The fat threeridge (Amblema neislerii), the surprisingly common endangered mussel in the Apalachicola River, Florida.
Native freshwater mussels (Family: Unionidae) are the most 'endangered' organisms in North America; in January 2006 the U.S. Fish and Wildlife Service listed 70 species as threatened or endangered. Although some species are widely distributed throughout the central and eastern United States, many others are localized and found only in certain watersheds. For example, the fat threeridge mussel, Amblema neislerii (Lea, 1858), is now restricted to the Apalachicola River, Florida. Although results of surveys conducted during the 20th century suggest that this species was always rare in the river, our findings indicate that in moderately depositional areas near shore, A. neislerii is common-to-abundant and exhibits good evidence of recent recruitment. In 6 surveys between 1996 and 2003, divers and waders searched for mussels at approximately 100 sites in the 171-km-long river. Over 4,500 live mussels were collected and 19 species were identified. Amblema neislerii dominated the bivalve fauna at moderately depositional sites where it constituted approximately 36% of the fauna. Evidence of recent recruitment (live individuals less than 30 mm total shell length) was evident at many sites. This article examines the status of A. neislerii in the Apalachicola River based on a literature review and recent surveys.
Mejillones nativos de agua fresca son los organismos mas amenazados en Am6rica del Norte; en enero del 2006 el Servicio de Pesca y Vida Silvestre de EE.UU. listo 70 especies como amenazadas o en peligro. A pesar de que algunas especies estan ampliamente distribuidas por todo el centro y la parte este de los EE.UU., muchas otras estan localizadas y se encuentran solo en ciertos acuiferos. Por ejemplo, el mejillon Amblema neislerii (Lea, 1858) esta ahora restricto al Rio Apalachicola, Florida. Aunque los resultados de conteos realizados durante el siglo 20 sugieren que esta especie siempre rue rara en el rio nuestros resultados indican queen areas cerca de la orilla de deposicidn moderada, A.neislerii es de comun a abundante y hay buena evidencia de reclutamiento reciente. En 6 conteos de 1996 a 2003, buzos y vadeadores buscaron mejillones en aproximadamente 100 lugares en el estrecho de 171 km del rio. Mils de 4,500 mejillones vivos fueron recolectados y se identificaron 19 especies. Amblema neislerii domina la fauna bi-valvular en lugares de deposicion moderada, donde formaba parte del 36% de la fauna. Evidencia de reclutamiento reciente (individuos vivos de menos de 30mm de largo de concha) estaba presente en muchos de los lugares. Este articulo examina el estatus de A.neislerii en el Rio Apalachicola basado en una revisidn de la literatura y conteos recientes.
The Apalachicola River provides habitat for an endemic freshwater mussel (family: Unionidae) the fat threeridge, Amblema neislerii (Lea, 1858), which was listed as endangered on 15 April 1998. The decision to list this and 6 other mussel species in the Southeast was partially based on results of a status survey conducted at 324 sites in the Apalachicola-Chattahoochee-Flint (ACF) river basin and 77 sites along the Ochlockonee River Systems, southeast Alabama, southwest Georgia, and north Florida (Federal Register 63(50): 12664-12687). Jayne Brim Box and James D. Williams conducted the status survey in 199193 using scuba and snorkeling, and by handpicking in shallow water. These and other studies (Butler 1993) were synthesized for the Technical/Agency Draft Recovery Plan (Butler and Alam 1999) and for the Final Recovery Plan (Butler et al. 2003).
As of January 2006 the total number of federally listed threatened and endangered species was 1,272, which included 527 animals and 745 plants (US Fish and Wildlife Service 2006). When compared with charismatic species such as mammals and birds, concern has been expressed by some that invertebrates have been largely overlooked by the Endangered Species Act (ESA) (Kellert 1993; Opler 1987; Bean 1993; Murphy 1991; Hughes et al. 2000; Black et al. 2001). Regardless, of the 297 mussel species in the United States (Williams et al. 1993), 62 are endangered and 8 are threatened; therefore 24% have federal protection. Considering this comparatively high percentage, one could conclude that either native mussels are in serious trouble (Stansbery 1970; Fuller 1974; Master 1990; Bogan 1993; Seddon et al. 1998; Hayes 1998; Williams et al. 1993; Neves 1999; and Strayer et al. 2004) or they benefit from strong advocates (Yaffee 1982). Most likely, it is a combination of both.
