43212-1194
voice: 614-292-6170 fax: 614-292-0181 email: gwatters@postbox.acs.ohio-state.edu
The conglutinate of the Squawfoot has been known for many years, and illustrated as far back as 1858. The infective conglutinate is a short, white cord bearing glochidia attached to it on the outside surface by a glochidial thread. However, we have found that when within the marsupium, the glochidia are on the inside of the conglutinate. After the conglutinates are released by the female, the glochidia are pushed through pores in the sides of the conglutinate, and within 1-2 minutes (sometimes within seconds), they emerge to the outside and open, ready to infect. The mechanism for this movement is believed to be osmotic. Conglutinates may be bathed in a hypotonic solution in the marsupium, and when expelled to the outside water, the conglutinate material swells, pushing the glochidia out through the pores. We believe this is the first report of such a 'kinetic' conglutinate - a conglutinate that has innate movement. This phenomenon probably facilitates release of the conglutinates by the female, which may be difficult if the glochidia are already on the outer surface and open

SEM photo of a 'kinetic' conglutinate. The lower glochidium is just emerging; the upper one is nearly free, but has not opened. Bar indicates 200 u.
New potential hosts for: Strophitus undulatus- Ohio River drainage; Strophitus undulatus - Susquehanna River drainage; Alasimidonta undulata - Susquehanna River drainage; Actinonaias ligamentina - Ohio River drainage; and Lasmigona costata - Ohio River drainage
G. Thomas Watters, Scott H. O'Dee & Steve Chordas
Ohio Biological Survey & Aquatic Ecology Laboratory, Ohio State University, 1314 Kinnear Rd., Columbus, OH 43212-1194
voice: 614-292-6170 fax: 614-292-0181 email: gwatters@postbox.acs.ohio-state.edu
1. Squawfoot, Strophitus undulatus (Say, 1817) - Ohio River drainage
Laboratory transforrnations occurred on the following species:
Bluntnose Minnow
The following fishes did not act as hosts:
| Lavender Gourami | Goldfish | Central Stoneroller |
| Longear Sunfish | Banded Darter |
2. Squawfoot, Strophitus undulatus (Say, 1817) - Susquehanna River drainage
Laboratory transformations occurred on the following species:
| Longnose Dace | Sand Shiner | White Crappie |
| Banded Darter | Fantail Darter |
The following fishes did not act as hosts:
| Siamese Fighting Fish | Spotfin Shiner | Rosyface Shiner |
| Central Stoneroller | Bluntnose Minnow | Silverjaw Minnow |
| Fallfish | Largemouth Bass | Shield Darter |
3. Triangle Floater, Alasmidonta undulata (Say, 1817) - Susquehanna River drainage
Laboratory transformations occurred on the following species:
| Slimy Sculpin | Common Shiner | Central Stoneroller |
| Rosyface Shiner | Northern Hogsucker | Pumpkinseed |
| Largemouth Bass | Fantail Darter |
The following fishes did not act as hosts:
| Siamese Fighting Fish | Bluntnose Minnow | Silverjaw Minnow |
| Swallow Shiner | Spotfin Shiner | Longnose Dace |
| Banded Darter |
4. Mucket, Actinonaias ligamentina (Barnes, 1823) - Ohio River drainage
Laboratory transformations occurred on the following species:
| Largemouth Bass | Rock Bass | Tippecanoe Darter |
| Silverjaw Minnow | Central Stoneroller |
The following fishes did not act as hosts:
| Bluntnose Minnow | Creek Chub | Rosyface Shiner |
| Central Stoneroller | Sand Shiner | Spotfin Shiner |
| Striped Shiner | Banded Darter | Variegate Darter |
| Slenderhead Darter | Greenside Darter | Logperch |
