(n)=# fish infected |
Duration (days) |
Attached |
Recovered |
| Lampsilis reeviana brevicula(Strawberry River, AR) | |||
| Goldfish (1) | 14 | 2 | 0 |
| Common shiner (4) | 21 | 6 | 0 |
| Spotfin shiner (4) | 21 | 12 | 0 |
| Sand shiner(4) | 31 | 16 | 8 |
| Rosyface shiner (4) | 14 | 15 | 0 |
| White sucker (1) | 24 | 82 | 6 |
| Bluntnose minnow (4) | 28 | 49 | 8 |
| Northern hogsucker (1) | 26 | 7 | 0 |
| Siamese fighting fish (1) | 26 | 33 | 5 |
| Lavender gourami (1) | 26 | 57 | 24 |
| Longear sunfish (1) | 17 | 5 | 0 |
| Bluegill (1) | 26 | 125 | 7 |
| Pumpkinseed (1) | 31 | 382 | 337 |
| Rock bass (1) | 31 | 368 | 199 |
| White crappie (1) | 28 | 123 | 11 |
| Largemouth bass (1) | 31 | 501 | 288 |
| Greenside darter (1) | 12 | 24 | 0 |
| Banded darter (2) | 21 | 74 | 7 |
| Fantail darter(2) | 0 | 0 | 0 |
| Logperch (1) | 31 | 113 | 55 |
| Obliquaria reflexa(Muskingum River, OH) | |||
| Mottled sculpin (1) | 14 | 64 | 0 |
| White sucker (1) | 21 | 1284 | 0 |
| Bluntnose minnow (4) | 11 | 7 | 0 |
| Sand shiner (4) | 19X | 68 | 0 |
| Common shiner (4) | 19 | 21 | 1 |
| Whitetail shiner (4) | 19 | 71 | 0 |
| Spotfin shiner(4) | 0 | 0 | 0 |
| Fallfish(l) | 21 | 542 | 0 |
| Longnose dace (2) | 17 | 129 | 3 |
| Rosyface minnow (2) | 19 | 307 | 0 |
| Silverjaw minnow (4) | 17 | 26 | 2 |
| Stoneroller(4) | 20 | 5 | 0 |
| Largemouth bass (1) | 21 | 667 | 0 |
| White crappie (1) | 21 | 1065 | 0 |
| Bluegill (1) | 14 | 87 | 0 |
| Longear sunfish (1) | 14 | 318 | 0 |
| Variegate darter (1) | 19 | 41 | 0 |
| Banded darter (4) | 21 | 117 | 0 |
| Logperch (1) | 14 | 6 | 0 |
Non-parasitic life cycle in the green floater, Lasmigona subviridis(Conrad 1835)
Margaret L. Barfield
University of Georgia, 305 EHS Building, Athens, GA 30602
v:706-542-6076 f:706-542-7472 mbarfiel@flavor.fst.uga.edu
&
G. Thomas Watters
Ohio Biological Survey & Aquatic Ecology Laboratory
Ohio State University, 1314 Kinnear Rd., Columbus, OH 43212-1194
v: 614-292-6170 f: 614-292-0181 gwatters@postbox.acs.ohio-state.edu
The uncommon Green Floater was found to have transformed juveniles within the marsupia of females from two widely-separated populations. On March 29, 1998, one of us (MB) found juveniles in 17 of 24 individuals collected in Little River, a tributary of the Neuse River in North Carolina. Adults discharged all juveniles held in marsupia within one week of collection. On April 26, 1998, one of us (TW) found this species in Sideling Hill Creek, a tributary of the Susquehanna River in Pennsylvania. Only one gravid female was found, but it contained transformed juveniles as well. This female released juveniles for over a month after capture. No non-metamorphosed glochidia were found in either population. The juveniles from both sites are very active. SEM photographs show that the juveniles had deposited a small amount of new shell material before release.
This represents the first recent report of a non-parasitic life cycle in a North American unionid. Earlier reports of Strophitus undulatus(Say, 1817) and Utterbackia imbecillis(Say, 1829) transforming without a host have ever been substantiated; indeed, U. imbecillishas more potential hosts identified than any other unionid. Outside of North America, several South American mycetopodids and a Lake Tanganyikan unionid have been shown to bypass the parasitic stage.
We thank John Alderman, Judy Johnson (NC Wildlife Resource Commission) and Tom Proch (PA Dept. Environmental Protection) for help with this discovery.
Release of metamorphosed juveniles by the green floater, Lasmigona subviridis
William A. Lellis and Timothy L. King
U.S. Geological Survey, BRD, Wellsboro, PA 16901
U.S. Geological Survey, BRD, Kearneysville, WV 25430
lelliswmd@epix.net; tim_king@usgs.gov
Two years of laboratory-based reproductive and behavioral studies of the green floater Lasmigona subviridishave now been completed. Mussels were collected December 1996 through May 1998 from Pine Creek, Tioga County, Pennsylvania (tributary of the Susquehanna River) and held in 160 1 glass aquariums with white sand/gravel substrate. Tanks received approximately 1 1/min flow-through well water and were lit with overhead fluorescent lights. Temperature and photoperiod were adjusted throughout the year to match Pine Creek conditions. A current was maintained in each tank using a long rectangular airstone at one end. Mussels were fed twice daily with a mixture of cultured microalgae, pond detritus, and commercial algal products.
In 1997, several mussels released what appeared to be transformed juveniles between June 6-12 at 16.8-18.3oC. Expulsion was observed in one individual as a 3-step process: 1) with both apertures open, small numbers of individuals began spilling from the exhale aperture; 2) exhale aperture closed tightly, the mussel inhaled deeply sucking up most of the spilled juveniles; 3) inhale aperture shut, juveniles were expelled 20-30 cm into the water column from the exhale aperture. Release continued in short bursts at 4-5 min intervals for 2 hours. The apparent juveniles were spherical, measuring approximately 400 um in diameter, were toothed, and had a fully developed and active pedal foot. Photographs revealed that the juveniles remained closed during the expulsion process. Juveniles consumed algae and remained active for several weeks, often climbing solid structures found in the culture environment.
In 1998, release of juveniles again occurred between June 2-9 at 16.1-16.5oC. Material was released as small clumps, containing a single live transformed juvenile within 10-20 smaller particles that were believed to be either unfertilized eggs or underdeveloped glochidia. The particles had a darkened triangular appearance and were held together by sticky, translucent strands. DNA analysis of the juveniles confirmed their identity as Lasmigona subviridis. On June 15, a dead or dying adult was found that contained live, active, transformed juveniles in her marsupia.
To this date, no unmetamorphosed glochidia have been observed released from any adult, although this event could easily have been missed if occurring in mid-winter. Studies are continuing on the transformation process within the marsupia, identification of expelled materials, and ecology and culture of juveniles.
Measuring the degree of variation in the Wisconsin waterways mollusk Anodonta grandis
Abstract of Poster
Wisconsin Academy of Sciences, Arts & Letters Annual Conference May 2, 1998
Joan Jass and Jeanette Glenn
Invertebrate Zoology Section Milwaukee Public Museum, Milwaukee, Wisconsin 53233
Variation in the ubiquitous and abundant freshwater bivalve Anodonta grandis(giant floater) was studied using Milwaukee Public Museum specimens collected during a 1973 to 1977 statewide survey of Wisconsin rivers for unionid mollusks by collector H. Mathiak. For this study of intraspecific variation, data on six shell traits were gathered for each specimen: l ) beak sculpturing, 2) length overall, 3) height, 4) width, 5) anterior-to-beak length of the right valve, and 6) darkness of the periostracum. Variables 2-5 represent morphometric traits, while 1 and 6 represent continuous, nonnumeric traits which were assigned to numeric classes for analysis purposes. The resulting data were subsequently pooled into three Wisconsin regional groupings representing sites from the northeast, the southwest, and an intermediate tension zone. Comparison of the three groups revealed statistically significant differences and indicated a high degree of intraspecific variation. Northern region shells had a beak sculpture less consistently double-looped, widths, heights, lengths and anterior-to-beak measurements that were smaller, and a darker color than those in the southern group.
