Freshwater Mussels and Clams

A Natural History of the Unionidae Mussels

of the Lower Susquehanna River Watershed

Including Commentary on Other Native and Non-native Bivalve Mollusks 

 SUMMARY

Historical records, particularly those of local malacologist Samuel Steman Haldeman (1812-1880), indicate nine species of native Unionidae bivalves, commonly known as river mussels, have occurred in the waters of the Lower Susquehanna River Watershed in Pennsylvania.  One of the nine species, Alasmidonta heterodon, is likely extirpated.  Another, Lampsilis radiata, is seriously diminished in range—a fragmented population surviving mostly downriver of Pennsylvania in tidal freshwater areas near the mouth of the Susquehanna in Maryland.  Two additional species of unionids, Anodonta implicata and Leptodea ochracea, favor these same tidal waters and occur in the Susquehanna basin only in Maryland.

In the Lower Susquehanna River Watershed, Unionidae communities are comprised of these ten surviving species—Alasmidonta marginata susquehannae, Alasmidonta undulata, Anodonta implicata, Elliptio complanata, Lampsilis cariosa, Lampsilis radiata, Lasmigona subviridis, Leptodea ochracea, Pyganodon cataracta, and Strophitus undulatus.  Since 1980, an additional species, Alasmidonta varicosa, has been reported in small numbers, but exclusively outside of Lancaster County.  It may have escaped the notice of Haldeman and other nineteenth-century naturalists who conducted the majority of their surveying along the river in Lancaster County and in nearby areas on the east side of the Susquehanna.  Anodontoides ferussacianus and Villosa iris have also been reported during the years since 1980, though the status and origins of these species are as yet undetermined.  Their arrival as native transplants, particularly as larval parasites on stocked fish, is suspected.  The latter species, Villosa iris, appears to be reproducing.

The river mussels are widely regarded to be the most imperiled family of animals in North America.  Improved interest in populations of Unionidae bivalves throughout the Lower Susquehanna River Watershed has led to better monitoring of the surviving species and increased concern for their habitat—our waterways.


All Unionidae mussels occurring in Pennsylvania and Maryland are now protected species and may not be collected or harvested.


INTRODUCTION TO THE UNIONIDAE

The Unionidae are a family of large freshwater bivalve mollusks often known as river mussels.  Adults of all species exceed one inch in length.  In some species, older specimens, often decades in age, can be six or more inches in length.  Two valves, comprised mostly of calcium carbonate, form the protective outer shell.  The inner surface of the shell is covered with a thin surface called the nacre.  The color of the iridescent nacre is often a key to species identification.  Viewed on the exterior, the valves are joined dorsally near a forward directed beak or umbo.  Unionids spend much of their time partially buried in the substratum.  The beak of each valve is often worn and white because it is the only portion of the animal exposed to abrasive materials in the current.  In some species, a posterior ridge extends from the beak to the posterior-ventral corner of the valves.  Internally, the valves often have protruding pseudocardinal hinge teeth anterior to the beak and long thin lateral hinge teeth extending toward the posterior.

Lampsilis cariosa
A Yellow Lampmussel (Lampsilis cariosa) as unionids are most often seen, with the worn beaks of the shell showing above the substrate.  (Vintage 35mm image)
Topography of a Unionid Shell
Shell topography of a Unionidae mussel.  (United States Fish and Wildlife Service image by Ryan Hagerty and Kristin Simanek)
Aging a Unionid Mussel
Growth rings on the shell of a river mussel can be used to estimate its age, just like the rings on a tree. This rather young Yellow Lampmussel (Lampsilis carosa) is in at least its eleventh year.  Some unionids have reportedly lived for seventy years or more.  (Vintage 35 mm base image)

The Unionidae exhibit slow locomotion using a soft “foot” extended ventrally toward the anterior end of the open valves.  To the posterior they exchange water through the incurrent and excurrent apertures, also known as the inhalant and exhalant siphons.  Motion of the internal gills provides respiration and the transfer of food, plankton, and organic detritus, to the labial palps.

Anatomy of a Unionid Mussel
Anatomy of a Unionidae mussel.  (United States Fish and Wildlife Service image by Kristin Simanek)
Alasmidonta marginata susquehannae
Alasmidonta marginata susquehannae, the Susquehanna Elktoe, is renowned for digging its foot deep into the substrate to anchor itself in strong current.  (Vintage 35mm image)

The eggs of the female are fertilized in the gills with sperm pumped in through the incurrent aperture.  After hatching, the larvae, known as glochidia, are brooded in the gills.  Upon being released by the female, glochidia must quickly become attached to the gills or fins of a preferred species of host fish to survive.  Some species of unionids expel their glochidia to the stream bottom.  In the case of others, a portion of the female’s body resembling a prey species favored by the host fish is displayed outside the shell like a lure.  When a potential host is attracted, glochidia are ejected by the female mussel so that they might be inhaled during respiration by the host fish and trapped in its gills.  Successful glochidia encyst on the host for about two to four weeks, causing little if any harm.  The parasitic stage of their life cycle complete, they detach and begin life in the substate as juvenile mussels.

Gills of a Gravid River Mussel
The inflated outer gill of this dissected female Lampsilis mussel is indicative of glochidia brooding.  (United States Fish and Wildlife Service image by Mathew Patterson)
Unionid Glochidia
Glochidia of the Eastern Elliptio (Elliptio complanata) under magnification (actual size about 0.2 mm in diameter).  (United States Geological Survey image by Heather Galbraith)
Lampsilis with Lures Deployed
A gravid female Yellow Lampmussel (Lampsilis cariosa) attempting to lure a host fish for its parasitic glochidia by displaying appendages that resemble a small eel or other fish.  (United States Geological Survey image by Jeffrey C, Cole)
Glochidia Encysted on Eel Gills
The parasitic glochidia of an Eastern Elliptio on the gills of its host fish, the American Eel (Anguilla rostrata).  The encysted larvae will hitch a ride for about two to four weeks, then disembark as juvenile mussels.  (United States Geological Survey image)

Those glochidia that break free in suitable benthic habitat stand the best chance of survival.  Where fish movements are unencumbered, the life cycle of a unionid mussel enhances its ability to remain widely distributed in favorable waters throughout a watershed.  Detrimentally, the life cycle can place limits on the success of reproduction in impaired streams, where glochidia can break free and become buried in silt or other unfavorable substrate.

Juvenile Unionidae
Juvenile river mussels under magnification.  (United States Fish and Wildlife Service image by Ryan Hagerty)

Juvenile unionids that survive the larval stage of their life cycle spend the remainder of their lives in a small geographic area, growing slowly while filtering the nourishment they need from the water column.  Collectively, healthy populations of river mussels and other bivalves purify massive volumes of water, effectively reducing turbidity and sequestering nutrients in the streams, rivers, lakes, and ponds they inhabit.  In the Lower Susquehanna River Watershed, restoration of communities of native freshwater mussels and clams can help improve water quality for both human use and aquatic life alike.  Cleaner water here extends its benefits downstream to Chesapeake Bay, home to important fish nurseries and troubled populations of a well-known and very popular bivalve—the Eastern Oyster (Crassostrea virginica).

The Eastern Oyster (Crassostrea virginica) lives in the tidal waters of middle and lower Chesapeake Bay
The Eastern Oyster (Crassostrea virginica) lives in the tidal waters of middle and lower Chesapeake Bay.  (National Oceanic and Atmospheric Administration image)

THREATS TO THE UNIONIDAE

All native freshwater bivalves—our mussels and clams—are particularly susceptible to habitat and water quality degradation.  As a family, the Unionidae are probably the most threatened animals in North America.  In the Lower Susquehanna River Watershed, they are seriously diminished in numbers or are absent from streams affected by one or more of the numerous impairment factors that besiege them

MECHANICAL ALTERATION OF STREAM CORRIDORS

Mechanical alterations to stream bottoms and floodplains can negatively impact populations of freshwater mussels.  There are several undertakings that are, or were, particularly devastating.

Man-made dams, first those constructed for milling operations, then those built for recreation lakes and hydroelectric energy production, have seriously reduced mussel and clam populations in the Lower Susquehanna River Watershed.  Silt and sediment accumulations behind dams often bury suitable substrate for a mile or more upstream of the impounding structure, rendering the bottom of the waterway uninhabitable for bivalves and the many other forms of benthic life that thrive in sand and gravel.  After detaching from their host fish, young unionids are particularly susceptible to being buried in silt.  Adult mussels find the muddy bottoms of mill ponds and other impoundments inhospitable as well.  Because they rely on a host fish to nourish and distribute their parasitic larvae (glochidia), unionids are especially sensitive to the limitations on fish movements created by man-made dams.  When dams impede the migrations and other seasonal travels of host fish carrying larval glochidia, contraction and fragmentation of the mussel species’ geographic range can result.  In the absence of a suitable substitute fish, loss of a host fish species can lead to the disappearance of any river mussel that relies on it for larval development.