| Yellow Perch | Bluegill | Longear Sunfish |
| Mottled Sculpin | Grass Pike |
5. Fluted-shell, Lasmigona costata (Rafinesque, 1820) - Ohio River drainage
Laboratory transformations occurred on the following species:
| Northern Hogsucker | Longnose Dace | Banded Darter |
The following fishes did not act as hosts (* - extralimital):
| Longnose Gar | White Sucker | Rosyface Shiner |
| Spotfin Shiner | Swallowtail Shiner* | Central Stoneroller |
| Longear Sunfish | Largemouth Bass | Pumpkinseed |
| Yellow Perch | Greenside Darter | Slimy Sculpin* |
Infective and non-infective glochidia in Lasmigona costata
G. Thomas Watters, Scott H. O'Dee & Steve Chordas
Ohio Biological Survey & Aquatic Ecology Laboratory, Ohio State University, 1314 Kinnear Rd., Columbus, OH 43212-1194
voice: 614-292-6170 fax: 614-292-0181 email: gwatters@postbox.acs.ohio-state.edu
While conducting host identification studies on Lasmigona costata, we encountered two types of glochidia within the marsupia. The first is a triangular, strongly hooked infective glochidium. The second (see figure) is a round, weakly-hooked or unhooked glochidium. Individuals of this _ second type had obviously grown shell material while in the marsupium. We suspect that this species, like its congener Lasmigona subviridis, may be able to forego the parasitic stage (see elsewhere in this report). But unlike that species, L. costata may be a facultative parasite. It is possible that the two types of glochidia are formed at different times of the year.
Scale bar = 200um
Draft guidelines for maintaining genetic integrity in translocation efforts for aquatic mollusks
Robert S. Butler
U.S. Fish and Wildlife Service
160 Zillicoa Street
Asheville NC 28801
828/258-3939 Ext. 235
Bob_Butler@fws.gov
I am soliciting comments on the following draft guidelines on mollusk translocation projects (many of you have seen earlier drafts of these guidelines). Of particular interest are the genetic implications of mixing populations from different drainages (e.g., augmentation projects), and what researchers should do to prevent the swamping of resident populations. Please address your comments directly to me at the above address.
DRAFT GUIDELINES FOR MAINTAINING GENETIC INTEGRITY IN TRANSLOCATION EFFORTS FOR AQUATIC MOLLUSKS
Recent advances in propagation techniques are enabling researchers to potentially produce large numbers of juvenile mollusks in the lab. Concomitantly, water and habitat quality has improved at many riverine sites throughout the eastern United States. The coupling of propagation research advances and improvement in habitat conditions has enabled population augmentation and reintroduction efforts to become a reality.
Genetics research involving certain faunal groups (e.g., fishes) is continuing to indicate that many forms, particularly in the Southeast, that were formerly thought to be fairly wide-ranging species are actually complexes of species that have discreet distributions in specific stream/tributary systems and/or physiographic provinces. As many researchers know, there are numerous questions that must be answered regarding the taxonomic identity of aquatic molluscan forms as well (e.g., southern Atlantic Slope Elliptio, Pleurobema oviforme and Villosa iris complexes, certain pleurocerids). What follows are a set of preliminary guidelines to reduce the possibility of unnecessary and potentially deleterious mixing of genetic stocks in the wild when conducting population augmentation and reintroduction activities for aquatic mollusks.