Setback hinders endangered mussel recovery
Roberta E. Hylton
U.S. Fish and Wildlife Service, Southwestern Virginia Field Office
PO Box 2345, Abingdon, VA 24212
(540) 623-1233
roberta_hylton@fws.gov
Efforts to recover endangered freshwater mussels suffered a tragic setback on August 27, 1998, when a tanker truck wreck spilled about 1,250 gallons of Octocure 554, a rubber accelerant, into the Clinch River at Cedar Bluff, Virginia. The spill resulted in the largest "take" of endangered species since passage of the Endangered Species Act in 1973. The Clinch River ran a snowy white color, the water filtration plant at Richlands, Virginia was shut down, and most aquatic organisms over at least a 6.6 mile stream reach were killed. Aquatic fauna killed included fish, aquatic insect larvae, snails, crayfish, turtles, and mussels. The Virginia Department of Environmental Quality reported a kill of approximately 3000-4000 fish. The spill devastated snail and mussel populations. Freshwater mussels from 17 species been killed by the spill. Biologists at the U.S. Fish and Wildlife Service's Southwestern Virginia Field Office have collected the remains of 242 endangered mussels killed by the spill--including the tan riffleshell, purple bean, and rough rabbitsfoot-- and approximately 6000 non-listed mussels. The Service and others working to protect and restore aquatic fauna of the upper Tennessee River basin fear the total number of individuals of listed and non-listed species killed is likely much higher. A storm event could resuspend particles that may have settled or precipated out in pools, potentially resulting in further die-offs of mussels and other aquatic fauna further downstream.
The Service, The Nature Conservancy, and others recognize the Clinch River as one of the most ecologically significant freshwater river systems in North America. Take of endangered tan riffleshells resulting from the spill represents a significant loss from the world's only known reproducing population of this species. Service biologists are working desperately to save remnants of this population that extend a short distance upstream into a tributary of the Clinch River. Efforts to protect the remaining "seed source" of tan riffleshell and recover the species include artificial propagation, augmentation of existing populations, and establishment of nonessential experimental populations in Tennessee's Hiwassee River. The Service also hopes to garner support in the State of Virginia to establish non-essential experimental populations there as well.
New unionid records for Coastal Matagorda County, Texas
Eric Nelson1, Bernard E. Sietman1, and Robert G. Howells2
1Ecological Specialists, Inc., 114 Algana Court, St. Peters, MO 63376;
Phone: 314-447-5355, Fax: 314-447-4101, BES E-mail: Ecologist3@aol.com
2Texas Parks and Wildlife Department, Heart of the Hills Research Station, HC07, Box 62, Ingram, TX 78025;
Phone: 830-866-3356, Fax: 830-866-3549, E-mail: rhowells@ktc.com
Ecological Specialists, Inc. surveyed for unionids in a small unnamed tributary of the Colorado River, Matagorda County, Texas on 7 April 1998. Specimens were subsequently sent to Texas Parks and Wildlife Department's Heart of the Hills Research Station for examination. Six unionid species and the Asian clam were collected in 8 hours of sampling; however, only one unionid was alive when taken (Table 1). Substrate in the tributary was primarily sand, silt, and soft mud. The stream channel and riparian vegetation were heavily disturbed from trampling by grazing cattle. All of the species are common and relatively widespread in Texas, and each represents a new record for Matagorda County (Howells et al., 1996).
Table 1. Bivalves collected in a tributary of the Colorado River, Matagorda County, Texas.
| Common Name | Species | |
| Tampico pearlymussel | Cyrtonaias tampicoensis | |
| Fragile papershell | Leptodea fragilis | |
| Yellow sandshell | Lampsilis teres | |
| Bleufer | Potamilus purpuatus | |
| Giant floater | Pyganodon grandis | |
| Texas liliput | Toxolasma texasensis | |
| Asian clam | Corbicula fluminea |
WD = Weathered dead
Literature Cited:
Howells, R.G., R.W. Neck, and H.D. Murray. 1996. Freshwater Mussels of Texas. Texas Parks and Wildlife Press, Austin. 218 pp.
Unio Gallery Website
Chris Barnhart
Department of Biology, Southwest Missouri State University, Springfield, MO 65804
417-836-5166
MCB095f@mail.smsu.edu
Conservation of endangered species requires public interest and support. Unfortunately, unionids lack the stage presence of eagles, wolves, or even little blue butterflies, and the uninitiated public may wonder why we are all so excited about a bunch of living rocks. Public interest can be enhanced by focus on the unionid life cycle. The interaction of mussels with fish is especially compelling, and adds color and intrigue to the story. Pictures of these phenomena are a great way to convince others that mussels are worth their attention.
The Unio Gallery is an Internet site presenting photographs of unionids and their life history stages. The purpose of the site is to give conservation professionals, educators, and other interested parties access to pictures for illustrating presentations. The images are JPEG files. They can be viewed on the Internet, but they can also be downloaded individually and entered into PowerPoint or other presentation software. They can then be used for electronic presentations, which are becoming increasingly popular, or they can be printed as 2x2 photographic slides and used with a traditional slide projector.
The Unio Gallery currently contains 61 images, mostly photographs that illustrate strategies for infecting fish hosts. Each page (group of 6-12 images) illustrates the adaptations of a particular species or genus. Each image is captioned with a brief explanation. I anticipate adding more pictures soon and I hope to add pages that illustrate other aspects of unionid biology, as well as reproduction.
If you would like to share your own photographs in this format, please contact me. I can scan your slides, or, if you scan your own, you can E-mail the JPEG files to me. Your name and copyright can be added to the pictures if you wish. Visit the Unio Gallery at the following URL: http://www.smsu.edu/mcb095f/gallery.
Release of Endangered Freshwater Mussels in 1998
Authors: Jess W. Jones and Richard J. Neves, VA Cooperative Fish and Wildlife Research Unit, Dept. of Fisheries and Wildlife Sciences, VA Tech, Blacksburg, VA 24061-0321, 540-231-5927
Research Sponsors: Tennessee Wildlife Resources Agency, U.S. Fish and Wildlife Service, U.S. Geological Survey, and Virginia Department of Game and Inland Fisheries Cooperating Agencies: Tennessee Valley Authonty, U.S. Army Corps of Engineers, U.S. Forest Service
Project Description: The Tennessee Wildlife Resources Agency has comrnitted funds to a 5 year project to produce culture, and release juvenile mussels of nwnerous endangered species into rivers of eastern Tennessee. The goal of this project is to augment natural reproduction in current populations and to release juvenile mussels into histonc habitat to expand the range of existing populations. Our inihal focus for the first 2 years will be the Clinch and Powell rivers where suff~cient suitable habitat exists to augment and re-establish the populations of rare mussels. The selection of species and release sites was determined by a joint meeting of mussel biologists representing the various funding and cooperating agencies. This is the first project of its kind in the United States, to implement recovery plans for each of these species using captive propagation.
Methods: Procedures for infestation of host fish were those of Zale and Neves (1982). Juvenile mussels were placed on a sand substrate, held in artificial streams, and fed cultured algae until a desired size was achieved. Most juvenile mussels were 1 month old when released into the wild, although ages ranged from 1 to 22 weeks. Results: In 1998, a total of over 35,000 endangered juvenile mussels of 6 species were released primarily into the Clinch River at 3 sites. Similar releases will occur annually for the next 4 years, and an evaluation of the success of the releases will be initiated in the year 2000. The following table is a summary of our juvenile production results:
| Mussel Species | Release Site | |
| fanshell Cyprogenia stegaria | 203 |
Clinch River at Horton Ford Clinch River at Wallens Bend |
| Cumberland combshell Epioblasma brevidens | 20 |
Clinch River at Horton Ford Clinch River at Wallens Bend |
| oyster mussel Epioblasma capsaeformis | 4,757 7,973 1,706 |
Clinch River at Horton Ford Clinch River at Wallens Bend Clinch River at Kyles Ford Powell River at Bales Ford |
| snuffbox Epioblasma triquetra | Clinch River at Horton Ford | |
| birdwing pearlymussel Lemiox rimosus | Clinch River at Wallens Bend | |
| cracking pearlymussel Hemistena lata | Clinch River at Sneedsville | |
Literature Cited: Zale, A.V. and R.J., Neves. 1982. Fish hosts of four species of lampsiline mussels (Mollusca: Unionidae) in Big Moccasin Creek. Canadian Journal of Zoology 60: 2535-2542.