Between 1996 and 2003 six mussel surveys were conducted in the Apalachicola River for the U.S. Army Engineer District, Mobile. These studies were designed to obtain information on distribution and abundance of federally listed mussels to avoid impacts of dredged material disposal. During this period nearly 211 hours were expended searching at approximately 100 sites in the 171-km-long river. As a result of these surveys and a critical review of previous papers on A. neislerii, it became apparent that this species is more common in the Apalachicola River than results of previous surveys would suggest. The purpose of this paper is to discuss survey results and the status of A. neislerii in the Apalachicola River. The other federally-listed mussel in the Apalachicola River is the purple bank climber, Elliptoideus sloatianus (Lea, 1840), listed as threatened on 15 April 1998.
The Apalachicola River, formed by the confluence of the Flint and Chattahoochee Rivers, originates at Navigation Mile (NM) 106.3, just south of Lake Seminole in the tailwater of Jim Woodruff Lock and Dam. This 171-km river is the largest in Florida with a mean annual flow of 690 [m.sup.3]/sec (Light et al. 1998). The Apalachicola-Chattahoochee-Flint (ACF) River Basin, in Georgia and northeastern Florida, drains approximately 210,448 hectares. The river enters the Apalachicola Bay at Apalachicola, Florida.
Jim Woodruff Dam is located at Navigation Mile 106.3 on the Apalachicola River and forms the Lake Seminole impoundment. Jim Woodruff Dam and Lake Seminole are operated as a run-of-the-river reservoir with the capability for only limited water storage. The tailwaters below Jim Woodruff Dam on the Apalachicola River are free-flowing and unobstructed, but can be affected by upstream reservoir operations and releases. The USACE allows basin outflows from Jim Woodruff Dam to approximately equal inflows from the upstream reservoirs in the basin except when upstream reservoirs are refilling. However, to avoid having discharge fall below 141.6 cms (minimum flow) during low flow periods, flows can be augmented by releases from Jim Woodruff Dam and/or other upstream reservoirs along the Chattahoochee River.
In 1875 the USACE was authorized to maintain a navigation channel in the Apalachicola River (U.S. Army Engineer District, Mobile 1987). In the early 20th century sediments were dredged from the main channel, oxbows, tributaries, and sloughs and placed on the floodplain within natural riverbanks. In the 1980s nearly 150 disposal areas were permitted throughout the river, although in any single year relatively few are used. Dredging was restricted to the main channel and material was only placed at specifically designated disposal areas primarily along shore in within-bank disposal sites. Although maintained for commercial navigation, commercial river traffic on the Apalachicola River in recent years has been light and has consisted mainly of recreational vessels. A number of factors have led to an unreliable navigation channel and the observed reduction in commercial navigation on the river, including recurrent drought conditions, dredged material capacity shortfalls, increasing restrictions on dredged material disposal, and funding limitations. The continued use of within-bank disposal areas has remained controversial within the State of Florida. However, mussel surveys have been conducted at all proposed within-bank disposal sites prior to their use in order to avoid impacts to threatened and endangered mussels or their habitat.