I. Population Augmentation--adding individuals to an existing population
II. Reintroduction--returning individuals to historical habitat
Needs:
Establish or adopt an existing committee to more formally develop the following criteria:
A list of host species for rare freshwater mussels in Virginia
The following table was compiled by Cindy Schulz and Kim Marbain, Virginia Field Office, U.S. Fish and Wildlife Service, P.O. Box 99, Gloucester, VA 23061. If you have comments, additions, or deletions, please provide them to Cindy Schulz at (804) 693-6694 x127. Fax (804) 693-9032. E-mail cindy_schulz@fws.gov
HOST SPECIES FOR RARE FRESHWATER MUSSELS IN VIRGINIA
PREPARED BY U.S. FISH AND WILDLIFE SERVICE, VIRGINIA FIELD OFFICE
Last Revised: 1/5/98
| Freshwater Mussel | Host Fishes | References |
| Dwarf wedge mussel (Alasmidonta heterodon) | 1johnny darter (Etheostoma nigrum) 1mottled sculpin (Cottus bairdi) 2slimy sculpin (Cottus cognatus) 1tessellated darter (Etheostoma olmstedi) |
1Michaelson, D.L. and R.J. Neves. 1995. Life history and habitat of the endangered dwarf wedgemussel Alasmidonta heterodon (Bivalvia: Unionidae). J. N. Am. Benthol. Soc. 14(2):324-340. 2Dr. Barry Wicklow, St. Anselm College, NH |
| Elktoe (Alasmidonta marginata) | 1,2northern hogsucker (Hypentelium nigricans) 1,2shorthead redhorse (Moxostoma macrolepidotum) 1,2rock bass (Ambloplites rupestris) 1,2warmouth (Lepomis gulosus) 1,2white sucker (Catostomus commersoni) |
1Fuller, S.L.H. 1974. Clams and mussels (Mollusca:Bivalvia). In: C.W. Hart, Jr. and S.L.H. Fuller (eds.): Pollution Ecology of Freshwater Invertebrates. New York: Academic Press, pp. 215-273.
2Howard A.D. and B.J. Anson 1922. Phases in the parasitism of the Unionidae. J. Parasitology 9:68-82. |
| Brook floater (Alasmidonta varicosa) | 1blacknose dace (Rhinichthys atratulus) 1golden shiner (Notemigonus crysoleucas) 1longnose dace (Rhinichthys cataractae) 1margined madtom (Noturus insignis) 1pumpkinseed (Lepomis gibbosus) 1slimy sculpin (Cottus cognatus) 1yellow perch (Perca flavescens) |
1Dr. Barry Wicklow, St. Anselm College, NH |
| Birdwing pearlymussel (Conradilla caelata) | 1,2banded darter (Etheostoma zonale) 3snubnose darter (Etheostoma simoterum)
Possible hosts: |
1Hill, D.M. 1986. Cumberlandian Mollusk Conservation Program Activity 3: Identification of fish hosts. Tennessee Valley Authority Office of Natural Resources and Economic Development. 2U.S. Fish and Wildlife Service. 1983. Birdwing pearly mussel recovery plan. Atlanta, GA. 3Based on Brian Watson's M.S. Thesis (in preparation), VA Tech (R.J. Neves, VA Coop. Fish and Wildl. Res. Unit, pers. comm. 11/97). |
| Spectaclecase (Cumberlandia monodonta) | unknown | |
| Fanshell (Cyprogenia stegaria) | 1sculpin (Cottus carolinae) 1greenside darter (Etheostoma blennioides) |
1Based on Brian Watson s M.S. Thesis (in preparation), VA Tech (R.J. Neves, VA Coop. Fish and Wildl. Res. Unit, pers. comm. 12/5/97). |
| Dromedary pearlymussel (Dromus dromas) | 2fantail darter (Etheostoma flabellare)
Possible hosts: |
1Neves, R.J. 1991. Dromedary pearlymussel. Pages 292-294 in K. Terwilliger, ed. Virginia's Endangered Species, Proceedings of a Symposium. McDonald and Woodward Publishing Co., Blacksburg, VA.
2Watson, B.T. and R.J. Neves. 1998. Fish host identification for two federally endangered Unionids in the Upper Tennessee River drainage. Triannual Unionid Report No. 14. |
| Yellow lance (Elliptio lanceolata) | unknown | |
| Cumberlandian combshell (Epioblasma brevidens) | 1,2banded sculpin (Cottus carolinae) 1,2greenside darter (Etheostoma blennioides) 1,2logperch (Percina caprodes) 1,2redline darter (Etheostoma rufilineatum) 1spotted darter (Etheostoma maculatum) 1,2Tennessee snubnose darter (Etheostoma simoterum) 1,2wounded darter (Etheostoma vulneratum) |
1Yeager, B.L. 1987. Fish hosts for glochidia of Epioblasma brevidens, E. capsaeformis,and E. triquetra(Pelecypoda: Unionidae) from the upper Tennessee River drainage. Unpublished report on file with Office of Natural Resources and Economic Development, Tennessee Valley Authority, Norris, TN.