Survey of mollusks in the upper-Conasauga River system inventory project
Please direct any questions to Paul Johnson
Southeast Aquatic Research Institute, 817-B North Market Street, Chattanooga TN 37405
Phone (423) 785-4074, pdj@tennis.org, http://www.sari.org/
Paul Johnson along with Ryan Evans and several other research interns have recently completed the summer component of a survey of the upper Conasauga River system for mussels and snails. Additional experience was lent to the task when Steve Ahlstedt (USGS), Leigh Ann McDougal (USFS), and Bob Butler (USFWS) participated in some of the field operations. This work is being supported by a contract from the U.S. Geological Survey's Species At Risk program. The overall goal of the project is to produce a database of both historical and contemporary distribution records for mollusks within the Conasauga River and its tributaries above the Georgia Highway 76 crossing just east of Dalton, Georgia. Survey results will be the basis of Mr. Evan's Master's research.
To date approximately 80% of the survey area has been examined. Historically the Conasauga River contained one of the densest and most diverse mussel faunas of any small river system in the world. However, although at least 40 species of freshwater mussels occurred in the watershed, Johnson's survey has only located 25 species. Furthermore, the apparent decline in the numbers of individual mussels is just as alarming. Historically, Some shoals in the Conasauga were reported to have mussel densities in excess of 50 mussels per square meter. This summer, the survey crew was only able to locate about 400 live mussels in the entire region they examined. Without recovery efforts many of the remaining mussel species within the Conasauga River system will almost certainly disappear.
The Conasauga mollusk survey is a critical component of the mussel propagation program underway at SARI because it is providing data that can help to identify where mussels might be successfully reintroduced. The survey work also allows founder stock to be located that can be used in SARI's propagation efforts. Results from the survey are being shared with other groups concerned with the health of the Conasauga, such as The Nature Conservancy, the Conasauga River Alliance, the U.S. Forest Service, U.S. Fish and Wildlife Service, and the USGS.
Construction phase of mussel and snail propagation projects completed
Please direct any questions to Paul Johnson
Southeast Aquatic Research Institute, 817-B North Market Street, Chattanooga TN 37405
Phone (423) 785-4074, pdj@tennis.org, http://www.sari.org/
The construction phases of SARI's mussel and snail propagation projects are virtually complete. Propagation and holding facilities have been constructed at both the Cohutta Fisheries Science Center, in Cohutta, Georgia and at the Tennessee Aquarium. Partially funded by a contract with the Jackson Office of the U.S. Fish and Wildlife Service, the snail propagation and rearing facilities consist of two raceways and one additional standing tank. The mussel propagation facilities were partially funded by a contract with the Asheville Office of the U.S. Fish and Wildlife Service, and because the mussel propagation work is relatively more elaborate these facilities are more extensive. This project when operation will focus on artificial propagation/restoration efforts with the upper Coosa River fauna. Angela Collier, an Environmental Science graduate student at UTC, and Paul Johnson designed and constructed much of the propagation facilities, with additional help and advice coming from the Aquarium's Maintenance and Husbandry departments. The mussel propagation work is expected to be the focus of Collier's Master's thesis research.
SARI to co-host First Symposium of the Freshwater Mollusk Conservation Society, March 17- 19, 1999
Please direct any questions to Paul Johnson
Southeast Aquatic Research Institute, 817-B North Market Street, Chattanooga TN 37405
Phone (423) 785-4074, pdj@tennis.org, http://www.sari.org/
Plans are underway for SARI and the Tennessee Aquarium to co-host the first symposium of the Freshwater Mollusk Conservation Society in Chattanooga, March 17-l9, l999. The symposium, Musseling in on Biodiversity, will interest biologists concerned with the status, distribution, regulation, management, and biology of unionid mussels - North America's most imperiled fauna. The symposium is expected to attract 250-300 attendees. In addition to the information exchange regarding freshwater mussels, a special session is planned that will focus on the biology and conservation of freshwater gastropods.
A local organizing committee consisting of Drs. Paul Johnson and George Benz (both SARI), Dr. John Jenkinson (TVA), and Steve Ahlstedt (USGS) has recently released a first call for papers. For more information about the meeting, please see the attached information and registration sheets in this issue of the Triannual Report.
New publication: 1998. Effects of temperature and chronic hypoxia on survivorship of the zebra mussel, Dreissena polymorpha,and Asian clam, Corbicula fluminea
Can. J. Fish. Aquat. Sci. 55: 1564-1572 (1998)
Paul D. Johnson and Robert F. McMahon
Abstract: We examined the effects of four levels of chronic hypoxic stress at three temperatures on the survivorship of Dreissena polymorphaand Corbicula fluminea to assess the efficacy of O2 deprivation as a macrofouling control treatment and examine if critical hypoxia limits support reported distribution patterns. At 25oC, the hypoxia tolerance was examined at PO2 = 7.9, 11.9, 15.9, 23.8, and 31.8 Torr (1 Torr = 133.322 Pa) or 5, 7.5, 10, 15, and 20% of full air O2 saturation (PO2 = 159 Torr). At 15oC, the hypoxia tolerance to 7.9, 11.9, and 15.9 Torr was tested and at 7.9 Torr for 5oC treatments. For both species, PO2 and temperature influenced survivorship dramatically with increasing survivorship at higher PO2 and decreasing temperatures. At 25oC, C. flumineaexperienced mortality at 7.9, 11.9, and 15.9 Torr, with LT50 values of 144, 216, and 216 h, respectively, versus 288, 384, and 480 h for the 15oC exposures. Dreissena polymorpha treatments had LT50 values of 120, 216, and 216 h at 25oC for the 7.9-, 11.9-, and 15.9-Torr treatments versus 26% mortality after 600 h and 28% mortality after 720 h at 15oC. The 7.9-Torr treatments at 5oC had LT50 values of 480 h for C. fluminea and 1056 h for D. polymorpha. This study showed that both species displayed broad seasonal variation in hypoxia tolerance and that hypoxia limits may be used to assess infestation risk.
New publication: 1998. Intraspecific life history variation in the threatened Louisiana pearlshell mussel, Margaritifera hembeli
PAUL D. JOHNSON* AND KENNETH M.BROWN Department of Biological Sciences, Louisiana State University, Baton Rauge, Louisiana 70803-1725, USA
Freshwater Biology (1998) 40, 317-330
SUMMARY
1. Margaritifera hembeliis a threatened mussel limited to twenty-two headwater streams in the Red River drainage in central Louisiana, USA. This study evaluated intraspecific variation in density, growth, size and age structure and shell morphology among several isolated populations. This study also identified the host fish and considered the role that host fish distribution played in determining mussel recruitment.
2. Mussels were aggregated in beds and average densities differed among streams. However, maximum mussel densities in beds were similar in all streams; the observed maxima were among the largest for monospecific mussel beds in North America, often exceeding 300 individuals m-2.
3. The maximum size reached by individuals differed among streams, but all size distributions were skewed towards larger individuals. A repeated measures analysis of tagged mussels in four populations, over a 2-year period, indicated 2-fold differences in growth rates among streams, and significant variation among years. Growth rates were not affected by local population density. Maximum ages reached, determined indirectly by comparing growth rates, varied from 45 to 75 years. A canonical discriminant analysis also revealed significant differences in shell morphology across populations.