Red Hill Dam
Man-made dams on the Susquehanna and its tributaries trap accumulations of silt and sediment destroying habitat for river mussels and other benthic life.  These structures also block the migrations of anadromous and catadromous fishes and the seasonal movements of resident species including hosts critical to the survival and distribution of young unionid bivalves.  (Vintage 35mm image)

Dredging of sections of the lower Susquehanna for spilled, discarded, and washed-out anthracite coal sediment went on for nearly 100 years and was a particularly active enterprise in the Harrisburg area and in Lake Clarke below Chickies Rock until 1973.  The repeated benthic disturbances that accompanied waste coal recovery in these segments of the river may have been the catastrophic factor leading to the demise of Eastern Lampmussel (Lampsilis radiata) and Dwarf Wedgemussel (Alasmidonta heterodon) populations there.

Stream channelization is mechanical modification to stream geomorphology that destroys both fish and river mussel populations by negatively altering substrate composition, water quality parameters, and flow characteristics during periods of both high and low water.  In the lower Susquehanna valley, the naturally occurring dynamic of a multi-channeled stream meandering through a floodplain of vegetated wetlands is seldom tolerated.  Though misguided, channelization is the favored “remedy”, despite the horrendous damage it causes.

Stream Channelization
Walls intended to create embankments for steering the course of a stream or to protect structures built within a floodway face a losing battle against the hydraulic energy produced by raging waters during a big storm.  They tend to fail when needed most.  Materials used to channelize streams, whether earthen, stone, or masonry, displace rising water into elevations not previously prone to flooding.  Walls focus energy into the stream bottom causing scour of the substrate, often undermining the structures they were intended to protect.  In extreme cases such as the one shown to the right, a channelized creek functions mostly as a collector of polluted runoff from streets, parking lots, and commercial properties.  It has little capability of purifying the water entering it.  A lack of nutrient-sequestering vegetation and an impaired benthic ecosystem make this stream little more than an open sewer for the length of its run through the walled area.

NUTRIENT AND SEDIMENT RUNOFF

As filter feeders, freshwater mussels and clams are renowned for clarifying water by removing organic particulates, but they are intolerant of excessive turbidity.  Unionids do not remove silt and sediment in suspension and are especially vulnerable to excessive loads of nitrogen and phosphorus, the nutrients that lead to massive blooms of algal growth.  As algae dies and decays, eutrophication and its depletion of dissolved oxygen levels can prove fatal to populations of bivalves, especially in warm weather.  For this reason, river mussels have disappeared from Susquehanna valley streams affected by significant volumes of agricultural and urban runoff.  The effects are magnified where streamside vegetation has been removed and riparian buffers are lacking.

Bare farmland soils loaded with manure are a major source of nutrient and sediment pollution in the Lower Susquehanna River Watershed.
Whether originating as runoff from fields used for raising crops…
Bare farmland soils loaded with manure are a major source of nutrient and sediment pollution in the Lower Susquehanna River Watershed.
…or from parcels used for livestock grazing, bare farmland soils loaded with manure are a major source of nutrient and sediment pollution in the Lower Susquehanna River Watershed.
Urban runoff is a source of a wide range of pollutants.
Urban runoff is not only a significant source of nutrient and sediment loading, it’s responsible for a wide range of other pollutants as well.
Impaired Stream
Mowed creekbanks offer little protection from erosion and do little to take up the nutrients that cause algal blooms in impaired streams like this one.  Note the pipe for discharging stormwater or something worse.  Because they feed persistently and never migrate, handfed ducks add to the nutrient load in the stream and obliterate populations of benthic organisms including unionid mussels.  (Vintage 35mm image)

REDUCED BASE FLOW

In addition to the effects of the silt and nutrients that lead to eutrophication, loss of base flow in streams that drain disturbed landscapes make them more likely suffer severe depletion of dissolved oxygen levels during hot weather.  Within a given watershed, progressive reductions in stream base flow can occur as increased volumes of ground and surface waters are removed for human use.  This condition is further aggravated when the amount of rainfall infiltrated to recharge groundwater supplies decreases as the volumetric area of the watershed converted to non-porous surfaces such as streets, parking areas, lawns, and roofs increases.  In urbanized areas, waterways with reduced flow are susceptible to thermal shock during summertime showers when stormwater drains away from sun-scorched pavement into a stream with an already stressed ecosystem.  During periods of drought, a body of water may dry up completely.  River mussels can survive for just a short time by retreating into their shell and remaining buried in the substrate, but prolonged exposure to air and sunshine is fatal.  While fish may recolonize a segment of desiccated waterway rather quickly, unionids may not readily return.

Flooding and Desiccation of Impaired Stream
An urban stream with reduced base flow is subject to thermal shock and sediment loading from summertime flooding (left) and complete desiccation during periods of drought (right).  (Vintage 35mm images)
Dead Pyganodon cataracta
The shells of expired Eastern Floater (Pyganodon cataracta) mussels on the dried-up bed of a pond that had recently been drained for installation of a flood gate.

TOXIC POLLUTANTS

Freshwater mussels may bioaccumulate pesticides and other toxic substances found in their environment.  Because unionids, following their larval stage, spend their entire lives in a small geographic area within a single body of water, and because they can live for decades, these invertebrates can be ideal long-term indicators of stream health.  For the same reasons, unionids don’t belong on anyone’s menu.

Unionid Shells in Late Woodland Period Dump
Back in the good ol’ days when the Susquehanna wasn’t so polluted, river mussels were plentiful and safe to eat.  People back then crafted homemade pottery so that they might have a clam bake. This photo shows a diorama at the State Museum of Pennsylvania depicting a Late Woodland Period (800 A.D.-1600 A.D.) Clemson’s Island Culture “village dump” found along the Susquehanna north of Harrisburg.  Therein are the leftovers from the party.

ACID MINE DRAINAGE

Some streams in the Lower Susquehanna River Watershed lack river mussels for self-evident reasons.  Those waterways to the north and northeast of Harrisburg that originate in anthracite coal fields run red brown with acid mine drainage—pure poison to aquatic creatures, particularly bivalves whose calcium carbonate shells dissolve in low pH water.  An obvious example of the effects of the severity of this pollution can be found in the case of Swatara Creek.  After originating in mining areas of western Schuylkill County, it supports no significant life at all during its run through the hills of the Ridge and Valley Province.  Fish, mussels, and other fauna inhabit the Swatara only downstream of its confluence with Little Swatara Creek, a diluting tributary that drains a portion of the dolomite-rich Great Valley through which the Swatara flows along most of the remainder of its course to the Susquehanna River.

Acid Mine Drainage Pollution
Swatara Creek near Ravine, Schuylkill County, Pennsylvania, is bordered by beautiful mountain forest, but the stream is void of fish, mussels, and other aquatic life.  The reddish-brown ferrous hydroxide (iron hydroxide) stains on the rocks in the water are a telltale sign of pollution from acid mine drainage.

INVASIVE SPECIES

An additional threat to freshwater mussels and clams is competition with non-native invasive species.  Introduced fishes can displace a favorable species of host for the mussels’ larvae.  Recent introductions of invasive Flathead Catfish (Pylodictis olivaris), Blue Catfish (Ictalurus furcatus), and Northern Snakehead (Channa argus) are especially concerning.  Zebra mussels (Dreissena species) are a particular concern—possessing the potential to overwhelm and eliminate otherwise healthy populations of unionids.  In extreme cases, zebra mussel colonies have encrusted native mussels, crayfish, and other benthic species (Shaw et al. 2004).  Early discovery and control of invasive species, particularly zebra mussels, may protect native organisms, including bivalves, and provide financial savings to municipalities, businesses, utilities and other users of freshwater.

Zebra Mussels on Unionid
Non-native Zebra Mussels (Dreissena polymorpha) encrusting a native freshwater river mussel.  (National Oceanic and Atmospheric Administration image)
Zebra Mussels on Unionid
A crippling accumulation of invasive Zebra Mussels (Dreissena polymorpha) on a river mussel.  (United States Fish and Wildlife Service image)

HISTORICAL RECORDS
Samuel Staman Haldeman
Samuel Steman Haldeman was born at Locust Grove along the Susquehanna River just downstream of Conewago Falls near Bainbridge, Lancaster County. Pennsylvania.  (Library of Congress image)

Samuel Steman Haldeman provides an early record of the Unionidae found in the Lower Susquehanna River Watershed in Pennsylvania.  Haldeman was born in 1812 at the village of Locust Grove along the Susquehanna, just downstream of Conewago Falls near Bainbridge, Lancaster County.  As a boy he studied the wildlife found near his family home, including freshwater mussels and snails.  In later years, Haldeman built his own home on the Susquehanna at Chickies Rock.  He became a well-known scholar, authoring numerous papers on wide-ranging topics.  His best-known works were A Monograph of the Freshwater Univalve Mollusca of the United States, published as a series from 1842 through 1845, and Enumeration of the recent freshwater Mollusca which are common to North America and Europe, 1844.  The latter drew the interest of Charles Darwin, who briefly comments on Haldeman’s paper in Origin of Species.  Haldeman’s account of the mollusks of the area appears in Rupp’s History of Lancaster County, published in 1844 by I. Daniel Rupp.  There, Haldeman describes eight species of river mussels found in the Susquehanna and its “branches” within Lancaster County, Pennsylvania.