2Yeager B.L. and C.F. Saylor. 1995. Fish Hosts for Four Species of Freshwater Mussels (Pelecypoda:Unionidae) in the Upper Tennessee River Drainage. Amer. Midland Naturalist l33(1):1-6. |
| Oyster mussel (Epioblasma capsaeformis) | 1,2,3banded sculpin (Cottus carolinae) 1,2,3dusky darter (Percina sciera) 1,2,3redline darter (Etheostoma rufilineatum) 1,3spotted darter (Etheostoma maculatum) 2wounded darter (Etheostoma vulneratum) | 1Yeager, B.L. 1987. Fish hosts for glochidia of Epioblasma brevidens, E. capsaeformis, and E. triquetra (Pelecypoda: Unionidae) from the upper Tennessee River drainage. Unpublished report on file with Office of Natural Resources and Economic Development, Tennessee Valley Authority, Norris, TN.
2Yeager, B.L. and C.F. Saylor. 1995. Fish Hosts for Four Species of Freshwater Mussels (Pelecypoda:Unionidae) in the Upper Tennessee River Drainage. Amer. Midland Naturalist 131(1):1-6. 3Hill, D.M. 1986. Cumberlandian Mollusk Conservation Program Activity 3: Identification of fish hosts. Tennessee Valley Authority Office of Natural Resources and Economic Development. |
| Green-blossom pearlymussel (Epioblasma torulosa gubernaculum) | unknown | |
| Snuffbox mussel (Epioblasma triquetra) | 1,2,3banded sculpin (Cottus carolinae) 1,2,3logperch (Percina caprodes) 4blackside darter (Percina maculata) |
1Yeager, B.L. 1987. Fish hosts for glochidia of Epioblasma brevidens, E. capsaeformis,and E. triquetra (Pelecypoda:Unionidae) from the upper Tennessee River drainage. Unpublished report on file with Office of Natural Resources and Economic Development, Tennessee Valley Authority, Norris, TN.
2Yeager, B.L. and C.F. Saylor. 1995. Fish hosts for four species of freshwater mussels (Pelecypoda:Unionidae) in the Upper Tennessee River Drainage. Amer. Midland Naturalist 131(1):1-6. 3Hill, D.M. 1986. Cumberlandian Mollusk Conservation Program Activity 3: Identification of fish hosts. Tennessee Valley Authority Office of Natural Resources and Economic Development. 4Hillegass, K.R. and M.C. Hove. 1997. Suitable fish hosts for glochidia of three freshwater mussels: strange floater, ellipse, and snuffbox. Triannual Unionid Report No. 13. |
| Tan riffleshell (Epioblasma walkeri) | 1banded sculpin (Cottus carolinae) and/or mottled sculpin (Cottus bairdi) 1fantail darter (Etheostoma flabellare) 1greenside darter (Etheostoma blennioides) 1redline darter (Etheostoma rufilineatum) 1Tennessee snubnose darter (Etheostoma simoterum) |
1Based on work conducted by Brian Watson, graduate student at VA Tech (R.J. Neves, VA Coop. Fish and Wildl. Res. Unit, pers. comm. 7/23/96). |
| Shiny pigtoe (Fusconaia cor) | 1,2whitetail shiner (Cyprinella galactura)
Possible hosts: |
1Neves. R.J., F.X. O Beirn, G.S. Schurig, and G.S. Libey. 1996. Fish host and propagation studies of freshwater mussels in the upper Tennessee River Drainage, Virginia and Tennessee. 2Neves, R.J. 1991. Shiny pigtoe. Pages 272-274 in K. Terwilliger, ed. Virginia's Endangered Species, Proceedings of a Symposium. McDonald and Woodward Publishing Co., Blacksburg, VA. |
| Fine-rayed pigtoe (Fusconaia cuneolus) | 1central stoneroller (Campostoma anomalum) 1fathead minnow (Pimephales promelas) 1mottled sculpin (Cottus bairdi) 1river chub (Nocomis micropogon) 1telescope shiner (Notropis telescopus) 1Tennessee shiner (Notropis leuciodus) 1white shiner (Luxilus albeolus) 1whitetail shiner (Cyprinella galactura) |