4. Half of the populations showed evidence of recent recruitment, and these sites had fish assemblages dominated by the host fish Noturus phaeus(Taylor). Host fish abundance appeared more important than adult mussel density in explaining recruitment patterns.
5. Considerable intraspecific life history variation suggests that management strategies for this species should be stream-specific, with emphasis on ensuring long-term habitat stability.
Decline and extirpation of freshwater mussels in Little Black River, Missouri: There's still hope
Bruenderman, Sue A. and Alan C. Buchanan
Missouri Department of Conservation, Fisheries and Wildlife Research Center, 1110 S. College Avenue, Columbia, Missouri 65201
(573) 882-9880
bruens@mail.conservation.state.mo.us
buchaa@mail.conservation.state.mo.us
Qualitative timed-searches using snorkeling and waterscoping techniques were conducted in March and August, 1997 in the upper Little Black River, Ripley County, Missouri for the federally endangered Curtis pearlymussel, Epioblasma florentina curtisi(Utterback 1915). Nineteen freshwater mussel species were recorded from the survey reach in 27 person-hours of search time. In September, 1998, quantitative surveys (n=130, .25m2 quadrats) were conducted to compare with three previous quantitative surveys conducted at the same sites between 1980-1992. No Curtis pearlymussels were found during the study. Its absence in repeated surveys, and continued decline in species richness, abundance, recruitment, and excessive shell erosion in other associated naiad species during the past two decades indicate that the Curtis pearlymussel no longer exists in the upper Little Black River, Missouri. Problems identified in Little Black River, Missouri include chronic, elevated levels of fecal coliform bacteria in drinking water and excessive silt in the river bed. Potential sources of observed problems include inadequate treatment of human sewage, excessive nutrients from high densities of cattle and other domestic livestock, and poor land-use practices in this mostly-forested upper section of the watershed. Recent upgrades to the water treatment facility in the town of Grandin in the headwaters of the stream should correct some historical problems. Besides water quality problems, however, physical habitat in upper Little Black River is relatively stable compared to other Ozark streams in Missouri. Restoration will be difficult, but possible with a coordinated interagency, interdisciplinary, and public effort within the watershed. A population of the Curtis pearlymussel may still exist in Arkansas, which is a potential source of specimens for artificial propagation and the last hope for preserving this federally endangered species. Regardless of the outcome of the Curtis pearlymussel, the upper Little Black River still contains a relatively unique and diverse aquatic fauna worth saving. Recovery seems possible if actions are taken immediately to further identify and arrest problems in the watershed.
Commercial mussel harvest in Tennessee
Don Hubbs
P.O. Box 70, Camden, TN 38320
e-mail - TNMussels@aol.com
phone (901-584-8548)
The mussel shell harvest has been nearly non-existent since July, with none of the major companies openly purchasing shells. Commercial shell industry contacts speculate that next year will be as bad or worse for them as 1998. But as the industry is experiencing hard times, the resource is certainly benefiting from the decreased harvest activity.
Lack of commercial harvest activity has allowed TWRA mussel personnel to concentrate on survey work on the upper Kentucky Reservoir mussel beds. A new section 6 project has provided funding to locate habitat of endangered mussels, collect adults for propagation by Dr. James Layzer at Tenn. Tech. Co-op Fish Research Unit, and establish sites for population augmentation. Several endangered mussel species have been brought into the propagation program including: Lampsilis abrupta, Plethobasus cooperianus, Pleurobema plenum, & Cyprogenia stegaria. This reach of the Tennessee River below Pickwick Dam has areas of prime mussel habitat that have populations of common species at densities exceeding 100 mussels per square meter and evidence of recent recruitment of almost all species encountered.
TWRA will again be attempting to revise its commercial mussel regulations this winter. The Wildlife Resources Commission has shown increased interest in the commercial aspect of Tennessee's mussel program since the Federal investigation of the shell industry and its illegal harvest activities made headlines this past summer. TWRA is currently evaluating existing regulations in light information gained through the investigation. We hope to develop a program which benefits the legal harvester and gives more control over the resource to the TWRA.
New publication: The Freshwater Mussels of Tennessee
Paul W. Parmalee and Arthur E. Bogan

344 pages, with color plates, line drawings, and range maps
8" x 10" format
ISBN 1-57233-013-9
Price: $50.00, hardback
Special discounted price: $40.00
"The Freshwater Mussels of Tennessee . . . is indispensable to anyone, anywhere, working on this group. Parmalee and Bogan have written a work that sets the standard for future regional guides." - G. Thomas Watters, Ohio Biological Survey
With more than 150 species and subspecies recorded in the state, Tennessee has one of the most diverse freshwater mussel faunas in North America. Valuable as indicators of water quality, these mollusks have themselves become threatened as development encroaches on habitat-twenty-three are currently listed as endangered species and at least twelve have become extinct.
This book, the first of its kind for Tennessee, offers a comprehensive survey of this biologically and commercially significant group of mollusks. Its authors have been studying and writing about the mussels of Tennessee for more than twenty years and have undertaken a systematic organization of a large and complex body of information to bring order to a difficult field.
The book traces the long history of human exploitation of mussels, from aboriginal food gathering to the growth of the cultured pearl industry. It provides an interpretive context for its exhaustive species accounts with background material on biology, distribution, economic utilization, taxonomy, and conservation issues. The authors also review the life cycle of the mussel and describe its many remarkable traits, such as its shell formation and the strategies it employs during the larval stage in parasitizing fish.
The species accounts comprise 128 members of Family Unionidae-from pigtoes and pocketbooks to lilliputs and spikes-plus four additional species. The authors cover classification and synonymy, range and distribution, life history and ecology, and survival status. Particular attention is paid to shell description and structure to assist the reader in identification. Each species account includes a distribution map and color photos of two specimens.
The Freshwater Mussels of Tennessee is a major reference that encompasses historical and modern mussel collections and draws on conservation studies that span two centuries. It will stand as an authoritative guide to understanding Tennessee mollusks and as a benchmark in the study of these species worldwide.
The Authors: Paul W. Parmalee is professor emeritus of zooarchaeology and director emeritus of the McClung Museum at the University of Tennessee, Knoxville.
Arthur E. Bogan is curator of aquatic invertebrates at the North Carolina State Museum of Natural Sciences, Raleigh.
Add $3.50 for the first book ($4.50 for foreign orders) and $.75 for each additional book ($1.00 for foreign orders) to cover postage and handling. Illinois state residents add 8.75% sales tax; Tennessee residents add 8.25% sales tax. (Please remit in U.S. funds only.)
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Special concern mussels found in northern Minnesota watershed
Mark Hove, Jodi Gustafson, Jennifer Sieracki, Jennifer Kurth, Parnell Mahoney, Melissa
Tenpas & Susan Weller
Univ. of Minnesota, Bell Museum, 1980 Folwell Ave., St. Paul, MN 55108
(612) 624-3019, email address: Mark.Hove@fw.umn.edu
Very little survey work has been conducted in the Lake of the Woods drainage in northern Minnesota (Graf 1997). The Little Fork River, a subdrainage in the watershed, is 1,849 mi2 in size, nearly all of it flowing through the bed of Glacial Lake Agassiz. The Little Fork River, flows north, to the Rainy River; Minnesota's border with Canada. This watershed is relatively undisturbed when compared with the rest of the state. Pine and aspen forests cover much of the land in the basin, with a small number of ranches (Waters 1977).
Twenty-five sites within the Little Fork River watershed were surveyed using snorkeling equipment and SCUBA. Lampsilis siliquoidea was observed at nearly every site. Pyganodon grandis, Anodontoides ferussacianus,and Lampsilis cardiumwere observed at thirteen sites. Ligumia recta,a special concern species in Minnesota, were found at nearly half the sites. The other special concern species encountered, Lasmigona compressa,was observed at five sites distributed widely throughout the basin. Lasmigona complanataand Strophitus undulatuswere collected at six and two locations respectively. Live mussel densities ranged between 0.4-7 mussels/m2 in the Little Fork River (Figure 1).