      1.  Unio cariosus—currently known as Lampsilis cariosa
      2.  Unio radiata—currently known as Lampsilis radiata
      3.  Unio complanatus—currently known as Elliptio complanata
      4.  Unio viridis—currently known as Lasmigona subviridis
      5.  Alasmodon undulatus—currently known as  Alasmidonta undulata
      6.  Alasmodon marginatus—currently known as Alasmidonta marginata
      7.  Anodon cataractus—currently known as Pyganodon cataracta
      8.  Anodon undulatus—currently known as Strophitus undulatus

Later in the nineteenth century, Bruckhart (1869) lists ten species of unionids in the lower Susquehanna watershed in Lancaster County.  Active changes in taxonomy during the 1800s may explain the confusing taxa used.  Using Clarke and Berg (1959) to edit apparent synonyms from Bruckhart’s list distills his species count to no more than the eight enumerated by Haldeman.

In addition to Haldeman’s eight species, there is an historical record of a ninth— Alasmidonta heterodon, the Dwarf Wedgemussel.  Moser (1993) plots the species on the Susquehanna River at Chickies Rock in a location coded as “Historical occurrence, presumed extirpated” at “…Susquehanna River at Columbia, Lancaster County, PA”.  The valves of the specimen(s) referred to in Moser’s report are apparently those collected in 1919 by L. H. Streng.  They are in the collection of the Philadelphia Academy of Natural Sciences (ANSP 48308).  Alasmidonta heterodon is a federally endangered species.

An Eastern Lampmussel (Lampsilis radiata) valve specimen (ANSP 101665) at the Philadelphia Academy of Natural Sciences was collected at York Furnace on September 12, 1910.  The ruins of York Furnace are found in southern York County along Otter Creek near its confluence with the Susquehanna River.  The small village known as York Furnace lies just downstream of the mouth of Otter Creek opposite the Lancaster County village of Pequea.  It is not clear whether the Lampsilis radiata population was in Otter Creek in York County, or in the river near the creek’s mouth, thus within the boundaries of Lancaster County, but a contiguous range in both counties is probable.  In the same year the specimen was collected, Holtwood Dam was constructed on the Susquehanna downstream, flooding much of the free-flowing segment of the river at York Furnace as part of the “Lake Aldred” impoundment.  Since 1910, silt deposition and waste-coal dredging, along with other habitat and water quality degradation factors, have probably eliminated Lampsilis radiata from most of its suitable habitat in the Pennsylvania section of the lower Susquehanna watershed.  A population still exists in tidal freshwater areas at the mouth of the Susquehanna in Maryland.  Though believed to be globally secure, Lampsilis radiata is ranked “Critically Imperiled” in Pennsylvania.

Two species of unionids occur in the Susquehanna basin only in areas in or near tidal freshwater at the mouth of the river in Maryland—Anodonta implicata, the Alewife Floater, and Leptodea ochracea, the Tidewater Mucket.

HALDEMAN’S TRANSPLANTS

Endpaper image from “Monograph of the Freshwater Univalve Mollusca of the United States”, a lithograph by Helen E. Lawson depicting Professor Samuel Stamen Haldeman’s residence and arboretum at “Chicquesalunga” along the Susquehanna River at the base of Chiques Rock.

Throughout the eighteenth and nineteenth centuries, it was common practice for agronomists, botanists, naturalists, and others to collect and transport live plants and animals for introduction into areas outside their native range.  Generally, native transplants consisted of species introduced into new areas on their native continent, while non-native transplants were flora and fauna introduced into continents entirely outside of their native range.  Both native and non-native transplants possessed the potential to become invasive species.  But during these years before the prevalence of any widespread conservation ethos, the threat of significant agricultural or ecological damage from transplanted species went unforeseen.  Among those participating in plant and animal introductions, there appears to be little if any awareness of the potential consequences.

NATIVE TRANSPLANTS

The October, 1841, Proceedings of the Academy of Natural Sciences (Volume 1, page 104) record—as part of a presentation on the nomenclature used for the river mussels then known as Unio viridis and Unio tappanianus, and the proposal by Conrad of the species name subviridis for both—that Samuel Stamen Haldeman made known to the members present, “that he had placed some living specimens of Western Unio, Unio rectus, triqueter, circulus, cylindricus, ovatus, and others in the Susquehanna, where no western species has hitherto been found, except U. viridis, Raf.”  The mussels Haldeman describes as introduced from the “west”, a term which during the early 1840s often described areas only as far west as the Mississippi and western Great Lakes drainages, were collected from the Ohio River system, probably in Kentucky.

Haldeman, in his presentation to the Academy, makes reference to the similarities shared by “western” specimens of Unio viridis from Kentucky and those from the Atlantic Slope, the latter known by some naturalists as Unio tappanianus.  He seems to be convinced that the eastern and “western” specimens are of a single species.  Today, Unio viridis and Unio tappanianus are indeed considered a single species—Lasmigona subviridis.  Furthermore, Lasmigona subviridisis is recognized not as a “western” species, but as a native of the Atlantic slope, including the Susquehanna watershed Today,  Lasmigona subviridis is absent from the “west”, so how did specimens from Kentucky find their way to the meeting of the Academy of Natural Sciences in 1841.  Were they misidentified shells of another similar species?  Maybe.  But the case of Physella acuta (see the Physella acuta species account by clicking the “Freshwater Snails” tab at the top of this page) demonstrates that the practice of transplanting can complicate the difficulties of differentiating species based on their morphological features and obfuscate their geographic origins.  There is the possibility that, similar to the way mussels from the “west” were transplanted into the Susquehanna by Haldeman, live specimens of Lasmigona subviridis had, prior to 1841, been collected from the Atlantic slope, then transplanted into waterways of the “west”, particularly the Ohio River basin in Kentucky.

NON-NATIVE TRANSPLANTS

The February 1846, Proceedings of the Academy of Natural Sciences (Volume 3, pages 14-16) record Professor Haldeman’s reaction to a specimen of Unio crassus presented to him at the meeting, “it is one of those which he placed in the river Susquehanna, in a living state, in the year 1841, a record of which fact will be found at page 104, Vol. 1, of the Proceedings of the Academy.  As no western species of Unio except U. viridis, Raf, had hitherto been found in that river, Mr. Haldeman had no doubt that the present specimen was in reality one of those referred to.  The growth had been inconsiderable, and the general appearance very little changed.  The individuals of this and other species seem not to have survived.”  Unio crassus, the Thick-shelled River Mussel, is a declining species native to Europe and is not known to presently inhabit any North American waters.


FRESHWATER BIVALVE MOLLUSKS

Of the Lower Susquehanna River Watershed


UNIONIDAE

The River Mussels

 

SPECIES STATUS KEY

Federally Endangered-a native species listed by the United States government as imminently in danger of extinction.

PA Endangered-a native species listed by the Commonwealth of Pennsylvania as imminently in danger of extinction or of extirpation as a breeding species in the state.

MD Endangered-a native species listed by the State of Maryland as imminently in danger of extinction or of extirpation as a breeding species in the state.

Federally Threatened-a native species listed by the United States government as under threat to become an endangered species in the foreseeable future.

PA Threatened-a native species listed by the Commonwealth of Pennsylvania as under threat to become an endangered species in the state in the foreseeable future.

MD Threatened-a native species listed by the State of Maryland as under threat to become an endangered species in the state in the foreseeable future.

PA Candidate-an uncommon native species that could, in the future, become listed by the Commonwealth of Pennsylvania as endangered or threatened in the state.

Domain-Eukaryota

Kingdom-Animalia

Phylum-Mollusca

Class-Bivalvia

Order-Unionida

Family-Unionidae

Note:  Photographs of river mussel shells on a blue background show two pairs of valves…

    1.   A pair of closed valves, showing the exterior of the shell, appears to the left in each photograph.  (Two valves are shown in Figure 4 to display female and male.) The left of the closed mussel is the posterior, the right the anterior.  The beak and the dorsal surface of the shell are at the top.  The ventral edge of the shell is at the bottom.
    2.   A pair of open valves, showing the interior of the shell, appears to the right in each photograph.  The left valve is to the left, the right valve to the right.  The posterior of the mussel is at the top in this view.  Pseudocardinal hinge teeth, if present, are anterior of the hinge along the dorsal edge of the interior of the valves.  Lateral hinge teeth, if present, are parallel with the hinge extending toward the posterior of the mussel along the dorsal edge of the interior of the valves.