1Bruenderman, S.A. 1989. Life history of the fine-rayed pigtoe pearly mussel, Fusconaia cuneolus (Lea 1840), in the upper Clinch River, Virginia. M.S. Thesis, Virginia Polytechnic Institute and State University, Blacksburg, VA. |
| Atlantic pigtoe (Fusconaia masoni) | Possible hosts: 1bluegill (Lepomis macrochirus) 1shield darter (Percina peltata) |
1Watters, G.T. and S.H. O'Dee. 1997. Identification of potential hosts. Triannual Unionid Report No. 13. |
| Cracking pearlymussel (Hemistena lata) | unknown | |
| Pink mucket pearlymussel (Lampsilis abrupta) | 1freshwater drum (Aplodinotus grunniens) 1sauger (Stizostedion canadense) 2largemouth bass (Micropterus salmoides) 2smallmouth bass (Micropterus dolomieu) 2spotted bass (Micropterus punctulatus) 2walleye (Stizostedion vitreum) |
1Virginia Department of Game and Inland Fisheries. 413196. Fish and Wildlife Information System. Richmond, VA.
2Barnhart, M.C., F.A. Riusech, and A.D. Roberts. 1997. Fish hosts of the federally endangered pink mucket, Lampsilis abrupta. Triannual Unionid Report No. 13. |
| Yellow lampmussel (Lampsilis cariosa) | ||
| Tennessee heelsplitter (Lasmigona holstonia) | 1banded sculpin (Cottus carolinae)
1rockbass (Ambloplites rupestris)
Possible hosts: |
1Steg, M.B. and R.J. Neves. 1997. Fish host identification for Virginia listed Unionids in the Upper Tennessee River Drainage. Triannual Unionid Report No. 13. |
| Green floater (Lasmigona subviridis) | unknown | |
| Slabside pearlymussel (Lexingtonia dolabelloides) | 2smallmouth bass (Micropterus dolomieu) Possible hosts: |
1Kitchel, H.E. 1985. Life history of the endangered shiny pigtoe pearly mussel, Fusconaia edgariana,in the North Fork Holston River. M.S. Thesis, Virginia Polytechnic Institute and State University, Blacksburg, VA. 2Neves, R.J., F.X. O Beirn, G.S. Schurig, and G.S. Libey. 1996. Fish host and propagation studies of freshwater mussels in the Upper Tennessee River Drainage, Virginia and Tennessee. |
| Virginia pigtoe (Lexingtonia subplana) | unknown | |
| Black sandshell (Ligumia recta) | 1largemouth bass (Micropterus salmoides) 1green sunfish (Lepomis cyanellus) 1redbreast sunfish (Lepomis auritus) 1rockbass (Ambloplites rupestris) 1white perch (Morone americana) 1yellow perch (Perca flavescens) 1platy (Xiphophorus maculatus) 1convict cichlid (Cichlasoma nigrofasciatum) |
1Steg, M.B. and R.J. Neves. 1997. Fish host identification for Virginia listed Unionids in the Upper Tennessee River Drainage. Triannual Unionid Report No. 13. |
| Little-wing pearlymussel (Pegias fabula) | Possible hosts: 1banded sculpin (Cottus carolinae) 1redline darter (Etheostoma ruflineatum) |
1Ahlstedt, S.A. 1986. A status survey of the little-wing pearly mussel Pegias fabula (Lea, 1838). Unpublished report on file with Endangered Species Field Office, United States Fish and Wildlife Service, Asheville, NC. |
| James River spiny mussel (Pleurobema collina) | 1blacknose dace (Rhinichthys atratulus) 1bluehead chub (Nocomis leptocephalus) 1central stoneroller (Campostoma anomalum) 1roseftn shiner (Lythrurus ardens) 1rosyside dace (Clinostomus funduloides) 1satinfin shiner (Cyprinella analostana) 1swallowtail shiner (Notropis procne) 1mountain redbelly dace (Phoxinus oreas) |
1Hove, M.C. and R.J. Neves. 1994. Life history of the endangered James spinymussel Pleurobema collina (Conrad, 1837)(Mollusca: Unionidae). Amer. Malacological Bulletin 11(1):29-40. |