Figure 1. Live mussel densities in the Little Fork River, Minnesota.
Financial and logistic support for this survey was provided by: the Minnesota Legislature, ML 1997 Chapter 216, Section 15, Subdivision 15b as recommended by the Legislative Commission on Minnesota Resources from the Minnesota Environmental and Natural Resources Trust Fund, University of Minnesota's Undergraduate Research Opportunities Program, Science Centrum, the James Ford Bell Museum of Natural History, and Chantel Cook, Jeremy Cable, Nancy Berlin, and Brenda Stauffer of the National Forest Service.
Literature Cited
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.
Quadrula fragosaexhibit unusual reproductive behaviors
Dave Heath1, Mark Hove2, Ronald Benjamin3, Mark Endris3, Rhonda Kenyon3, & Jennifer Kurth3
1 - WI DNR, 107 Sutliff Ave., Rhinelander, WI 54501. (715) 365-8979 HEATHD@dnr.state.wi.us
2 - Univ. of Minn., 1980 Folwell Ave. St. Paul, MN 55108. (612) 624-3019 Mark.Hove@fw.umn.edu
3 -WI DNR, 3550 Mormon Coulee Rd., La Crosse, WI 54601. (608) 785-9012 benjar@mail01.dnr.state.wi.us
This fall brings to an end the second of a three-year study to describe aspects of the largely unknown life history of the federally endangered, winged mapleleaf (Quadrula fragosa(Conrad, 1835)). Although this species once ranged throughout the upper Mississippi River watershed, it is now thought to occur only in the St. Croix River, bordering Wisconsin and Minnesota, and possibly in the Ouachita River, Arkansas (Posey et al. 1996). The winged mapleleaf was listed as federally endangered in 1991.
The objectives of this study include: (1) description of the brooding period and reproductive behavior, (2) identification of conchological and molecular characters of glochidia, and (3) determination of suitable glochidial hosts.
We used SCUBA to sample nine species of amblemines biweekly from May to November 1997 and April through October 1998. During fall 1998, winged mapleleaf were sampled every week. Winged mapleleaf glochidia were collected in 1997 and 1998 for use in the 2nd and 3rd objectives.
Unlike most amblemines, which brood glochidia during spring and summer, winged mapleleaf brood glochidia during a relatively short period in September and October (Table 1). In 1997, only a single gravid individual was observed. Unfortunately this animal released immature glochidia that were unusable for host suitability trials. Nineteen gravid individuals were observed in 1998. Demibranchs of gravid winged mapleleaf were usually only slightly swollen making non-lethal gravidity determinations difficult. Consistent with other amblimines, all four demibranchs served as marsupia. Four gravid individuals brought into the laboratory released a few to several conglutinates. Conglutinates were released individually and in groups. They were roughly 5 mm wide by 10 mm long and were slightly negatively buoyant. Glochidia were densely packed throughout the length of the white, thin conglutinates that tapered at both ends.
Table 1. Observed amblemine brooding periods in the St. Croix River.
| Species | '97 Brooding Period | '98 Brooding Period |
| Amblema plicata(Say, 1817) | ||
| Cyclonaias tuberculata(Raf., 1820) | ||
| Elliptio dilatata(Raf., 1820) | ||
| Fusconaia flava(Raf., 1820) | ||
| Pleurobema sintoxia(Raf., 1820) | ||
| Quadrula fragosa(Conrad, 1835) | ||
| Quadrula metanevra(Raf., 1820) | ||
| Quadrula p. pustulosa(Lea, 1831) | ||
| Tritogonia verrucosa(Raf., 1820) |
A surprising behavior exhibited by brooding and some non-brooding individuals was the presence of a swollen excurrent siphon. The siphon protruded approximately 10 mm from the shell margin, had black-ridged crenulations overlaying the gray mantle. Similarly swollen siphons and mantles were observed on other brooding amblemines.
Glochidia from four of five females that released in the laboratory were mature and used in vertebrate host suitability trials. Seventy-five host suitability trials were conducted (53 species tested). Although no winged mapleleaf juveniles have been observed, glochidia grew while attached to yellow, black, and brown bullheads, and channel and flathead catfish. Some glochidia nearly doubled in size. Glochidia remain attached to flathead catfish. To date. we have not identified a definitive host.
We will continue this study in 1999 to better describe the environmental variables surrounding the winged mapleleaf brooding period, conduct additional host suitability tests, and attempt to collect fishes naturally infested with winged mapleleaf glochidia.
We thank Bill Smith, Matt Christianson, Helen Kitchel, Robert Hay, Jim Burnham and Colin Dovichin of the WI DNR, Mike Davis, Susan Miller, Bonita Eliason and Missy Wipf of the MN DNR; Rick Hart of North Dakota State University; Jerry Spetzman of the MN DoA; Byron Karns of the U.S. National Park Service, Jennifer Seiracki, Shawn Strong, Michelle Lebeau and Melissa Tenpas of U. of MN, and Nick Rowse and Chuck Kjos, USFWS; Glenn Miller of the Great Lake Indian Fish & Wildlife Commission; Keith Patrick of Northern Ecological Services (NSA); and R. Maercklein for assistance. Funding for this study was provided by the federal aid under Section 6 of the Endangered Species Act of 1973 with matching funds from the Wisconsin Department of Natural Resources, Minnesota Department of Natural Resources and Minnesota Environmental and Natural Resources Trust Fund.
Literature Cited
Posey, W. R., J. L. Harris, and G. L. Harp. 1996. New distribution records for freshwater mussels in the Ouachita River, Arkansas. Proceedings Arkansas Acad. of Science 50: 96-98.
Hosts of salamander mussel, Simpsonaias ambigua,and snuffbox, Epioblasma triquetra,from the Meramec River system, Missouri
Chris Barnhart, Frank Riusech and Michael Baird
Department of Biology, Southwest Missouri State University, Springfield, MO 65804
417-836-5166, MCB095f@mail.smsu.edu
The salamander mussel is one of the most elusive and unusual unionids (Clarke 1985) and may be the only unionid that is an obligate parasite of an amphibian host. Howard (1915) collected naturally infected mudpuppies (Necturus maculosus)near Moline, Illinois on October 17. He maintained the hosts through the winter and observed excysted juveniles in late May of the following spring. Howard attributed the glochidia that he observed to Simpsonaias(formerly Hemilastena) ambiguaby comparison with glochidia later collected from gravid female mussels. However, it appears that no experimental infections were ever carried out. In the present study, salamander mussels were collected in August 1997 in the Meramec River. These individuals were not gravid at the time of collection and therefore were caged on site over the winter. A single gravid female was recovered on April 9 and subsequently used for host tests.
The glochidia of Simpsonaiastransformed on mudpuppies, but not on any of the 12 species of fish that were tested. Time from infection to excystment was 19-28 days (peak 23 days) at 20oC. The percent transformation success on Necturus was rather low; 13% of initially attached glochidia survived and transformed. The glochidia used for host tests were removed manually from the marsupia by flushing with sterile water from a syringe. However, the mussel subsequently released glochidia in what appeared to be a normal fashion. No conglutinates were evident. The glochidia bore prominent larval threads and were carried away from the female on the excurrent water flow in strands of threads and mucus similar to those produced by Utterbackia and other anodontines.
Snuffbox mussels were collected from the Bourbeuse River (Meramec system) in the summer and caged over the winter as described above. A gravid female was recovered on April 9. Snuffbox glochidia transformed on three of the 23 host species tested. Transformation occurred on logperch (Percina caprodes),blackspotted topminnow (Fundulus olivaceous),and Ozark sculpin (Cottus bairdii). Transformation time on logperch was 21 -27 days (peak 24 days) at 20oC. Hosts of E. triquetrahave been reported previously (Yeager and Saylor 1995, Hillegass and Hove 1997).