[FIGURE 2 OMITTED]
Most dredged material disposal areas are now located on erosional point bars, typically at a bend in the river so high flow redistributes sediments downriver. As is the case with all rivers, downriver of the erosional point bar is a zone of moderate sediment deposition. Concerning sediment deposition, the term 'moderate' is used to indicate that during low flow fine-grained sediments or silts will be deposited and gradually increase in depth. Moderately depositional areas are firm but muddy and will support benthic invertebrates such as mussels, snails, worms (oligochaeta) and dipterans (chironomidae). A period of high-velocity water will scour sediments and remove most of the smaller, short-lived fauna, although the site usually recolonizes quickly. Depending on conditions, these moderately depositional areas could scour several times a year, or simply maintain a dynamic equilibrium between erosion and deposition which is not detrimental to the fauna. Many shoals in large rivers such as the Ohio, Tennessee, and upper Mississippi that support dense and diverse mussel assemblages meet these latter criteria
Mussels were collected by 2-4 waders in shallow water and by 2 divers in water deeper than 1 m. Searches were timed and usually lasted 15-20 minutes. Collecting was done tactilely since underwater visibility was poor. Divers were equipped with a pneumofathometer to record water depth and were tethered to the boat with a 100-m line. All live mussels were taken to the boat or a station onshore and counted, identified, and returned to a location unlikely to be disturbed by future maintenance. Demographic data were obtained at a single site by collecting total substratum quantitative samples using a 0.25-[m.sup.2] quadrat (Miller and Payne 1993). Mussel taxonomy is consistent with Williams et al. (1993).
The major objective during most study years was to assess presence/ absence of threatened and endangered mussels in areas likely to be affected by dredged material disposal operations. In 1996, 1997, 1999, and 2002 these surveys were conducted immediately up-and downriver of 57 disposal areas. In 2001 searches were conducted immediately up- and downriver of 34 sloughs scheduled for maintenance dredging for ecosystem restoration. All sites were chosen by USACE and state environmental resource agency personnel and included both high quality benthic habitats as well as erosional zones not inhabited by live mussels or other benthic organisms.
A second objective was to analyze A. neislerii size demography, and abundance with respect to water depth at sites where this species was known to be common to abundant. These investigations were initiated to obtain a more complete understanding of this species in the Apalachicola River during low flow conditions. Population structure and evidence of recent recruitment were examined in 1999 by collecting quantitative total substratum samples using a 0.25-[m.sub.2] quadrat. Total shell length of each live A. neislerii was measured with digital calipers, and then it was returned to the river unharmed. These samples were taken from a moderately depositional area along the right descending bank of the Chipola Cutoff immediately downriver of the point where it exits the Apalachicola River at NM 41.7. As part of this objective, the distribution of A. neislerii with respect to water depth was investigated in November 2003 at 11 moderately depositional sites between NM 30.0 and 73.3. Transects perpendicular to shore were established that ran from shallow (0.6 m) to deep (2.7 m) water. At 0.3-m depth increments along each transect 2 divers searched for mussels for 15 minutes. A total of 100 timed searches were conducted. Gauge height and discharge at the nearest gauge near Blountstown, Florida (NM 78) was 1.11 m, 266.7 cms (18 Nov 03); 1.27 m, 291.7 cms (19 Nov 03); and 1.50 m 325.6 cms (20 Nov 03).
Data from the first objective, to search for endangered species at sites likely to be affected by dredged material disposal, are summarized in Table 1. More than 4,200 live mussels were collected at approximately 100 sites in the Apalachicola River. A. neislerii constituted 10% of the fauna and ranked 4th of 19 species. The most abundant species at these sites was Lampsilis teres (Rafinesque, 1820), which constituted 35.2% of the fauna. This species is usually common in sandy substratum in rivers, streams, and lakes throughout the Midwest (Cummings and Mayer 1992). Overall Collection per Unit Effort (CPUE; mussels collected per person hour) for all mussels was 21.9 and for A. neislerii was 2.2. As noted above, these sites included some where A. neislerii was common to abundant and others where virtually no benthic organisms were found.