| Tennessee clubshell (Pleurobema oviforme) | 1central stoneroller (Campostoma anomalum) 1common shiner (Luxilus cornutus) 1fantail darter (Etheostoma flabellare) 1river chub (Nocomis micropogon) 1telescope shiner (Notropis telescopus) 1Tennessee shiner (Notropis leuciodus) 1whitetail shiner (Cyprinella galactura) |
1Weaver, L.R., G.B. Pardue, and R.J. Neves. 1991. Reproductive biology and fish hosts of the Tennessee Clubshell Pleurobema oviforme (Mollusca: Unionidae) in Virginia. Amer. Midland Naturalist. 126:82-89. |
| Rough pigtoe (Pleurobema plenum) | Possible hosts: 1bluegill (Lepomis macrochirus) 1rosefin shiner (Lythrurus ardens) |
1Neves, R.J. 1991. Rough pigtoe. Pages 284-285 in K. Terwilliger, ed. Virginia's Endangered Species, Proceedings of a Symposium. McDonald and Woodward Publishing Co., Blacksburg, VA. |
| Pink pigtoe (Pleurobema pyramidatum) = Pyramid pigtoe (Pleurobema rubrum) | Possible hosts: 1bluegill (Lepomis macrochirus) 1rosefin shiner (Lythrurus ardens) |
1Neves, R.J. 1991. Pink pigtoe. Pages 285-286 in K. Terwilliger, ed. Virginia's Endangered Species, Proceedings of a Symposium. McDonald and Woodward Publishing Co., Blacksburg, VA. |
| Rough rabbitsfoot (Quadrula cylindrica strigillata) | 1bigeye chub (Hybopsis amblops) 1spotfin shiner (Cyprinella spiloptera) 1whitetail shiner (Cyprinella galactura) |
1Yeager, B.L. and R.J. Neves. 1986. Reproductive cycle and fish hosts of the Rabbit's foot mussel, Quadrula cylindrica strigillata (Mollusca:Unionidae) in the Upper Tennessee River Drainage. Amer. Midland Naturalist. 116(2):329-610. |
| Cumberland monkeyface pearlymussel (Quadrula intermedia) | 1,2blotched chub (Erimystax insignis) 1,2streamline chub (Erimystax dissimilis) |
1Hill, D.M. 1986. Cumberlandian Mollusk Conservation Program Activity 3: Identification of fish hosts. Tennessee Valley Authority Office of Natural Resources and Economic Development. 2Yeager, B.L. and C.F. Saylor. 1995. Fish hosts for Four Species of Freshwater Mussels (Pelecypoda: Unionidae) in the Upper Tennessee River Drainage. Amer. Midland Naturalist. 131(1):1-6. |
| Appalachian monkeyface pearlymussel (Quadrula sparsa) | unknown | |
| Purple lilliput (Toxolasma lividus) | 1,2green sunfish (Lepomis cyanellus) 1,2Longear sunfish (Lepomis megalotis) |
U.S. Fish and Wildlife Service. 1984. Pale lilliput pearly mussel recovery plan. Atlanta, GA. 2Hill, D.M. 1986. Cumberlandian Mollusk Conservation Program Activity 3: Identification of fish hosts. Tennessee Valley Authority Office of Natural Resources and Economic Development. |
| Rayed bean (Villosa fabalis) | ||
| Purple bean (Villosa perpurpurea) | 1banded sculpin (Cottus carolinae) and/or mottled sculpin (Cottus bairdi) 1fantail darter (Etheostoma flabellare) 1greenside darter (Etheostoma blennioides) |
1Based on work conducted by Brian Watson, graduate student at VA Tech (R.J. Neves, VA Coop. Fish and Wildl. Res. Unit, pers. comm. 7/23/96). |
| Cumberland bean (Villosa trabalis) | Possible hosts: 1fantail darter (Etheostoma flabellare) 1striped darter (Etheostoma virgatum) 1barcheek darter (Etheostoma obeyense) 1stripetail darter (Etheostoma kennicotti) |
1Based on work conducted by Jim Layzer at TN Tech (Leigh Ann McDougal, USFS, pers. comm. 11/6/97). |
VOLUME 30
MISSISSIPPI RIVER RESEARCH CONSORTIUM, INC.