Literature Cited:
Clarke, A.H. The tribe Alasmidontini (Unionidae: Anodontinae), Part II: Lasmigonaand Simpsonaias. Smithsonian Contributions to Zoology 399: 1-75.
Hillegass, K.R. and M.C. Hove 1997. Suitable fish hosts for glochidia of three freshwater mussels: strange floater, ellipse, and snuffbox. Triannual Unionid Report 13:25.
Howard, A.D. 1915. Some exceptional cases of breeding among the Unionidae. Nautilus 29:4- 11.
Yeager, B.L. and C.F. Saylor. 1995. Fish hosts for four species of freshwater mussels (Pelecypoda: Unionidae) in the upper Tennessee River Drainage. American Midland Naturalist 133: 1-6.
Drum is host of the scaleshell, Leptodea leptodon
Chris Barnhart, Frank Riusech and Michael Baird
Department of Biology, Southwest Missouri State University, Springfield, MO 65804
417-836-5166, MCB095f@mail.smsu.edu
Scaleshell mussels were obtained from the Meramec River, Missouri in during surveys conducted by the Missouri Department of Conservation. Three females were gravid with early embryos on August 15, 1997. These individuals were caged on site over the winter, and recollected in April, at which time the glochidia were mature. Twenty-four fish and one amphibian species were tested as hosts by experimental infections, using fishes obtained primarily from Meramec tributaries. were tested. Transformation was observed only on drum (Aplodinotus grunniens),from which several thousand juveniles were recovered.
Transformation did not occur on the following species: common carp (Cyprinus carpio),striped shiner (Notropis chrysocephalus),central stoneroller (Campostoma anomalum),bleeding shiner (Notropis zonatus),bluntnose minnow (Pimephales notatus),Ozark minnow (Dioinda nubila),spotfin shiner (Notropis spilopterus),northern hogsucker (Hypentilium nigricans), slender madtom (Noturus exilis),checkered madtom (Noturus flavater),blackspotted topminnow (Fundulus olivaceous),northern studfish (Fundulus catenatus),longear sunfish (Lepomis megalotis),bluegill sunfish (Lepomis macrochirus),redear sunfish (Lepomis microlophus),smallmouth bass (Micropterus dolomieu),largemouth bass (Micropterus salmoides),logperch (Percina caprodes), Etheostoma blennioides(greenside darter), rainbow darter (Etheostoma caeruleum),Missouri saddled darter (Etheostoma euzonum),walleye (Stizostedion vitreum),Ozark sculpin (Cottus ozarkae),and mudpuppy (Necturus maculosus).
A regionwide status assessment of scaleshell recently concluded that the species is in serious decline, and that recruitment is evident only in the Meramec basin (Szymanski 1998). This decline contrasts with the use of a widespread and relatively common host. Recent genetic studies link the genus Leptodeaclosely with Potamilus(Roe and Lydeard 1997). Other Potamilusand Leptodeaspecies that have been investigated also utilize drum as host (e.g. Roe et al. 1997, Barnhart and Roberts 1997).
Literature Cited
Barnhart, M. C. and A.D. Roberts 1997. Reproduction and fish hosts of the fat pocketbook mussel, Potamilus capax.< Triannual Unionid Report 11:24.
Roe, K.J., A.W. Simons, and P. Hartfield 1997. Identification of a fish host of the inflated heelsplitter, Potamilus inflatus(Bivalvia: Unionida), with a description of its glochidium. American Midland Naturalist 138:48-54.
Roe, K.J. and C. Lydeard. 1997. Molecular systematics of the freshwater mussel genus Potamilus(Bivalvia: Unionida). Malacologia 39:195-205.
Szymanski, J. 1998. Leptodea leptodon(Scaleshell Mussel) Rangewide Status Assessment. U.S. Fish and Wildlife Service, Endangered Species Division, I Federal Drive, Ft. Snelling, MN.
The following abstracts were selected from presentations made at the 10th annual meeting of the St. Croix River Research Rendezvous. The meeting was held on October 20, 1998 at Marine on the St. Croix, and was sponsored by the Science Museum of Minnesota.
Mark Hove, Univ. of Minnesota, (612) 624-3019
Examination of mussel population and community stability at Interstate Park, St. Croix River
Daniel J. Hornbach, Melissa Kemperman, Valerie Kurth, Alicia Andersen, Leda Cunningham, Faith Hareldson, Ben Miller, and Phoebe Vanselow
Department of Biology, Macalester College, St. Paul, MN 55105
There are 40 species of freshwater mussels in the St. Croix River. The Nature Conservancy states that the St. Croix Watershed is critical for the conservation of the North American mussel fauna. Little is known about the population and community dynamics of freshwater mussels in the St. Croix despite its importance.
The Interstate Park area of the St. Croix River contains an abundant and diverse mussel assemblage. Two federally endangered species of mussel (the Higgins' Eye mussel and the winged mapleleaf mussel) are found in this area. This area is subjected to daily variations in water level because of the Northern States Hydroelectric Dam located at Taylor's Falls/St. Croix Falls. There has been some controversy concerning the most appropriate water release regime for this facility which would protect and enhance mussel habitat. This study was designed to continue a long-term monitoring program that may shed some light on the mussel population and community dynamics at this location.
We have quantitatively sampled (at least 100 0.25-m2 quadrats) this location in 1992, 1995 and again in 1998. After removing all of the substrate and mussels from the quadrats, we sieved the material to assess substrate size and U) collect all mussels. We were able to collect mussels <10 mm using this procedure. We identified and measured the shell length of all mussels and then returned them to the river. At each quadrat we also measured water depth and velocity.
We found significant decreases in both average mussel density and average species richness over this 6 year period. We found that there appeared to be strong young age classes in 1992 and an absence of another large reproductive output during this period. The decrease in mussel density, thus may be due to higher juvenile mortality. It is unknown whether the presence/absence of strong recruitment peaks is a 'natural' event or a response to habitat alterations.
Funding provided by The National Park Service - St. Croix National Scenic Riverway.
SUGGESTED READING:
Hornbach, D.J., J.G. March, T. Deneka, N.H. Troelstrup and J.A. Perry. 1996. Factors influencing the distribution and abundance of the endangered winged mapleleaf mussel, Quadrula fragosain the St. Croix River, Minnesota and Wisconsin. American Midland Naturalist 136: 278-286.
Physical microhabitat limitations of juvenile mussels
Melissa M. Kemperman and Daniel J. Hornbach
Macalester College, St. Paul, MN 55105
Since stability of a viable, multi-cohort mussel population depends on localized juvenile recruitment, conservation efforts must ensure that juvenile microhabitat requirements are met. Prior research in the St. Croix River found juvenile mussels clumped in non-adult locales, suggesting preferential microhabitat use. Despite appropriate food sources and minimum competition and predation, juveniles will not persist locally if water currents dislodge them from their attachment site. This study explores the physical limitations to juvenile settlement and persistence in the Sunrise River, a tributary of the St. Croix River.
We sampled fifteen sites along an area of high mussel density below Kost Dam, representing microhabitats of various flow, depth, and substrate type. A set of two settling samplers made of 11.4 cm diameter x 5.1 cm tall clear dishes was placed at each site during three time periods. Their contents were removed weekly to find newly-settled juveniles. Directly upstream and to the east and west sides of each set of settling samplers, Surber samplers were placed onto the substrate and the top portion of substrate loosened into the net to collect small juveniles. The rest of the sediment within a 0.09 m2 quad was excavated to collect larger mussels and to assess sediment size. Sediment from settling and Surber samplers was preserved in alcohol and juveniles searched under polarized light.
