Western pearlshell mussel (Margaritifera falcata)

Category: Molluscs
Vulnerability to climate change (More details)

Moderate

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In Washington, the western pearlshell mussel is uncommon and is declining or extinct over much of its range due to habitat alteration and pollution. It has been extirpated from much of the mainstem Columbia and Snake Rivers. The western pearlshell is long-lived, sedentary, and sensitive to environmental change, so it is considered an excellent indicator of water quality.

Freshwater mussels have been greatly affected by dams and annual water drawdowns, as well as degraded water quality resulting from development and agriculture. Many historical sites no longer support mussels, and many local populations no longer successfully reproduce.

Description and Range

Physical description

Western pearlshell is a bivalved freshwater mollusk. They have an oblong shape, and they are up to 5 inches long. Their shell may be light brown, dark brown or black. The shell is curved on the top and somewhat concave on the bottom along the ventral margin. For more details (including photos), see the Xerces Society’s guide to Freshwater Mussels of the Pacific Northwest.

Ecology and life history

Freshwater mussels are found in shallow habitats in permanent bodies of water, including creeks, rivers, and ponds generally at low elevations. Mussels tend to concentrate in areas of streams with consistent flows and stable substrate conditions. They are often absent or sparse in high-gradient, rocky rivers, but are frequently encountered in low-gradient creeks and rivers, perhaps because they provide a variety of habitat conditions, reliable flow, good water quality, and diverse fish communities. The mussels are filter feeders that consume phytoplankton and zooplankton suspended in the water.

Western pearlshell mussels inhabit cold creeks and rivers with clear, cold water and sea-run salmon or native trout including waterways above 5,000 feet in elevation. These mussels are typically found at depths of 1.5 to 5 feet, and they tend to congregate in areas with boulders and gravel substrate, with some sand, silt and clay. These mussels occur in waterways with low velocities and stable substrates and are frequently found in eddies or pools and areas with stones or boulders that likely shelter mussel beds from scour during flood events. This species appears to be intolerant of sedimentation.

Freshwater mussels have a complex life cycle. They have separate sexes, although hermaphrodites (individuals with male and female traits that are capable of self-fertilization) have been documented for some North American species, including the western pearlshell. During breeding, males release sperm into the water and females filter it from the water for fertilization to occur. Embryos develop into larvae called glochidia, which are released into the water and must encounter and attach to a fin or gill filaments of host fish. Glochidia form a cyst around themselves and remain on a host for several weeks. They subsequently release from the host fish and sink to the bottom, burrow in the sediment and remain buried until they mature.

Like other freshwater mussels, western pearlshell mussels rely on host fishes to reproduce and disperse. Because freshwater mussels are not able to move far on their own, their association with fish allows them to colonize new areas or repopulate areas from which they have been extirpated. During their lives, mussels may move less than a few yards from the spot where they first landed after dropping from their host fish. Documented host fishes for western pearlshells include cutthroat trout, rainbow/steelhead trout, Chinook salmon, and brown trout, and a number of other fish are considered potential hosts.

Freshwater mussels that live in dense beds, including western pearlshell and western ridged mussels, provide an important water purification service; they can filter suspended solids, nutrients and contaminants from the water column and collectively improve water quality by reducing turbidity and controlling nutrient levels.

Western pearlshell mussels have an average life span of approximately 60 to 70 years, although some individuals are thought to have lived more than 100 years. Because this species is sedentary, sensitive to environmental changes, and long-lived, it can be an excellent biological indicator of water quality.

Geographic range

The range of the western pearlshell mussel extends from Alaska and British Columbia south to California and east to Nevada, Wyoming, Utah and Montana; it is apparently most abundant in Oregon, Washington, Idaho and British Columbia.