Alasmidonta marginata susquehannae

Common Name(s):  Susquehanna Elktoe

Status:

Rank:  Pennsylvania S3 (Vulnerable) and S4 (Apparently Secure), Globally G4 (Apparently Secure) for the species (Alasmidonta marginata)

Host Fish known to occur in the Susquehanna and/or its tributaries:  List for interior Alasmidonta marginata, not particularly the Atlantic Slope subspecies A. m. susquehannae—Banded Killifish (Fundulus diaphanus), Brook Stickleback (Culea inconstans), Creek Chub (Semolitus atromaculatus), Creek Chubsucker (Erimyzon oblongus), Northern Hogsucker (Hypentelium nigricans), Shorthead Redhorse (Moxostoma macrolepidotum), Silver Redhorse (Moxostoma anisurum), White Sucker (Catostomus commersoni), Golden Shiner (Notimegonus crysoleucas), Longnose Dace (Rhinichthys cataractae), Mottled Sculpin (Cottus bairdii), Slimy Sculpin (Cottus cognatus), and Rock Bass (Ambloplites rupestris).

Comments:

Haldeman (1844), using the taxa Alasmodon marginatus, described Alasmidonta marginata susquehannae, “… green rayed, cardinal teeth small and thin, posterior extremity of shell truncated. 2 inches.”

Freshwater mussels of the Lower Susquehanna River Watershed: Alasmidonta marginata susquehannae
Alasmidonta marginata susquehannae Shell is sub-trapezoidal in shape with a sharply defined posterior ridge.  The exterior is brown and strongly rayed, often lighter in color toward the posterior.  The interior has 1 narrow pseudocardinal tooth in each valve.  The nacre is white to bluish white with hues of salmon.  The protruding “foot” of live specimens is most often salmon in color.  The similar Alasmidonta varicosa has a more evenly rounded posterior ridge, a darker external color to the posterior, and a size not exceeding 2 ¾ inches (70 millimeters) in length.
Freshwater mussels of the Lower Susquehanna River Watershed: Alasmidonta marginata susquehannae
Alasmidonta marginata susquehannae, a Susquehanna Elktoe, showing its salmon-colored foot.  (Vintage 35mm image)
Freshwater mussels of the Lower Susquehanna River Watershed: Alasmidonta marginata susquehannae and Corbicula fluminea
Alasmidonta marginata susquehannae, a Susquehanna Elktoe, and a non-native Asiatic Clam (Corbicula fluminea) emerging from their shells.  (Vintage 35mm image)

Alasmidonta varicosa

Common Name(s):  Brook Floater

Status:  MD Endangered

Rank:  Pennsylvania S1 (Critically Imperiled) and S2 (Imperiled), Maryland S1 (Critically Imperiled), Globally G3 (Vulnerable)

Host Fish known to occur in the Susquehanna and/or its tributaries:  Golden Shiner (Notemigonus chrysoleucas), Longnose Dace (Rhinichthys cataracte), Blacknose Dace (Rhinichthys atratulus), Mottled Sculpin (Cottus bairdi), Slimy Sculpin (Cottus cognatus), Redbreast Sunfish (Lepomis auritus), Pumpkinseed (Lepomis gibbosus), Bluegill (Lepomis macrochirus), Margined Madtom (Noturus insignis), Fantail Darter (Etheostoma flabellare), and Yellow Perch (Perca flavescens).

Comments:

Alasmidonta varicosa
Alasmidonta varicosa is similar to Alasmidonta marginata susquehannae, but has a more evenly rounded posterior ridge, a darker external color to the posterior, and a size not exceeding 2 ¾ inches (70 millimeters) in length.  In this photograph, the exterior of the left valve is to the left and the interior of the right valve is to the right.  (United States Fish and Wildlife Service image by Mathew Patterson)
Alasmidonta varicosa
Alasmidonta varicosa specimen from New York.  The exterior of the right valve is to the left and the interior of the left valve is to the right.  (United States Fish and Wildlife Service image by Mathew Patterson)
Alasmidonta varicosa
Alasmidonta varicosa, a Brook Floater.  (United States Fish and Wildlife Service image by Ryan Hagerty)
Alasmidonta varicosa
Alasmidonta varicosa, gravid female brook floaters in a captive breeding program.  (United States Fish and Wildlife Service image by Rachael Hoch, NC Wildlife Resources Commission)
Alasmidonta varicosa
Alasmidonta varicosa, female brook floaters in a captive breeding program one hour after serotonin treatment to prepare them for harvest of glochidia.  Note the similarity of the foot color to that of Alasmidonta marginata susquehannae.  (United States Fish and Wildlife Service image by Rachael Hoch, NC Wildlife Resources Commission)

Alasmidonta undulata

Common Name(s):  Triangle Floater

Status:  MD Endangered

Rank:  Pennsylvania S3 (Vulnerable), Maryland S1 (Critically Imperiled), Globally G4 (Apparently Secure)

Host Fish known to occur in the Susquehanna and/or its tributaries:  Central Stoneroller (Campostoma anomalum), Common Shiner (Luxilus cornutus), Rosyface Shiner (Notropis rubellus), Fallfish (Semotilus corporalis), Longnose Dace (Rhinichthys cataracte), Northern Hogsucker (Hypentelium nigricans), Slimy Sculpin (Cottus cognatus), Pumpkinseed (Lepomis gibossus), Largemouth Bass (Micropterus salmoides), White Perch (Morone americana), and Fantail Darter (Etheostoma flabellare).

Comments:

Haldeman (1844), using the taxa Alasmodon undulatus, described Alasmidonta undulata, “… dark brown, rayed, a very robust tooth in each valve. 1 ½ inches.”

Freshwater mussels of the Lower Susquehanna River Watershed: Alasmidonta undulata
Alasmidonta undulata Shell is sturdy and inflated with a subdued, rounded posterior ridge.  The exterior is brown to black in color.  Lighter specimens are banded.  The interior has conspicuous pseudocardinal teeth, 2 in the left valve, 1 in the right, and no noticeable lateral teeth.  The nacre is bi-colored, white anteriorly and bluish to the posterior, often with a haze of salmon.  The similar Alasmidonta heterodon does not exceed 1 ¾ inches (45 millimeters) in length and has 2 lateral teeth in the right valve and 1 in the left valve, a characteristic unlike any other northeastern unionid.

Alasmidonta heterodon

Common Name(s):  Dwarf Wedgemussel

Status:  Federally Endangered, MD Endangered, PA Endangered

Rank:  Pennsylvania S1 (Critically Imperiled), Maryland S1 (Critically Imperiled), Globally G1 (Critically Imperiled) and G2 (Imperiled)

Host Fish known to occur in the Susquehanna and/or its tributaries:  Atlantic Salmon (Salmo salar), Brown Trout (Salmo trutta), Banded Killifish (Fundulus diaphanus), Mottled Sculpin (Cottus bairdi), Striped Bass (Morone saxatalis), Tessellated Darter (Etheostoma olmstedi), and Shield Darter (Percina peltata).

Comments:  Known in the lower Susquehanna from specimen(s) collected by L. H. Streng on the main stem of the river at Chickies Rock in 1919.

Alasmidonta heterodon
Alasmidonta heterodon has 2 lateral teeth in the right valve and 1 in the left valve, a characteristic unlike any other northeastern unionid.  In this photograph, the exterior of the left valve is to the left and the interior of the right valve is to the right.  (United States Fish and Wildlife Service image by Mathew Patterson)
Alasmidonta heterodon
Alasmidonta heterodon specimen from Virginia.  The exterior of the right valve is to the left and the interior of the left valve is to the right.  (United States Fish and Wildlife Service image by Mathew Patterson)
Alasmidonta heterodon
Alasmidonta heterodon, a Dwarf Wedgemussel, in substrate.  (United States Fish and Wildlife Service image by Susi Von Oettingen)

Anodonta implicata

Common Name(s):  Alewife Floater

Status:

Rank:  Maryland S3 (Vulnerable), Globally G5 (Secure)

Host Fish known to occur in the Susquehanna and/or its tributaries:  Alewife (Alosa pseudoharengus), Blueback Herring (Alosa aestivalis), White Sucker (Catastomus commersoni), Pumpkinseed (Lepomis gibbosus), and White Perch (Morone americana).

Comments:  A tidal freshwater species found in the Susquehanna watershed only in the area of the mouth of the river in Maryland.