It became apparent that freshwater mussels, including A. neislerii, were most abundant in moderately depositional areas often located 1-2 km or less downriver of point bars. Output from the CH3D-SED model (Raphelt and Alexander 2001) identifies areas of moderate sediment deposition downriver of point bars and disposal areas (Figure 3). A different impression of the relative abundance of A. neislerii emerges when collecting was restricted to moderately depositional sites (Objective 2). At 11 depositional sites (8 separate locations) A. neislerii ranked 1 of 12 and constituted 35.8% of the fauna. Average CPUE was 37.9 for all mussels and 13.6 for A. neislerii. CPUE ranged from 0.5 to 20.2 for A. neislerii and from 6.3 to 55.9 for total mussels on transects located perpendicular to shore (Figure 4). Total shell length varied from 30 to 90 mm with 12% less than 40 mm total shell length. Mussels were most abundant at a depth of 1.2 m. Mussels were virtually absent at water depths less than 1.2 m likely because of predation and aerial exposure. At depths greater than 2.7 m flow became erosional and few live mussels were found.
[FIGURES 3-4 OMITTED]
To investigate A. neislerii population demography, total substratum quantitative samples were taken at a moderately depositional site along the Chipola Cutoff where it connects with the Apalachicola River (approximate NM 41.7). CPUE for all mussels was 145, and A. neislerii was collected at the rate of nearly 90 per hour and constituted slightly more than 61% of the molluscan fauna, Total shell length ranged from 12.8 to 63.7 mm with good evidence of recent recruitment (Figure 5). We can only quantify the presence of small mussels, however, when total substratum samples were obtained. Mean density of A. neislerii was 27.2 individuals/m2, and mean density for all mussels was 34.8 individuals/m2.
[FIGURE 5 OMITTED]
The first published reference to A. neislerii in the ACF basin was by Hyning (1925) who considered this species to be 'rare.' He made this statement after receiving an unreported number of A. neislerii from the Chipola River that were given to him by a fisherman. Later van der Schalie (1940) summarized early mussel studies in the mainstem Chipola River and tributaries. He reported that A. neislerii was not found in tributaries but was collected at 2 sites in the Chipola River where it constituted 1.49% of the unionid fauna. Clench and Turner (1956) reported that A. neislerii was rare in the watershed, although when present it could be locally abundant. They considered it to be extinct in the upper Flint River where it had not been taken since the latter part of the previous century, although they did find some specimens in the lower Flint, Apalachicola, and Chipola Rivers. They reported that A. neislerii was 'amazingly abundant' in a natural impoundment in the lower Chipola River (referred to as Dead Lake) where 10-15 Crenodonta (=Amblema) neislerii could be found in "every square meter" along a 200-meter reach.
In a survey conducted for the Office of Endangered Species, Heard (1975) collected mussels at 150 locations in the Gulf and Southeastern States; 3 were in the Apalachicola and 4 were in the Chipola River. He collected live A. neislerii only in the lower Chipola River (Dead Lake). Heard (1975) reported no live A. neislerii in the Apalachicola River although he did find shells at I of 3 sites. He provided no information on sampling methods, intensity, or locations.
Richardson and Yokley (1996) collected mussels in the lower Apalachicola River using quantitative (6-0.25-m2 quadrats and total substratum removal) samples at each of 3 sites where adult A. neislerii or E. sloatianus had been found by previous investigators. Amblema neislerii was found at 1 of 3 sites (NM 21.8) where it constituted 25% of the assemblage. Three live organisms were smaller than 50 mm total shell length. Richardson and Yokley (1996) concluded that appropriate search methods (total substratum removal) would likely yield additional evidence of recent recruitment for A. neislerii in the Apalachicola River.
In 1991-92, Brim Box and Williams (2000) surveyed 324 sites in the ACF River Basin. They identified 33 species from a collection of 5,757 live individuals and 2,988 shells. Most sites were in the Chattahoochee and Flint Rivers upriver of Jim Woodruff Lock and Dam. In the Apalachicola River, Brim Box and Williams (2000) collected 32 live A. neislerii at 7 sites.
