Fawnsfoot (Truncilla donaciformis) COSEWIC assessment and status report: chapter 12

Technical Summary

Truncilla donaciformis

Fawnsfoot – Troncille pied-de-faon

Range of Occurrence in Canada:

Ontario

Demographic Information

Generation time (average age of parents in the population)
estimated 6-12 yrs
Population trend and dynamics
Estimated percentage of reduction in total number of mature individuals over the last 3 generations.
Unknown
Projected percentage of reduction in total number of mature individuals over the next 10 years.
Unknown
Observed percentage reduction in total number of mature individuals over any 10 years period, over a time period including both the past and the future.
Unknown
Are the causes of the decline clearly reversible?
No
Are the causes of the decline clearly understood?
Yes
Are the causes of the decline clearly ceased?
No
Observed trend in number of populations
Decline
Are there extreme fluctuations in number of mature individuals?
No
Are there extreme fluctuations in number of populations?
No

Number of mature individuals in each population

Extent and Area Information

Estimated extent of occurrence (km²):
Historical - 51,238; Current - 24,952 km². Area contained within a convex polygon drawn to include all confirmed occurrences.
Observed trend in extent of occurrence:
Decline. Decline by 51%
Are there extreme fluctuations in extent of occurrence?
No. Estimated area of occupancy (km²)
128km²: St. Clair delta – 4 km²; Muskrat Creek – 4 km²; Sydenham River – 4 km²; Thames River – 112 km²; Grand River – 4 km²
Observed trend in area of occupancy
Decline
Are there extreme fluctuations in area of occupancy?
No
Is the total population severely fragmented?
Yes. Found in 5 widely separated locations.
Number of current locations
5. 2 of the 5 locations are based on single specimens.
Trend in number of locations
Decline
Are there extreme fluctuations in number of locations?
No
Observed trend in area of habitat
Decline. Area, extent and quality of habitat have all declined.

Quantitative Analysis

Not available.

Threats (actual or imminent, to populations or habitats)

  1. Dreissenid mussels have rendered much of the historical habitat in Lake St. Clair, the DetroitRiver and Lake Erie unavailable and pose a continuing threat to remaining populations in the St. Clair delta, Thames River and Grand River.
  2. River fragmentation resulting from instream barriers and dams may restrict the upstream movement of the host species (believed to be freshwater drum), thereby limiting the available habitat.
  3. Poor water quality resulting from rural and urban influences in the watersheds poses a threat as mussels in general are known to be sensitive to many aquatic pollutants.

Rescue Effect (immigration from an outside source)

Status of outside population(s)?
USA : No federal or state designations have been made although the Fawnsfoot is considered declining across its North American range and is ranked S3 or higher in 11 U.S. jurisdictions.
Is immigration known or possible?
No
Would immigrants be adapted to survive in Canada?
Unknown
Is there sufficient habitat for immigrants in Canada?
No
Is rescue from outside populations likely?
No

Current Status

COSEWIC: Endangered, April 2008

Status and Reasons for Designation

Status: Endangered

Alpha-numeric code:  A2ce; B2ab(i,ii,iii,iv,v)

Reasons for Designation: This freshwater mussel is widely distributed in central North America, with the northern portion of its range extending into the Lake Erie, Lake St. Clair and lower Lake Huron drainages of southwestern Ontario. It appears to have always been a rare species in Canada, representing < 5% of the freshwater mussel community in terms of abundance wherever it occurs. Approximately 86% of historical records are in waters that are now infested with zebra mussels and therefore uninhabitable. Zebra mussels, which were accidentally introduced into the Great Lakes, attach to the shells of native freshwater mussels, causing them to suffocate or die from lack of food. The species has declined dramatically and has been lost from four historical locations resulting in a 51% reduction in its range. It is now found in only five widely separated locations, two of which represent single specimens. In two locations, the species’ distribution may be limited by the presence of dams that restrict the movements of the frehswater drum, the presumed fish host of the juvenile mussels. Poor water quality resulting from rural and urban influences poses an additional continuing threat.

Applicability of Criteria

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2018-01-02