Anodonta implicata
Anodonta implicata specimen from Maryland.  The exterior of the right valve is to the left and the interior of the left valve is to the right.  (United States Fish and Wildlife Service image by Mathew Patterson)
Anodonta implicata
Sub-adult Anodonta implicata specimen marked with a laser-generated tracking number.  (United States Fish and Wildlife Service image by Mathew Patterson)

Anodontoides ferussacianus

Common Name(s):  Cylindrical Papershell

Status:

Rank:  Pennsylvania S2 (Imperiled) and S3 (Vulnerable), Globally G5 (Secure)

Host Fish known to occur in the Susquehanna and/or its tributaries:  Sea Lamprey (Petromyzon marinus), Bluntnose Minnow (Pimephales notatus), Common Shiner (Luxilus cornutus), Spotfin Shiner (Cyrpinella spiloptera), White Sucker (Catostomus commersoni), Mottled Sculpin (Cottus bairdii), Bluegill (Lepomis macrochirus), Black Crappie (Pomoxis nigromaculatus), and Largemouth Bass (Micropterus salmoides).

Comments:  This species has been recorded in the lower Susquehanna drainage in Lancaster County, Pennsylvania, probably occurring as a native transplant.

Anodontoides ferussacianus
Anodontoides ferussacianus specimen from Illinois. The exterior of the left valve is to the left and the interior of the right valve is to the right.  (United States Fish and Wildlife Service image by Mathew Patterson)
Anodontoides ferussacianus
Anodontoides ferussacianus specimen from Ohio. The exterior of the left valve is to the left and the interior of the right valve is to the right.  (United States Fish and Wildlife Service image by Mathew Patterson)

Elliptio complanata

Common Name(s):  Eastern Elliptio, Flattened Filter Clam

Status:

Rank:   Globally G5 (Secure)

Host Fish known to occur in the Susquehanna and/or its tributaries:  American Eel (Anguilla rostrata), Brook Trout (Salvelinus fontinalis), Lake Trout (Salvelinus namaycush), Mottled Sculpin (Cottus bairdii), Slimy Sculpin (Cottus cognatus), Alewife (Alosa pseudoharengus), Banded Killifish (Fundulus diaphanous), Green Sunfish (Lepomis cyanellus), Largemouth Bass (Micropterus salmoides), Pumpkinseed (Lepomis gibbosus), Redbreast Sunfish (Lepomis auritus), Smallmouth Bass (Micropterus dolomieu), White Crappie (Pomoxis annularis), White Perch (Morone americana), and Yellow Perch (Perca flavascens).

Comments:  The most common and widespread unionid in the Lower Susquehanna River Watershed.

A laboratory study (Lellis, et. al., 2013) to determine the host fishes for Elliptio complanata from streams on the Atlantic Slope found glochidia from Chesapeake Bay drainages metamorphosed into juvenile mussels on five species of host fish: American Eel (Anguilla rostrata), Brook Trout (Salvelinus fontinalis), Lake Trout (Salvelinus namaycush), Mottled Sculpin (Cottus bairdii), and Slimy Sculpin (Cottus cognatus).  American Eel yielded the best results with 13.2 juveniles per fish and a success rate of ≥ 0.90 percent.  Subsequently, an effort was begun on the lower Susquehanna to capture migrating catadromous elvers at Conowingo Dam in Maryland and transport them to suitable waterways upstream to support existing populations of Eastern Elliptios and possibly expand their current range back into some of the streams they once occupied.

Fishes of the Lower Susquehanna River Watershed: American Eel
An American Eel (Anguilla rostrata) recovered during an electrofishing survey one year after being captured at Conowingo Dam in Maryland and transported upriver for release in a stream with a known population of Eastern Elliptio (Elliptio complanata) mussels.

Haldeman (1844), using the taxa Unio complanatus, described Elliptio complanata, “… compressed, dull brown, inside frequently purple.  Young sometimes rayed, extremely variable form, our most common species. 3 inches.”

Freshwater mussels of the Lower Susquehanna River Watershed: Elliptio complanata
Elliptio complanata Shell is strong and notably compressed.  Exterior varies from brown to nearly black.  The interior has 2 pseudocardinal and 2 lateral hinge teeth in the left valve, and one of each in the right valve.  The nacre is bright purple on most specimens, with intermediate shading to white on others.

Lampsilis cariosa

Common Name(s):  Yellow Lampmussel, Caried Lampmussel

Status:

Rank:  Globally G3 (Vulnerable) and G4 (Apparently Secure)

Host Fish known to occur in the Susquehanna and/or its tributaries:  Bluntnose Minnow (Pimephales notatus), White Sucker (Catostomus commersoni), Banded Killifish (Fundulus diaphanous), Chain Pickerel (Esox niger), Pumpkinseed (Lepomis gibbosus), Rock Bass (Amblopites rupestris), Bluegill (Lepomis macrochirus), Black Crappie (Pomoxis nigromaculatus), Largemouth Bass (Micropterus salmoides), Smallmouth Bass (Micropterus dolomieu), White Bass (Morone americana), White Perch (Morone americana), and Yellow Perch (Perca flavescens).

Comments:

Haldeman (1844), using the taxa Unio cariosus, described Lampsilis cariosa. “… shell straw yellow, 3 or 4 inches.”

Freshwater mussels of the Lower Susquehanna River Watershed: Lampsilis cariosa
Lampsilis cariosa The shell is strong and sturdy, thickened anteriorly.  Females are rounded in appearance (top left) and males are more elongate (bottom left).  The exterior is shiny and bright yellow, rarely dark brown.  The interior has prominent hinge teeth; 2 pseudocardinal teeth in each valve, 1 lateral tooth in the right valve, and 2 lateral teeth in the left valve.  The nacre is white, sometimes salmon-colored from the beaks to the posterior.  The similar Lampsilis radiata has a roughened external shell with broad dark bands.
Freshwater mussels of the Lower Susquehanna River Watershed: Lampsilis cariosa
Lampsilis cariosa, a Yellow Lampmussel, extending its foot into the substrate.  (Vintage 35mm image)

Lampsilis radiata

Common Name(s):  Eastern Lampmussel

Status:

Rank:  Pennsylvania S1 (Critically Imperiled), Globally G5 (Secure)

Host Fish known to occur in the Susquehanna and/or its tributaries:  Banded Killifish (Fundulus diaphanous), Black Crappie (Pomoxis nigromaculatus), Largemouth Bass (Micropterus salmoides), Rock Bass (Amblopites rupestris), Pumpkinseed (Lepomis gibbosus), Smallmouth Bass (Micropterus dolomieu), White Perch (Morone americana), and Yellow Perch (Perca flavescens).

Comments:  The range of the Eastern Lampmussel in the Susquehanna was apparently seriously fragmented, and its numbers precipitously depleted, by various impairment factors including dam construction, siltation, and waste-coal dredging.  This species may have been particularly susceptible to the latter due to its large size as a breeding adult.

Haldeman (1844), using the taxa Unio radiata, described Lampsilis radiata, “… covered with broad green bands, 4 or 5 inches.”

Lampsilis radiata
Lampsilis radiata Exterior view of right valve specimen from Maryland.  (United States Fish and Wildlife Service image by Mathew Patterson)
Lampsilis radiata
Lampsilis radiata Interior view of right valve specimen from Maryland.  (United States Fish and Wildlife Service image by Mathew Patterson)
Lampsilis radiata
Lampsilis radiata, sub-adult specimen from the Potomac River, DC.  Right valve is to the left and the left valve is to the right.  (Smithsonian National Museum of Natural History image www.si.edu)
Lampsilis radiata
Lampsilis radiata, sub-adult specimen from the Potomac River, DC.  Right valve is to the left and the left valve is to the right.  (Smithsonian National Museum of Natural History image www.si.edu)

Lasmigona subviridis

Common Name(s):  Green Floater

Status:  MD Endangered

Rank:  Pennsylvania S2 (Imperiled) and S3 (Vulnerable), Maryland S1 (Critically Imperiled), Globally G3 (Vulnerable)

Host Fish known to occur in the Susquehanna and/or its tributaries:  None needed?  In a lab setting, females have been observed expelling metamorphosed young.

Comments:

Haldeman (1844), using the taxa Unio viridis, described Lasmigona subviridis, “… a small, fragile, brown or green rayed species, with cardinal teeth, compressed and very variable. usually 1 ½ inches.”

Freshwater mussels of the Lower Susquehanna River Watershed: Lasmigona subviridis
Lasmigona subviridis Shell is fragile and compressed.  Posterior ridge is inflated and rounded.  The exterior is brown, rayed, and often well-worn.  The interior has forward tilting pseudocardinal teeth; 1 or 2 in left valve, and 1 in the right valve.  The nacre is white, sometimes bluish, and iridescent posteriorly on most specimens.

Leptodea ochracea

Common Name(s):  Tidewater Mucket

Status:

Rank:  Maryland S1 (Critically Imperiled) and S2 (Imperiled), Globally G3 (Vulnerable) and G4 (Apparently Secure)

Host Fish known to occur in the Susquehanna and/or its tributaries:  Banded Killifish (Fundulus diaphanous), and White Perch (Morone americana).

Comments:  A tidal freshwater species found in the Susquehanna watershed only in the area of the mouth of the river in Maryland.