Early studies (Hyning 1925, van der Schalie 1940, Clench and Turner 1956, Heard 1975) give an impression that A. neislerii is rare in the ACF basin, but it is difficult to critically evaluate their results without knowing details of the surveys. It is also true that this species would accurately be described as common-to-abundant in the Apalachicola River but uncommon in the ACF Basin as a whole. Richardson and Yokley (1996) collected just 6 quantitative samples at a site in the Apalachicola River where they knew A. neislerii was present and reached conclusions similar to ours but different from previous workers. Over 200 hours were spent searching at approximately 100 sites in the Apalachicola River. Over 4,800 live mussels were processed and more than 600 live A. neislerii were collected. This is far more than any previous surveys, even those upon which the decision to list A. neislerii as endangered was based.
Amblema neislerii survives best in slightly depositional, low-flow reaches of medium-to-large sized rivers, and is less common in small streams. Therefore it was probably never common in the smaller Flint or Chipola Rivers. It is endemic to the ACF basin because it has been isolated from the Mississippi drainage by marine conditions to the south and physiography to the east, north, and west. It was concluded that A. neislerii is common to abundant at moderately depositional sites in the Apalachicola River. If earlier workers had access to powerboats and divers and conducted intensive and extensive surveys, they would likely have concluded that this species was common in the Apalachicola River and uncommon in smaller tributaries. An alternative hypothesis seems unlikely. It is difficult to believe that A. neislerii was previously uncommon in the Apalachicola River and that its abundance has greatly increased during the last 30 years.
These studies were initiated assuming that A. neislerii was extremely uncommon and that intensive field searches would be needed to find live specimens. However, results of these field studies indicated that this species is not in imminent danger of becoming extirpated in the Apalachicola River; conversely, in appropriate habitat it is abundant and exhibits good evidence of recent recruitment. In the Apalachicola River, A. neislerii could even be used as an indicator of good quality moderately depositional mussel habitat. The ESA provided protection and raised awareness of abundance and distribution of A. neislerii. A similar situation was noted for the endangered bivalve Potamilus capax in the St. Francis basin, Arkansas (Miller and Payne 2005).
Depending on need, the USACE has dredged along the Apalachicola River and has typically placed the dredged material near shore. Dredging impacts, water levels, commercial uses of the river, and protection of endangered species is central to coordination among conservation groups, navigation interests, and the USACE. A complete understanding of the distribution and abundance of A. neislerii is therefore critical to managing the waterway.
Studies were funded by the U.S. Army Engineer District, Mobile, Mobile, Alabama. The authors thank Will Green, Mark Farr, Naomi Van Tol, Donald R. Manning, and divrs from Tennessee Valley Authority and Mainstream Commercial Divers for field assistance. Joanne Brandt, U.S. Army Engineer District, Mobile provided financial and technical support for this project. The Chief of Engineers granted permission to publish this information.
Bean, M. J. 1993. Invertebrates and the Endangered Species Act. Wings. 17(2):12-15.
Black, S. H., Shepard, M., and M. M. Allen. 2001. Endangered Invertebrates: The Case for Greater Attention to Invertebrate Conservation. Endangered Species Update 18(2):41-49.
Bogan, A. E. 1993. Freshwater bivalve extinctions (Mollusca: Unionidae): a search for causes. American Zoologist 33:599-609.
Brim Box, J., and J.D. Williams. 2000. Unionid mollusks of the Apalachicola Basin in Alabama, Florida, and Georgia. Bulletin of the Alabama Museum of Natural History No. 22. 143 pp.
Butler, R.S. 1993. Results of a status survey for 8 freshwater mussels (Bivalvia: Unionidae) endemic to eastern gulf slope drainages of the Apalachicolan Region of southeast Alabama, southwest Georgia, and north Florida. Status Report Prepared by U.S. Fish and Wildlife Service, Jacksonville, FL.
Butler, R.S., and S.K. Alam. 1999. Technical/ Agency Draft Recovery Plan for endangered fat threeridge (Amblema neislerii), shinyrayed pocketbook (Lampsilis subangulata), Gulf moccasinshell (Medionidus penicillatus), Ochlockonee moccasinshell (Medionidus simpsonianus), oval pigtoe, and threatened Chipola slabshell (Elliptio chipolaensis), and purple bankclimber (Elliptoideus sloatianus). Prepared for Southeast Region, U.S. Fish and Wildlife Service, Atlanta, GA.