30TH ANNUAL MEETING
23-24 APRIL 1998
YACHT CLUB RESORTS
LA CROSSE, WISCONSIN
visit our web site: http://www.emtc.usgs.gov/mrrc.html
PLATFORM PRESENTATION ABSTRACTS - ALPHABETICAL LISTING
Density, size, and age of the commercial unionid Megalonaias nervosa (Rafinesque 1820), in 277 miles of the Mississippi River, Reaches 9-19, Lansing - Fort Madison, Iowa, July - September 1997
Marian E. Havlik
Malacological Consultants, 1603 Mississippi Street, La Crosse, WI 54601-4969
In 1997 the Shell Exporters of America Inc. (SEA) sponsored the most extensive commercial unionid survey ever done. From 1 July -14 September we sampled the Mississippi River Mile 663.0-386.0, Reaches 9-12, 14-16, and 19, with emphasis on M. nervosa. Sites were identified by divers, malacologist, clammers, buyers, 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 made by Tennessee Shell, Camden, TN). One or 2 major, plus several minor sites, were sampled in most Reaches. Sylvan Slough Sanctuary, Moline, IL, was sampled in Reaches 15/16. 252 random timed dives were done starting near shorelines to determine a CPUE. 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 ranged from 2.7-7.6/ m2. Over 4800 living M. nervosa were measured and aged after being scrubbed with steel bristled brushes to remove Dreissena polymorpha debris. Few M. nervosa were fresh-dead from D. polymorpha. The weak age classes of young M. nervosa reported in 1986, were not real as evidenced by large numbers of 10-13 year old age classes. These strong age classes may also represent a response to the 1982-1986 Mississippi River die-off. In some areas 5-7 year age classes were also 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. 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 height (101.6 mm). The highest percentage of legal 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 have ever had the opportunity to observe unionid age and growth in such a long reach of a large river.
| REACH | LOCATION | # QUADS | #M.n. | #/m2 | TOT.LEGAL | TOT.Mn |
| 9 | Lynxville, WI | 101 | 192 | 7.6 | 2.08% | 1394 |
| 10 | Prairie du Chien | 69 | 65 | 3.77 | 10.77 | 526 |
| 11 | Platte River, WI | 130 | 88 | 2.71 | 10.23 | 823 |
| 12 | Dubuque, IA | - | - | - | - | 62 |
| 14 | Princeton, IA | 147 | 109 | 2.97 | 12.84 | 330 |
| 15 | Moline, IL | - | - | - | - | 245 |
|   | Sylvan Slough, IL | 82 | 76 | 3.71 | 18.42 | 611 |
| 19 | Ft. Madison, IA | 163 | 257 | 6.31 | 9.34 | 813 |
Physical and biological parameters and species composition of unionid mussels in the Wolf River, Western Tennessee
Kristin J. Pelizzal1,2 and Jack W. Grubaugh1
1Department of Biology, The University of Memphis, Memphis, TN 38152
2Environmental Analysis Branch, US Army Corps of Engineers, Memphis, TN 38103
The status of native unionid mussels in Tennessee is presently on the decline, with 75% of the reported species considered either endangered or threatened. The Wolf River, a primary Tennessee tributary to the lower Mississippi River, supports freshwater mussels, but little is known about the composition, abundance, or distribution of this community or critical abiotic parameters. We propose to initiate a study to examine the Wolf River mussel community at landscape, macrohabitat, and microhabitat scales in order to assess the relative influence of various abiotic factors on mussel distribution and growth. Qualitative sampling for species composition and distribution along the river gradient began in 1997; quantitative sampling to assess macro- and microhabitat parameters as well as mussel movement patterns will begin this year. This study is designed to provide information critical to assessing the present status and directing potential conservation and restoration efforts of freshwater mussels in the Wolf River.