Leptodea ochracea
Leptodea ochracea, sub-adult specimen from the Potomac River, DC.  (Smithsonian National Museum of Natural History image www.si.edu)
Leptodea ochracea
Leptodea ochracea, sub-adult specimen from the Potomac River, DC.  (Smithsonian National Museum of Natural History image www.si.edu)

Pyganodon cataracta

Common Name(s):  Eastern Floater, Fragile Freshwater Mussel

Status:

Rank:  Globally G5 (Secure)

Host Fish known to occur in the Susquehanna and/or its tributaries:  Common Carp (Cyprinus carpio), White Sucker (Catostomus commersoni), Pumpkinseed (Lepomis gibbosus), and Rock Bass (Ambloplites rupestris).

Comments:  Buoyant and more tolerant of silt than other river mussels, it is the most likely species to be found surviving in spring-fed ponds, farmland streams, and millponds choked with legacy sediments.

Haldeman (1844), using the taxa Anodon cataractus, described Pyganodon cataracta, “… bright green, rayed: delicate. 4 or 5 inches.”

Freshwater mussels of the Lower Susquehanna River Watershed: Pyganodon cataracta
Pyganodon cataracta Shell is inflated and fragile, often more elongate than shown.  The exterior is dull brown, often green, and occasionally banded posteriorly.  The interior lacks hinge teeth.  The nacre is silver and colorfully iridescent.
Freshwater mussels of the Lower Susquehanna River Watershed: Pyganodon cataracta
Pyganodon cataracta, an Eastern Floater, with its incurrent and excurrent apertures actively siphoning at the posterior (right) end of the mussel.  (Vintage 35mm image)
Freshwater mussels of the Lower Susquehanna River Watershed: Pyganodon cataracta
Pyganodon cataracta, an Eastern Floater, extending its foot into the gravel.  (Vintage 35mm image)

Strophitus undulatus

Common Name(s):  Creeper

Status:

Rank:  Maryland S2 (Imperiled), Globally G5 (Secure)

Host Fish known to occur in the Susquehanna and/or its tributaries:  Spotfin Shiner (Cyrpinella spiloptera), Bluntnose Minnow (Pimephales notatus), Longnose Dace (Rhinichthys cataractae), Central Stoneroller (Campostoma anomalum), Creek Chub (Semotilus atromaculataus), Yellow Bullhead (Ameriurus natalis), Largemouth Bass (Micropterus salmoides), Rock Bass (Ambloplites rupestris), Bluegill (Lepomis macrochirus), White Crappie (Pomoxis annularis), Walleye (Stizostedion vitreum), Banded Darter (Etheostoma zonale), and Fantail Darter (Etheostoma flabellare).

Comments:

Haldeman (1844), using the taxa Anodon undulatus, described Strophitus undulatus, “… dark brown, hinges slightly thickened having a tendency to form a slight pair of teeth. 2 or 3 inches.”

Freshwater mussels of the Lower Susquehanna River Watershed: Strophitus undulatus
Strophitus undulatus Shell exterior is shiny, dark brown, and sometimes rayed.  The interior is usually lacking noticeable pseudocardinal or lateral hinge teeth.  The nacre is bluish white, salmon-colored near the beaks.

Villosa iris

Common Name(s):  Rainbow Mussel

Status:

Rank:  Globally G5 (Secure)

Host Fish known to occur in the Susquehanna and/or its tributaries:  Rock Bass (Ambloplites rupestris), Smallmouth Bass (Micropterus dolomieu), and Largemouth Bass (Micropterus salmoides).

Comments:  A native transplant to the Susquehanna.

Villosa iris
Villosa iris specimen from Virginia.  The exterior of the right valve is to the left and the interior of the left valve is to the right.  (United States Fish and Wildlife Service image by Mathew Patterson)
Villosa iris
Villosa iris specimen from Michigan.  The exterior of the right valve is to the left and the interior of the left valve is to the right.  Note the rainbow-like colors of the nacre.  (United States Fish and Wildlife Service image by Mathew Patterson)

OTHER FRESHWATER BIVALVE MOLLUSKS


Order-Sphaeriida

 Family Sphaeriidae

Sphaeriidae is a family of small freshwater bivalves never exceeding one inch in length.  Three genera are found locally—Pisidium, the Peashell or Pill Clam; Sphaerium, the Short-siphoned Fingernail Clam; and Musculium, the Long-siphoned Fingernail Clam.  Sphaeriidae are most often found in sand and gravel in flowing waterways.  Sphaeriidae, particularly Pisidium, are known to climb vegetation and may prefer habitats with emergent and aquatic plants.  A few species will inhabit ponds and vernal pools.  In the Susquehanna River and its tributaries, populations of Sphaeriidae may have been reduced by invasive populations of the non-native Asiatic Clam (Corbicula fluminea).  Stream segments suffering from heavy silt deposits rarely support significant populations of Sphaeriidae clams.

Freshwater clams of the Lower Susquehanna River Watershed: Sphaeridae Clams
Sphaeriidae clams: Pisidium (left), the tiniest of the Sphaeriidae, has greater length from the beak to the anterior end of the shell.  Sphaerium (center) and Musculium (right) have greater length from the beak to the posterior end of the shell.  Musculium, unlike Sphaerium, have a swollen cap-like beak.  All genera have weak and fragile shells.

Order-Venerida

Family Corbiculidae

The Asiatic Clam, Corbicula fluminea, native to East Asia, is a member of the family Corbiculidae.  Asiatic Clams produce veliger larvae that distribute throughout the water column.  Unlike the Unionidae, Corbiculidae larvae require no host fish to ensure survival.  Asiatic Clams are able to distribute quickly into new areas of suitable habitat.

In North America, Corbicula fluminea was introduced to the Columbia River in Washington by Chinese immigrants in 1938.  During the 1960s, they arrived in the Chesapeake Bay watershed, reaching the Potomac River by 1975 (Lippson and Lippson 1997).  They invaded the Susquehanna River in Lancaster County in the mid-1980s.  By 1990, Corbicula fluminea was the most conspicuous macroinvertebrate in the river.  Today, shells of expired clams blanket the bottom of the Susquehanna from shore to shore in many areas.  Downstream of Conewago Falls, searching a cubic foot of submerged sand will often yield 30 to 50 individual live Asiatic Clams.  The impact of their enormous biomass on other benthic organisms could be studied at length.  Electric generating facilities on the lower Susquehanna River have seen dense colonies of Corbicula fluminea foul their cooling systems.  Resulting shutdowns and repairs have significant economic impact.  Asiatic Clams have invaded many of the Susquehanna’s tributaries.  Fortunately, they are not as invasive in cooler, fast-moving, high-gradient headwaters.

Freshwater clams of the Lower Susquehanna River Watershed: Corbicula fluminea
Corbicula fluminea Shells are sturdy, and triangular with unique beaks.  The exterior is shiny yellow to brown in color.  Small specimens can be differentiated from the Sphaeriidae by the presence of ribbed surfaces on the shell exterior.  The shell interior varies from white to glossy blue gray.
Corbicula fluminea
Corbicula fluminea, an Asiatic Clam, with its foot and siphons extended.  The latter are visible along the posterior (left) edge of the shell.  (Vintage 35mm image)

Order-Myida

Family Dreissenidae

Members of the family Dreissenidae—the Zebra Mussel, Dreissena polymorpha, and the Quagga Mussel, Dreissena rostriformis bugensis—are invasive freshwater mollusks of particular concern in the Lower Susquehanna River Watershed.  Both species are often known collectively as “zebra mussel”.  Using the name “clam” instead of “mussel” to describe a member of the bivalve family Unionidae would seem practical to most observers.  In comparison, Dreissena are “mussels” in the familiar sense, having byssal threads to firmly attach to solid surfaces and to each other, much like the familiar mussels found on pilings and rocks on the Atlantic coastline.  Creating massive, clumped colonies up to three feet in depth, Dreissena mussels cause millions of dollars in damage at power generating stations, manufactories, and other facilities with freshwater intakes.  Removal of Dreissena bivalves leads to operational shutdowns, high maintenance costs, and often the need for chemical treatment.  Some facilities faced with burdening populations of zebra mussels must be reengineered and reconstructed to compensate for their presence (O’Neill 1996).

Zebra Mussels in the Lower Susquehanna River Watershed: Dreissenidae Mussels
Dreissenidae mussel shells, presumptively Dreissena polymorpha, Zebra Mussels, to the left with a sharply angulated ridge between the dorsal and ventral edges of each valve, and Dreissena rostriformis bugensis, Quagga Mussels, to the right with a more compressed shape and lacking a ridge or carina.  Both species are often barred or banded in various shades of brown and black.
Zebra and Quagga Mussels
Differentiating the Zebra Mussel (left) from the Quagga Mussel (right).  (United States Geological Survey image by Myriah Richerson)
Zebra and Quagga Mussels
Zebra Mussel (left) and Quagga Mussel (right).  (United States Geological Survey image by Myriah Richerson)

Dreissena mussel larvae (veligers) are believed to have arrived in North America as stowaways on ships.  Freshwater containing veligers was pumped aboard these vessels as ballast prior to leaving an infected Eurasian port, then discharged upon arrival in a Great Lakes port.  Adult mussels may have arrived on anchor chains and other equipment not exposed to salt water during the voyage (O’Neill 1996).