Butler, R.S., Ziewitz, J., Alam, S.K., and H.N. Blalock-Herod. 2003. Recovery Plan for endangered fat threeridge (Amblema neislerii), shinyrayed pocketbook (Lampsilis subangulata), Gulf moccasinshell (Medionidus penicillatus), Ochlockonee moccasinshell (Medionidus simpsonianus), oval pigtoe, and threatened Chipola slabshell (Elliptio chipolaensis), and purple bankclimber (Elliptoideus sloatianus). Prepared for the U.S. Fish and Wildlife Service, Southeast Region, Atlanta, GA.
Clench, W.J., and R.D. Turner. 1956. Freshwater mollusks of Alabama, Georgia, and Florida from the Escambia to the Suwannee River. Bulletin of the Florida State Museum, Biological Sciences 1(3):97-349.
Cummings, K.S., and C.A. Mayer. 1992. Field Guide to Freshwater Mussels of the Midwest. Illinois Natural History Survey, Manual 5. 194 pp.
Fuller, S. L. H. 1974. Clams and Mussels (Mollusca: Bivalvia). Pages 215-273 in C. W. Hart, Jr., and S. L. H. Fuller, editors. Pollution Ecology of Freshwater Invertebrates. Academic Press. New York, NY.
Hayes, T. 1998. Conservation of Native Freshwater Mussels: An Overview. Endangered Species Update 15(6):108-110.
Heard, W.H. 1975. Determination of the endangered status of freshwater clams of the Gulf and Southeastern States. Terminal Report for the Office of Endangered Species, Bureau of Sport Fisheries & Wildlife, U.S. Department of Interior (Contract 14-16-000-8905).
Hughes, J. B., Daily, G. C., and P. Ehrlich. 2000. Conservation of Insect diversity: A habitat approach. Conservation Biology 14:1788-1797.
Hyning, V.T. 1925. Amblema neisleri (Sic) nest located. The Nautilus 38(3):105.
Kellert, S. R. 1993. Values and Perceptions of Invertebrates. Conservation Biology 7(4):845-855.
Light, H.M, Darst, M.R., and J.W. Grubbs. 1998. Aquatic Habitats in Relation to River Flow in the Apalachicola River Floodplain, Florida. U.S. Geological Survey Professional Paper 1594. ISBN 0-607-89269-2.
Master, L. 1990. The imperiled status of North American aquatic animals. Biodiversity Network News 3:1-2, 7-8.
Miller, A. C., and B. S. Payne. 1993. Qualitative versus quantitative sampling to evaluate population and community characteristics at a large-river mussel bed. The American Midland Naturalist 130:133-145.
Miller, A. C., and B. S. Payne. 2005. The curious case of the fat pocketbook mussel, Potamilus capax. Endangered Species Update 22(2):61-70.
Murphy, D. D. 1991. Invertebrate Conservation. Pages 181-198 in K. A. Kohm, editor. Balancing on the Brink of Extinction: the Endangered Species Act and Lessons for the Future. Island Press. Washington, D.C.
Neves, R. J. 1999. Conservation and commerce: management of freshwater mussel (Bivalvia: Unionidae) resources in the United States. Malacologia 41(2), 461-474.
Opler, P. A. 1987. Invertebrate surveys in North America are necessary. Wings 12: 8-10.
Raphelt, N. K. and M. P. Alexander. 2001. Multidimensional Models in Rivers and Streams. Coastal and Hydraulics Engineering Technical Note CHETN-VII-2, U.S. Army Engineer Research and Development Center, Vicksburg, MS.
Richardson, T.D., and P. Yokley, Jr. 1996. A note on sampling technique and evidence of recruitment in freshwater mussels (Unionidae). Archiv fur Hydrobiologie 137(1):135-140.