POSTER PRESENTATION ABSTRACTS - ALPHABETICAL LISTING
Bioenergetic effects of zebra mussels on a larval fish: an experimental test of the trophic bottleneck hypothesis
Lynn A. Bartsch1, William B. Richardson1, and Mark B. Sandheinrich2
1U.S. Geological Survey, Upper Mississippi Science Center, La Crosse, WI 54602
2River Studies Center, University of Wisconsin, La Crosse, WI 54601
Large populations of zebra mussels Dreissena polymorpha have been shown to reduce water column plankton, including many types of phytoplankton and small bodied zooplankton (especially rotifers, Bosmina sp., and some Daphnia sp.). Coincidentally, these zooplankton are an important food source for larval fish. A common effect of zebra mussel colonization is an increased standing stock of many benthic invertebrates, including amphipods, isopods, chironomids, and ephemeropterans. These are the prey items required by many juvenile fishes. In a newly infested water body, one might expect a depletion of zooplankton and an enhancement of benthic macroinvertebrates in zebra mussel beds. As a result, larval fish could be at significant risk of starvation, while fish, able to reach juvenile stages, could accrue a significant benefit by feeding on enhanced benthic invertebrate populations. If such a trophic bottle neck exists for larval fish we would expect reduction in growth and the number of fish surviving their first year of life. However, those fish that do survive, may eventually exhibit elevated growth and survival rates. To examine potential effects of Dreissena on growth and timing of ontogenetic diet shifts in an early life stage of fish we conducted a 48-d outdoor mesocosm experiment. We used a 2X2 factorial design with 4 treatment combinations (3 replicates/treatment) including the presence or absence of Dreissena (0 or 5000/m2) and a larval fish Pimephales promelas, (0 or 350/ tank, age 1-d old). Gut contents showed that rotifers initially made up 50-90% of the diet; as fish grew, diet shifted more toward benthic micro- and macroinvertebrates. Cumulative population prey-consumption rates were significantly lower in the presence of zebra mussels than without zebra mussels (P=0.026, mean 157 versus. 92 g). Temporal patterns of prey consumption varied between the treatments: initially individual consumption and growth was lower in zebra mussel tanks. After day 20, as fish shifted to benthic prey, consumption and growth was highest with zebra mussels. The initial bioenergetic disadvantage incurred by the larval fish was later offset by increased availability of benthic prey in zebra mussel tanks. Ultimately, the final biomass and survival of fish with and without zebra mussels was not different. These results do support aspects of the trophic bottleneck hypothesis. The increased growth rates associated with the ontogenetic shift to benthic prey was predicted, the similarity in fish biomass and survival was not. The initial reduction in growth of fish in the presence of zebra mussels may place these larval fish at a disadvantage when faced with other stressors (e.g., chemical, thermal, or predation).
Upper Mississippi River and effects of predator exclusion cages
Michelle R. Bartsch, Lynn A. Bartsch, Steve J. Gutreuter
U.S. Geological Survey , Upper Mississippi Science Center, La Crosse, WI 54602
During 1997, we assessed the effects of predator exclusion cages on zebra mussels demographics in Navigation Pool 8 of the Upper Mississippi River. Concrete blocks were deployed from May 22 to October 29, 1997, at two sites, in two habitat types (main channel border and backwater) of the Upper Mississippi River. At each site, two blocks were deployed, one of which was enclosed in a cage (60 cm long X 31 cm wide X 31 cm high, mesh size 7.3 cm X 5.0 cm); the other block was uncaged. At the end of the 159-day colonization per