Zebra mussels are native to the Caspian and Black Seas.  Their dispersal as a non-native invasive species was rapid.  Shaw et al. (2004) tracks the arrival of Dreissena from infected ports in Eurasia.  They were first noted in North America at Lake St. Clair on the Michigan/Ontario border in 1988.  By 1989, Dreissena were well established in sizeable colonies on the Great Lakes.  By 1991, they had extended their range into many of the major waterways of the northeastern United States and eastern Canada.

The first occurrence of Dreissena in the Susquehanna River watershed was of veligers at a sampling point at Goudy Station in Endicott, New York, in 1992.  No adults were found.  In Madison County, New York, a zebra mussel colony was found in the outflow of Eaton Brook reservoir upstream of the Upper Chenango River in 2000.  In 2002, a reproducing population was found in Canadarago Lake in Ostego County, New York.  Canadarago Lake is frequented by recreational boats which may have acted as vectors to infect the lake with Dreissena.  In 2004, Armstrong (2004) found adult and juvenile Zebra Mussels, Dreissena polymorpha, in Goodyear Lake, an impoundment on the Susquehanna River main stem near Cooperstown, New York—downstream of Canadarago Lake.  It is believed Goodyear Lake was colonized by veligers from Canadarago Lake.

Dreissena polymorpha
A buildup of nonindigenous Zebra Mussels, Dreissena polymorpha.  (National Oceanic and Atmospheric Administration image)

Promptly detecting and controlling isolated populations of zebra mussels can be a practice of significant economic advantage.  In the Chesapeake Bay watershed, the Millbrook Quarry in Prince William County, Virginia, is believed to have been infected with Dreissena by SCUBA divers or other recreational users.  After several years of establishment, the mussels were eradicated in late 2006 using 174,000 gallons of Potassium Chloride solution at a cost of $365,000 (see Millbrook Quarry Zebra Mussel Eradication 2006).  The elimination of Dreissena at the Millbrook Quarry will prevent their spread to neighboring waterways and will save operators of local water supply and power generating facilities millions of dollars in treatment, repair, and shutdown costs.

In 2000, zebra mussels (Dreissena species) were found at the Willow Springs Diving Park in the Richland Quarry near Myerstown, Lebanon County, Pennsylvania (Shaw et al. 2004).  This SCUBA facility is located adjacent to the Lower Susquehanna River Watershed in the Schuylkill River drainage basin.

During 2008 and 2009, Quagga Mussels (Dreissena rostriformis bugensis) were found in Billmeyer Quarry, a flooded dolomite operation near Bainbridge, Lancaster County, Pennsylvania.  The quarry, which happens to be located along the Susquehanna next door to Professor Samuel Steman Haldeman’s birthplace, was in use at the time as a SCUBA diving facility.  Following their discovery, the mussels were eradicated.

Dreissena rostriformis bugensis
Non-native Quagga Mussels (Dreissena rostriformis bugensis) on a boat propeller.  (National Park Service image)

In 2008, during a drawdown of the Muddy Run Pumped Storage reservoir along the eastern shore of the Susquehanna in southern Lancaster County, Pennsylvania, the valves of dead Zebra Mussels (Dreissena polymorpha) were found.  This impoundment, which is frequented by recreational boaters, apparently functioned as a source for establishment of the species in the lower Susquehanna.  During the following year, veligers were discovered downriver nearby along the western shore within the intake canals of Units 2 and 3 at the Peach Bottom Atomic Power Station.  In 2010, an adult was found there and subsequently a population became established throughout the adjacent segment of the Susquehanna River known as Conowingo Pond.  The range of that population now extends to the mouth of the Susquehanna on Chesapeake Bay at Havre de Grace, Maryland.

Dreissena polymorpha on Unionid Mussel
Native unionids encumbered by Dreissena mussels must not only compete for food with the invasives, but could also fail to successfully launch their larval glochidia into the water column for attachment to a host fish.  (United States Geological Survey image)

THE VALUE OF MONITORING AND PROTECTING NATIVE MUSSELS

Monitoring Unionidae mussel communities provides data that is useful in efforts to protect them, their aquatic habitats, and the quality of the water they inhabit.  Examination of unionid populations may be useful when assessing the impact of stream impairment and land use on benthic organisms.  Because some species of freshwater mussels can live for decades and, during that time, bioaccumulate a number of pollutants, they can function as long-term indicators of stream health.  On waterways where sediment and nutrient reduction projects are being implemented, the population densities and species diversity of native freshwater mussel communities may provide insight on the effectiveness of conservation work.  Pollution mitigation techniques found beneficial to the unionids could be utilized in other areas where mussels and other benthic fauna are imperiled.  And of course, protecting and restoring populations of Unionidae mussels promotes purification of the streams, rivers, and lakes they inhabit.  They are, after all, nature’s own water filters.


CONSERVATION PRACTICES BENEFICIAL TO NATIVE BIVALVES

MONITORING

Stream Chemistry Testing
Monitoring water quality parameters is an indispensable element of stream improvement, essential both for identifying sources of impairment and for tracking the progress of restoration.  (Vintage 35mm image)
Macroinvertebrate Sampling
Sampling, identifying, and counting macroinvertebrates, including freshwater bivalves, is an important step in the process of scoring a waterway’s suitability for sustaining healthy populations of fish, mussels, and other aquatic life.  (Vintage 35mm image)

CONSERVATION FARMING

Contour Farming
Cropland management practices that reduce sediment and nutrient runoff are essential to efforts aimed at mitigating impairment of streams and rivers in the lower Susquehanna region.  Planting in rows that follow the contour of the land was one of the earliest innovations for preventing erosion, but it did little to address runoff of bare soils across steeply sloped ground.
Cover Crops
A more recent conservation development is the practice of planting cold-tolerant cover crops to eliminate bare ground and hold soil through the winter.  In addition, nutrient management plans formalize procedures for the storage, handling, and application of manure.  An increasing number of farms are adopting these conventions.
Planting a cover crop with a "no-till drill".
A winter cover crop can be planted using a “no-till drill”.  The dead stems and roots from the previous growing season are left in place to help hold and condition the soil through the winter.  Both the cover crop and the debris from the previous season’s growth add organic matter to improve the soil’s ability to retain moisture and sustain microbial activity during the coming season.
Corn, soybeans, and other crops can be planted using a "no-till drill", leaving the soil relatively undisturbed.
In spring, corn, soybeans, and other crops can be planted using a “no-till drill”, leaving the soil relatively undisturbed.

DAM AND LEGACY SEDIMENT REMOVAL

Legacy Sediment
During the eighteenth and nineteenth centuries, a period prior to the implementation of soil conservation practices, eroding silts and sediments from croplands accumulated in mill pond sites throughout the Lower Susquehanna River Watershed.  Today, the majority of these deposits, known as legacy sediments, remain in place, even after the dams are removed.  Former mill pond sites are conspicuous, appearing as soil-choked floodplains incised by steep-banked creeks.  Streambank erosion introduces these nutrient-laden legacy sediments into the waterway, polluting everything downstream including the river and Chesapeake Bay.  At old mill pond sites, legacy sediment deposits displace flood waters, amplifying the effects of a storm, a fact seldom understood by property owners who, like the proprietor of the parcel seen here, dump rock, dirt, and other fill along the creek and atop the sediment in an effort to keep the stream “within its banks”.  This “solution” intensifies scour damage in the streambed and broadens the impact of flooding by displacing water into elevations not previously inundated.  To fix the problem, a good land steward knows it’s best to give up on the mowed lawn perched atop pollutants and time to get busy coming up with a plan to remove the sediment that’s choking the stream corridor.  (Vintage 35mm image)
Legacy Sediments
A small creek has incised its way through legacy sediments many years after removal of the mill dam that trapped them.  Scour has exposed the rounded pebbles of a pre-dam streambed (at the waterline) and the gray soils of the accompanying floodplain wetland.  The brown deposits with the small tree perched therein are legacy sediments.
Legacy sediment erosion and streambed scour.
An example of legacy sediment erosion and severe scour of a streambed.  The roots of grasses atop the far bank do little but hold clumps of sod together so they might tumble into the water and wash away.  Without rehabilitation, this segment of creek will release tons of nutrient-rich sediment with each storm event.
Live Staking a Slumping Streambank
In lieu of removing legacy sediments, planting trees to establish a forested riparian buffer is one method of attempting to stabilize their deposits in former mill ponds.  Known as “live stakes”, cuttings of Black Willow (Salix nigra) or shrub dogwood (Cornus sp.) can be driven into the slumping banks to take root and possibly reduce erosion.  (Vintage 35mm image)
A diorama depicting a stream and floodplain choked with legacy sediments.
A diorama depicting rehabilitation of an impaired watercourse.  Above, grazing livestock aggravate erosion of an embankment in a creek corridor choked with legacy sediments.  Below, the same segment after removal of legacy sediments.  The stream’s original substrate has been released from burial in silt, a vegetated riparian buffer has been planted, and a designated livestock watering/crossing area has been installed.