In Washington, western pearlshells have been extirpated from much of the mainstem Columbia and Snake Rivers; substantial declines, die-offs, or lack of recent reproduction have also been reported from the SanPoil River (Ferry County), Kettle River (Stevens County), the Little Spokane River (Spokane County), Snohomish River, Muck Creek (Pierce County), Bear Creek (King County), and Nason Creek (Chelan County). High levels of arsenic and organochlorine pesticides were found in the tissues of other mussel species collected from the mid-Columbia River during that survey.

This species has also been extirpated from northern Nevada, from most areas in northern Utah, several rivers in Montana, and numerous other locations. In addition, there are reports of populations of western pearlshells that apparently have not reproduced for decades. Populations of such a long-lived species may appear stable, when in fact they are not reproducing; populations showing repeated reproduction, evidenced by multiple age classes, are now rare.

For a map of range-wide distribution and conservation status of this species, check out Nature Serve Explorer.

Climate vulnerability

Sensitivity to climate change

Moderate

Western pearlshell mussels are a very long-lived species with lifespans of up to 100 years and have experienced significant declines over the past few decades. This species is generally found in shallow pools of freshwater streams and reservoirs with good water quality and a sufficient abundance of small fish who serve as hosts for mussels during their transition from the larval to juvenile stage. Therefore, their main sensitivity is likely to stem from climate-induced changes in water quality and host fish abundance. For instance, increased intensity of winter storms could lead to higher flow in rivers and increased nutrient runoff, both of which would degrade and reduce available mussel habitat. For this species, high levels of river discharge have been found to result in decreased recruitment, and higher nutrient levels have been associated with decreased juvenile growth and increased mortality. Additionally, increases in water temperature and nutrient runoff could lead to altered abundance of host fish (e.g., juvenile salmon) for larval stage mussels, thus leading to declines in abundance. The long generation times of this species is likely to make response and recovery to adverse climate conditions more difficult.

Confidence: Moderate

Exposure to climate change

Moderate

  • Increased water temperatures
  • Altered flow regimes
Confidence: Low

Regulations

Rules and seasons

For current rules about harvesting shellfish in Washington, be sure to check the statewide Shellfish/Seaweed Species Rules.

Conservation

This species is identified as a Species of Greatest Conservation Need (SGCN) under the State Wildlife Action Plan (SWAP). SGCN-classified species include both those with and without legal protection status under the Federal or State Endangered Species programs, as well as game species with low populations. The WDFW SWAP is part of a nationwide effort by all 50 states and five U.S. territories to develop conservation action plans for fish, wildlife and their natural habitats—identifying opportunities for species' recovery before they are imperiled and more limited.

Conservation Threats and Actions Needed

  • Agriculture and aquaculture side effects
    • Threat: Pollution and siltation.
    • Action Needed: Protect water quality
  • Fish and wildlife habitat loss or degradation.
    • Threat: Pollution and siltation.
    • Action Needed: Protect water quality.
    • Threat: Suction dredging for gold.
    • Action Needed: Delineate and protect sites.

See the Climate vulnerability section for information about the threats posed by climate change to this species.

Resources

References

Frest, T. J. and E. J. Johannes. 1995. Interior Columbia Basin mollusk species of special concern. Final report to the Interior Columbia Basin Ecosystem Management Project, Walla Walla, WA. Contract #43-0E00-4-9112. 274 pp. plus appendices.

Jepsen, S., C. LaBar,and J. Zarnoch. 2012. Profile: Western pearlshell (Margaritifera falcata). The Xerces Society. 24 pp.

Jepsen, S., C. LaBar,and J. Zarnoch. 2011. Profile: California floater (Anodonta californiensis) / Winged floater (Anodonta nuttalliana). The Xerces Society. 31 pp.

Jepsen, S., C. LaBar, and J. Zarnoch. 2011. Profile: Western ridged mussel (Gonidea angulata) .The Xerces Society. 19 pp.

Nedeau, E. J., A. K. Smith, J. Stione, and S. Jepsen. 2009. Freshwater Mussels of the Pacific Northwest. 2nd edition. The Xerces Society. 51pp.

Other resources