Seddon, M. B., Killeen, I. J., Bouchet, P., and A. E. Bogan. 1998. Developing a strategy for molluscan conservation in the next century. Journal of Conchology Special Publication No. 2(1998): 295-298.
Stansbery, D. H. 1970. Eastern freshwater mollusks: (I) the Mississippi and St. Lawrence River Systems. Malacologia 10(1), 9-22.
Strayer, D. L., Downing, J. A., hag, W. R., King, T. L., Layzer, J. B., Newton, T. J., and S. J. Nichols. 2004. Changing perspectives on pearly mussels, North America's most imperiled animals. BioScience 54(5): 429-439.
US Army Engineer District, Mobile. 1987. Apalachicola-Chattahoochee-Flint Waterway Navigation Maintenance Plan. Mobile, AL.
US Fish and Wildlife Service. 2006. http://ecos.fws.gov/tess_public/servlet /gov.doi.tess_public.servlets.TESSBoxscore?forma=print&type=current&sysdate =12/17/2005
van der Schalie. H. 1940. The naiad fauna of the Chipola River, in northwestern Florida. Lloydia 3(3):191-206.
Williams, J.D., Warren, M.L., Jr., Cummins, K.S., Harris, J L., and R.J. Neves. 1993. Conservation status of freshwater mussels of the United States and Canada. Fisheries 18(9):6-22.
Yaffee, S.L. 1982. Prohibitive Policy, Implementing the Federal Endangered Species Act. MIT Press, Cambridge, MA.
Andrew C. Miller (1,2)
Barry S. Payne (1,3)
(1) Environmental Laboratory, U.S. Army Engineer Research and Development Center, Vicksburg, MS 39180-6199
Table 1. Summary of timed searches for mussels at disposal areas, slough mouths, or banks requiring maintenance in the Apalachicola River, Florida (1996, 1997, 1999, 2001, and 2002). Species % Abundance % Occurrence CPUE, hr A. neislerii 35.8 47 13.57 G. rotundata 32.36 55 12.26 L. teres 10.67 28 4.04 E. icterina 8.26 21 3.13 Q. infucata 4.13 14 1.57 E. complanata 2.75 7 1.04 P. grandis 2.75 9 1.04 M. nervosa 1.03 4 0.39 U. peggyae 0.86 4 0.33 T. paulus 0.69 4 0.26 E. crassidens 0.34 2 0.13 V. lienosa 0.34 2 0.13 Total collections 100 Total individuals 581 Total species 12 Time, hr 15.3 CPUE, Catch per person hour 37.9 Table 2. Summary of results from timed searches at multiple depths (0.3 - 2 m) at 11 locations along the mainstem Apalachicola River, November 2003. Species % Abundance % Occurrence CPUE Lampsilis teres 35.22 58.3 7.7 Glebula rotundata 23.81 46.9 5.2 Elliptio icterina 14.48 22.9 3.16 Amblema neislerii 10 22.9 2.19 Quincuncina infucata 2.76 22.9 0.60 Elliptio crassidens 1.64 16.7 0.36 Megalonaias nervosa 1.55 15.6 0.34 Elliptoideus sloatianus 1.69 9.4 0.37 Pyganodon grandis 1.31 19.8 0.29 Elliptio complanata 6.12 15.6 1.34 Toxolasma paulus 0.40 8.3 0.09 Utterbackia imbecillis 0.21 6.3 0.05 Villosa villosa 0.19 3.1 0.04 Pyganodon cataracta 0.16 3.1 0.04 Uniomerus caroliniana 0.12 3.1 0.03 Elliptio ardata 0.19 3.1 0.04 Utterbackia peggyae 0.07 2.1 0.02 Pyganodon heardi 0.05 2.1 0.01 Latnpsilis claibornensis 0.05 2.1 0.01 Total locations 96 Total individuals 4,268 Total species 19 Time, hr 195.3 CPUE, Catch perperson hour 219
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|Author:||Miller, Andrew C.; Payne, Barry S.|
|Publication:||Endangered Species Update|
|Date:||Jan 1, 2006|
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