Adult densities were high but varied (102 (61 mussels/m2). This can be explained partly by negative effects of bottom flow (R2 = 0.225) and positive effects of depth (R2 = 0.198) and mean phi (R2 = 0.29). This indicates that adults are favored by sandier substrate and slower-flowing, deeper water. Surber and settling samplers are being processed to determine juvenile settlement rates and effects of sediment size distribution. Laboratory experimentation using a flume tank will investigate the effects of byssal thread strength, body shape and size, and substrate size on juveniles resistance to shear stress.
SUGGESTED READING:
Layzer, J. B. and L.M. Madison. 1995. Microhabitat use by freshwater mussels and recommendations for determining their instream flow needs. Regulated Rivers: Research and Management 10: 32945.
Neves, R. J. and J.C. Widlak. 1987. Habitat ecology of juvenile freshwater mussels (Bivalvia: Unionidae) in a headwater stream in Virginia. American Malacological Bulletin 5:1-7.
Effects of relocation on freshwater mussels
Leda A. Cunningham1, Daniel J. Hornbach1, Mark C. Hove2
1Dept. of Biology, Macalester College, St. Paul, MN, 55105,
2Dept. of Fisheries and Wildlife, University of Minnesota, St. Paul, MN, 55108.
Mussels are an important part of the St. Croix River system because they are biomonitors, indicators of habitat quality and stability, and because of the integral role they play in nutrient cycling. The St. Croix is home to 40 different species of freshwater mussels. Recent introduction of zebra mussels into the river and increasing construction of bridges and dams on the St. Croix make it necessary to study the effects of relocating mussels on the habitat into which they are moved and on the mussels themselves. This study explores these effects both qualitatively and quantitatively using two confined water sites on the St. Croix River. Beginning in July 1997, one 25m2 grid was laid down at Wild River State Park and another just upstream of where the Sunrise River joins the SL. Croix River. The grids were divided into five rows of five square meters (quadrats) and each quadrat was randomly assigned one of five different treatments. These were: Double Density, 78 mussels were added, , 10 Quadrula pustulosawere added, LC, 10 Lampsilis cardiumwere added, ED, 10 Elliptio dilatatawere added, and Control, where no manipulation of these quadrats occurred. All of the mussels of the three introduced species were obtained from the Sunrise (reference) site and relocated to the Wild River site. Using SCUBA, all mussels in each quadrat, alive and dead, were removed and brought onto the research vessel to be identified, weighed and measured for length. Mussels in all quadrats but the control were assigned a unique number that was etched into the mussel shell using a Dremel hand tool.
In August of 1998 the same procedure of mussel removal was followed as in 1997. Mussels found without a number were logged as "new", those numbers missing from the 1998 census were logged as "missing" and the rest were logged as "recovered", "control", or "dead" as applicable to their status. The data were analyzed using JMP. In the year-long study period, a total of 4531 mussels were catalogued, of which 40% were recovered, 32% were new, 12% were control (not given an identification number in 1997),12% were missing, and 4% were dead. There were comparable numbers of New, Recovered, Control, and Missing mussels between the two sites. However, there were almost twice as many dead mussels found at the Sunrise site (0.05%) compared to the Wild River site (0.03%), though mortality was low at both sites. The large number of new and missing mussels indicates movement out of and into the grid, a topic that is currently being studied. It appears that introduction of mussels into an existing mussel habitat does not adversely affect either the original or the relocated mussel populations on a short-term basis. We will continue to follow this relocation to further examine the efficacy of this procedure for populations threatened either by zebra mussel infestations or human interference.
Funding provided by the Minnesota Legislative Commission on Minnesota Resources.
SUGGESTED READING:
Cope, W.G. and D.L. Waller. 1995. An evaluation of freshwater mussel relocation as a conservation and management strategy. Regulated Rivers: Research and Management 11: 147-155.
Scanning electron microscopy of freshwater mussel larvae
Benjamin D. Miller and Daniel Hornbach
Department of Biology, Macalester College, St. Paul, MN 55105
The conservation of mussels requires an understanding of their dispersal by fish hosts; thus, successful species identification during their larval state is crucial. Limited data exists for the determination of a species from its larvae, or glochidia. The confident identification of glochidia has many useful applications in bivalve research. While general identification of subclasses, such as Ambleminae, may be possible using standard light microscopy, determination of the species level is unreliable by these methods.
Scanning electron microscopy (SEM ) may offer a reliable means to identify glochidia to species. SEM allows observation both qualitative and small but quantifiable differences in mussel valve structures.
In this study we used SEM, to examine glochidia from Quadrula metanevra, Q. pustulosa,and the federally endangered, winged mapleleaf mussel, Quadrula fragosa. Preliminary analysis of hinge and valve dimensions suggests that an accurate differentiation between species can be made using statistical methods. In addition to this quantitative analysis, qualitative examinations (pictures from the SEM) yield even better results. Although positive field identification of glochidial species is not yet possible; the methods used in this study offer a reliable means for identification in laboratory.
SUGGESTED READING:
Waller, D.L., Holland Bartels, L.E., and Mitchell, L.G. 1988. Morphology of glochidia of Lampsilis higginsi (Bivalvia: Unionidae) compared with three related species. American Malacological Bulletin, Vol 6, p. 3943.
Funding provided by the Wisconsin Department of Natural Resources.
Sublethal effects of emersion on three species of unionid mussels
Shari L. Greseth1, Ron G. Rada1, Diane L. Waller2, Michelle R. Bartsch2 and W. Gregory Cope3
1River Studies Center, University of Wisconsin-La Crosse, La Crosse, Wisconsin.
2 U.S. Geological Survey, Upper Mississippi Science Center, La Crosse, Wisconsin.
3Department of Toxicology, North Carolina State University, Raleigh, North Carolina.
Freshwater mussels are emersed (exposed to air) during conservation activities, such as status surveys, relocations and reintroductions. Success of these activities depends upon their ability to survive emersion and burrow into the substrate. Sublethal effects of emersion were determined by changes in energy reserves of mussels. Three species of unionid mussels (L. cardium, Q. pustulosa and E. dilatata) were acclimated in water at 25oC and exposed to five aerial temperatures (15 to 45oC) for 15, 30 or 60 min. After emersion, mussels were returned to water at 25oC. Burrowing and survival were observed for 14 d; mussels were then sacrificed and mantle tissue was analyzed for total lipid, carbohydrate, and protein content. All species demonstrated significant treatment effects on lipid content due to aerial exposure temperatures. Carbohydrate and protein content were not as sensitive. Carbohydrate content within the mantle tissue of Q. pustulosaand L. cardiumwas significantly affected by aerial temperature. Protein content within the mantle of Q. pustulosa was affected by duration of exposure.
SUGGESTED READING:
Cope, W. Gregory, and Diane L. Waller. 1995. Evaluation of freshwater mussel relocation as a conservation and management strategy. Regulated Rivers: Research and Management. Vol. 11, pp. 147-155.
Waller, Diane L., Jeffrey J. Rach, W. Gregory Cope, and Glenn A. Miller. 1995. Effects of handling and aerial exposure on the survival of unionid mussels. Journal of Freshwater Ecology. Vol. 10(3), pp. 199-207.
Where has Quadrula nodulata been hiding: A unionid mussel survey, Mississippi River Mile 820.0-821.6, lower Grey Cloud Island/Mail Channel, Cottage Grove, Minnesota
Marian E. Havlik
Malacological Consultants, La Crosse, Wisconsin
A unionid mussel (Mollusca: Bivalvia: Unionidae) survey was conducted September 1997 at the above site. During the first two random dives near Mississippi River Mile 820.0, each covering an area of about 3 X 15 m, yielded one Minnesota endangered Quadrula nodulata(Rafinesque 1820), wartyback, and one Minnesota threatened Tritogonia verrucosa(Rafinesque 1820), pistolgrip, among 130 living mussels (11 species). The latter specimen is probably the first living representative of T. verrucosafrom the Minnesota portion of the Upper Mississippi River in many years. Other random samples yielded five more wartybacks scattered throughout the study area including two found downstream of Lower Grey Cloud Island. Quantitative samples using 0.25 or 1.0 m2 quadrats (total 73.0 m2), yielded low densities (mean 1.41 mussels/m2), but included two additional wartybacks for a project total of 8. Q. nodulataeach representing a different age class (3,4,6,7,8,9,10,13 years). The CPUE for random dives was 1.5/minute.