A diorama depicting an impaired stream after removal of sediment accumulations and installation of a vegetated riparian buffer and a designated livestock watering/crossing area.

Floodplain restoration on Chickies Creek in Lancaster County, Pennsylvania
Dam and legacy sediment removal followed by floodplain, stream, and riparian buffer restoration improves water quality while creating functional habitat for native bivalves, fish, and other aquatic life.
Floodplain and Stream Restoration on Rife Run in Lancaster County, Pennsylvania
A legacy sediment removal project shortly after completion of the excavation work.  On this stream in Lancaster County, the floodplain, stream, and wetlands were restored, and livestock fencing was installed to keep grazing animals out.  To complete rehabilitation of this segment, native vegetation was planted to establish a pollutant filtering riparian buffer of native trees, shrubs and herbaceous growth.  (Vintage 35mm image)
A mill pond after removal of legacy sediments.
A former mill pond as it appears one year after removal of legacy sediments and restoration of stream geomorphology.  Such projects provide potential habitat for the return of Unionidae mussels and their host fishes.

FISH PASSAGE

Safe Harbor Dam Fish Lift
Work to install fish passages that bridge the Susquehanna’s hydroelectric dams and remove low-head mill dams on the river’s tributaries has improved access for anadromous migratory fishes seeking to make their way upstream for spawning in the spring.  These projects have benefited the movements of resident fishes as well, including host species for some freshwater mussels.  Here, the lift at Safe Harbor Dam discharges fish into the raceway (left) and shad dash by the observation window (right) into Lake Clarke.  (Vintage 35mm images)
York Haven Dam Fish Passage
Seen here to the left is the York Haven Dam Fish Passage on Three Mile Island at Conewago Falls, the only “swim-through” facility on the lower Susquehanna that doesn’t utilize a lift.  To the right is the observation window where a biologist counts anadromous and other species of fishes during the spring migration.  (Vintage 35mm images)

RIPARIAN BUFFERS

Riparian Buffer and Streamside Livestock Fencing
Despite being located in farmland, this stream supports a community of at least two species of freshwater mussels.  Their occurrence is facilitated in large part by fencing that excludes grazing livestock from the creek and by a buffer of unmanicured vegetation that helps remove nutrients and prevent erosion.  (Vintage 35mm image)
Riparian Buffer Tree Planting
Planting native trees is an essential step for establishing a forested stream buffer to mitigate impairment caused by nutrient and sediment loading.  (Vintage 35mm image)
CREP Tree Planting
Programs including CREP (U.S.D.A’s Conservation Resource Enhancement Program) provide funding and incentives for installation of riparian buffers, streambank fencing, and numerous other conservation measures.  Contact your County Conservation District office for more information.  And don’t be shy about it.  Money often goes unused for lack of interest, not a lack of need to get the work done.  (Vintage 35mm image)

AQUATIC VEGETATION

Emergent Vegetation
Emergent vegetation along the shoreline of a stream, river, lake, or pond is an oft times missing component of an aquatic ecosystem.  The cult-like practice of keeping the borders of waterways “tidy” is well-entrenched in lower Susquehanna valley culture and it’s a big reason why the water is so filthy.  Dense emergent growth not only reduces erosion and traps silt, but it is also the irreplaceable consumer of the nutrients that occur in our waters from both natural processes and man-made sources including agriculture.  To effectively reduce the occurrence of algal blooms and eutrophication, plant coverage on a stocked pond like this may need to be as high as thirty percent, maybe more, in order to sequester the nitrates produced by the nutrient load in fish waste and lawn runoff.  (Vintage 35mm image)
A colony of emergent Spatterdock.
Spatterdock (Nuphar advena) is a native emergent plant of low-gradient streams that provides nutrient uptake as well as habitat enhancement for fish including host species for unionid glochidia.
American Eelgrass and Smallmouth Bass
Like emergent vegetation, submerged plants are important consumers of nutrients and are excellent breeding cover for aquatic organisms, including host fish for unionid mussels.  On bright sunny summer days, plants like this American Eelgrass (Vallisneria americana) are good producers of dissolved oxygen, just when the inhabitants of the river may need it most.  (Vintage 35mm image)

WETLANDS

Oxbow Wetland
Once found in floodplains bordering nearly all low-gradient segments of lower Susquehanna valley streams, natural wetlands like this oxbow are increasingly rare.  Most have been drained, filled, and often built upon.  And yes, this practice does continue, including the construction of houses and other buildings in floodways!  Wetlands are essential floodplain components, collecting, purifying, and evaporating or infiltrating stormwater.  During large storm events, these marshes and pools buffer the impacts of high water.  Once filled or disconnected from the stream, the water quality and flood control advantages they offer are lost.  Because they are also essential habitat for hundreds of species of plants and animals, wetlands should receive a level of protection commensurate with their importance.
Man-made wetlands with wildlife enhancements.
These man-made wetlands (unused lagoons at a water treatment facility) were planted and enhanced to catch, absorb, and purify stormwater runoff from both the surrounding grounds and the adjacent creek when it overflows during severe flooding events.  They now function as vernal pools and marsh.  Wildlife, including breeding turtles, frogs, and toads, moved in right away.  (Vintage 35mm image)

I’M WORRIED ABOUT THE BEAVER

Beaver lodge in beaver pond.
Imagine a network of brooks and rivulets meandering through a mosaic of shrubby, sometimes boggy, marshland, purifying water and absorbing high volumes of flow during storm events.  This was a typical low-gradient stream in the valleys of the Lower Susquehanna River Watershed in the days prior to the arrival of the trans-Atlantic human migrant.  Then, a frenzy of trapping, tree chopping, mill building, and stream channelization accompanied the east to west waves of settlement across the region.  The first casualty: the indispensable lowlands manager, the North American Beaver (Castor canadensis).  Without the widespread presence of beavers, stream ecology quickly collapsed.  Pristine waterways were all at once gone, as were many of their floral and faunal inhabitants.  It was a streams-to-sewers saga completed in just one generation.  So, if we really want to restore our creeks and rivers, maybe we need to give the North American Beaver some space and respect.  After all, we as a species have yet to build an environmentally friendly dam and have yet to fully restore a wetland to its natural state.  The beaver is nature’s irreplaceable silt deposition engineer and could be called the 007 of wetland construction…doomed upon discovery, it must do its work without being noticed, but nobody does it better.
Sandhill Cranes in Beaver Pond
The return of beaver-managed floodplains can provide opportunities for the return and/or recovery of uncommon, rare, and extirpated species.  Freshwater mussels benefit from the improvements in water quality while birds like these Sandhill Cranes (Antigone canadensis) are particularly fond of the wetland habitat created by North American Beavers.

STORMWATER MANAGEMENT

Clean Stormwater Inlet
Keeping storm inlets clear of debris and litter not only prevents street flooding, but also keeps pollutants out of stream corridors and retention facilities.  Cleaning up rubbish before it accumulates is something everyone can do to improve water quality.  (Vintage 35mm image)
Storm Drain Marker
Marking storm drains is a way to remind everyone that only they’re for rainwater only.  (Vintage 35mm image)
Vegetated Swale
Rain gardens and vegetated swales polish and infiltrate stormwater to help reduce runoff and pollution.  (Vintage 35mm image)
Rain Garden Model
A cutaway model displayed by Rapho Township in Lancaster County, Pennsylvania, showing how one might construct a rain garden on their property to infiltrate stormwater from a downspout, driveway, or other source.  Ideal plantings include species that like wet soil.  Try sedges (Carex sp.), rushes (Juncus sp.), spike rushes (Eleocharis sp.), Cardinal Flower (Lobelia cardinalis), Joe Pye Weed (Eutrochium sp.), Common Winterberry (Ilex verticulata), Common Buttonbush (Cephalanthus occidentalis), Silky Dogwood (Cornus amomum), and others.
Native Wildflower Meadow
Converting mowed space into a native wildflower meadow or a forest is a great way to clean up and infiltrate runoff from a parking lot, driveway, or other non-porous surface.  (Vintage 35mm image)
Vegetated Stormwater Retention Basin
Properly designed and maintained stormwater retention basins prevent rain from becoming stream-flooding runoff and instead percolate it into the ground to recharge the aquifer and maintain base flow in nearby creeks.  You and I are going to need that water someday, so don’t let it get away!  (Vintage 35mm image)

…AND FINALLY, ONE LAST PIECE OF ADVICE

If you don’t know why, please scroll down to the bottom of this page.
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