Early 1900s literature indicates the host may be the channel catfish, flathead catfish, bluegill, or smallmouth bass (Fuller 1977). The wartybacks were unexpected since this species was not found alive in 1996 among 6,000 mussels we handled at Winona, Minnesota, nor among 13,000 mussels we handled at La Crosse, Wisconsin, and is nearly unknown from the St. Croix River. The pistolgrip was 11 years of age. Studies for the pistolgrip host fish have been done recently. A total of 738 living mussels (14 species) were measured and aged. Live mussels were in excellent condition with almost no erosion of the umbo even at 10-20 years of age. An additional 11 species were represented by empty shells; four were fresh-dead; seven were sub-fossil special status species, mostly from the LDB main channel border islands. Only one living Dreissena polymorpha(Pallas 1771), zebra mussel, was found attached to a Quadrula quadrula(Rafinesque 1820), mapleleaf. Improvements to sewage disposal plants in the Twin Cities area have apparently improved water quality to the extent that mussels have begun to re-populate the area around Lower Grey Cloud Island.
SUGGESTED READING:
Fuller, S.L.H. 1980b. Historical and current distribution of fresh-water mussels (Mollusca: Bivalvia: Unionidae) in the Upper Mississippi River. Pages 72-119 in J.L. Rasmussen, editor. Proceedings of the Symposium on Upper Mississippi River Bivalve Mollusks. Upper Mississippi River Conservation Committee, Rock Island, Illinois.
Havlik, M.E. 1985. A biotic index for naiad mollusks in the Upper Mississippi River System. 17th Mississippi River Research Consortium, Inc, April 1985, La Crosse, WI. Page 14.
Host and host attracting behaviors of five upper Mississippi River mussels
Mark C. Hove1, Jennifer E. Kurth1, Dave J. Heath2, Ronald L. Benjamin3, Mark B. Endris3, Rhonda L. Kenyon3, Anne R. Kapuscinski1, Katie R. Hillegass1, Tom W. Anderson1, Vanessa E. Pepit1, and Cindy J. Lee1
1University of Minnesota, Department of Fisheries and Wildlife, St. Paul, MN 55108. Email address: Mark.Hove@fw.umn.edu
2Wisconsin Department of Natural Resources, 107 Sutliff Avenue, Rhinelander, WI 54501. Email address: HEATHD@dnr.state.wi.us
2Wisconsin Department of Natural Resources, 3550 Mormon Coulee Road, La Crosse, WI 54601. Email address: benjar@mail01.dnr.state.wi.us
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 as an urgent research objective in the National Strategy for Freshwater Mussel Conservation. Suitable hosts were determined by artificially infesting various fishes and amphibians with glochidia from one of five mussel species. A fish was considered a suitable host when larval metamorphosis to the juvenile stage was observed. Observations of host attracting behavior were made in the laboratory and under natural conditions. Cumberlandia monodontareleased branched, white conglutinates held together in a clear, gelatinous matrix. Hosts have not been identified. Brooding female T. verrucosadisplayed a crenulate mantle, and release thin yellow conglutinates. Three-fold shell growth was observed on juveniles collected from yellow bullheads. Cyclonaias tuberculatadisplayed a slightly inflated mantle and released glochidia individually or together in a 1 x 3 cm conglutinate. Glochidial transformation was observed on four ictalurids. Brooding V. ellipsiformisdisplayed a small, light-sensitive, mantle flap with an eyespot. Glochidial transformation was observed in two cottids, four darters, and brook stickleback. Ligumia rectadisplayed a large, elaborate mantle and released 1 cm lanceolate, white conglutinates. Largemouth bass, bluegill, and walleye were suitable hosts for this species. Species-specific molecular markers are being developed for use in the identification of excysted juvenile mussels collected from naturally infested fish.
Mussel identification with PCR technology
Jesse D. Kroese, Premjit S. Deol, Zach D. Hayden, James G. Straka and Daniel J. Hornbach
Department of Biology, Macalester College, St. Paul, MN 55105
Freshwater mussels have an unusual life cycle that includes a period of parasitic encystment on fish hosts during their larval stage. Understanding these parasite-host interactions is integral to mussel conservation. Mussels in their larval form, however, are difficult to distinguish from one another. Polymerase chain reaction (PCR) technologies may be one way to distinguish between these larval forms.
This project seeks to facilitate identification of larval mussels in the St. Croix by creating a key for the genetic fingerprints of the 40 mussel species found in the river. In this process, foot tissue from adult specimens or whole glochidia are minced and DNA is extracted from the tissue following a standard phenol-chloroform extraction procedure. The extracted DNA is precipitated in a solution of ethanol/ammonium acetate, dried, and resuspended in water.
The ITS-1 region of rDNA is then amplified via polymerase chain reaction. Gene products are "cut" by several restriction endonucleases in order to detect differences in the DNA sequence of the ITS-I region. "Cut" and "uncut" DNA are applied to agarose gels and separated by size by passing an electric current through the gel (gel electrophoresis). Finally, gels are stained with ethidium bromide and DNA bands are visualized within the gels with UV light.
To date, DNA has been extracted from 20 of the St. Croix River mussel species including the federally endangered winged mapleleaf mussel, Quadrula fragosa. A promising number of inter-specific differences have been found. Preliminary data suggest that all 40 St. Croix River mussels can be distinguished with this method and that genetic fingerprinting though PCR may be a viable larval mussel identification tool in the near future.
Funding provided by the National Park Service, St. Croix National Scenic Riverway
SUGGESTED READING:
White, L.R., McPheron, B.A., and Jay R. Stauffer, Jr. 1996. Molecular Genetic Identification Tools for the Unionids of French Creek, Pennsylvania. Malacologia, 38(1-2): 181-202.
Effect of chlorpyrifos and acetylcholinesterase activities of the unionid mussel Amblema plicata plicata
W.J. Doran1, M.B. Sandheinrich1, R.G. Rada1, W.G. Cope2, D.L. Waller3, S.T. Cooper1.
1River Studies Center, University of Wisconsin--La Crosse, La Crosse, WI, 54601
2Department of Toxicology, North Carolina State University, Raleigh, NC 27695-7633
3Upper Mississippi Science Center, La Crosse, WI, 54602
Populations of freshwater mussels in North America have declined greatly over the past 30 years. Studies have demonstrated that effects of pesticides on freshwater mussels may be significant, especially in highly agricultural areas. Depletion of mussel populations in the Upper Mississippi River (UMR), for example, may have been partly caused by extensive use of organophosphorus compounds (OPs), such as chlorpyrifos. However, relatively little is known on sublethal effects of chlorpyrifos to native unionid mussels in the UMR. Amblema plicata plicatawere exposed in duplicate to a control and five concentrations of chlorpyrifos in flow-through aquaria with sand substrate. After 12, 24, and 96 h of exposure, the anterior adductor muscles of four randomly chosen mussels from each exposure chamber were analyzed for acetylcholinesterase activity, a bioindicator of exposure to OPs. After 12h of exposure, six randomly chosen mussels were removed, marked, and transferred to a flow-through tank containing clean water and sand. After 7 and 21 d of exposure to clean water, the anterior adductor muscles of three organisms from each treatment were analyzed for acetylcholinesterase recovery.
SUGGESTED READING: Fleming, W.J., T.P. Augspurger, and J.A Alderman. 1995. Freshwater mussel die-off attributed to anticholinesterase poisoning. Environ. Toxicol. Chem. 14: 877-879.
Moulton, C.A., W.J. Fleming, C.E. Purnell. 1996. Effects of two cholinesterase-inhibiting pesticides on freshwater mussels. Environ. Toxicol. Chem. 15: 131 - 137.
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