Fawnsfoot (Truncilla donaciformis) COSEWIC assessment and status report: chapter 7

Population Sizes and Trends (1)

Search effort

Historical surveys

Based on records from the Lower Great lakes Unionid Database, the Fawnsfoot was historically (1930-1996) found in Lake Erie, Lake St. Clair and the Detroit, Niagara, Sydenham and Grand rivers. Approximately two-thirds of the 43 historical records are from museum specimens that have no information on search effort associated with them. Information on sampling methods and search effort is available for the remaining records, which were taken from surveys published in the literature. Table 1 provides a summary of this information. Surveys conducted on the Saugeen and Thames rivers are included in Table 1 because the Fawnsfoot was recently recorded from these rivers. A variety of quantitative and semi-quantitative sampling techniques were used in the historical surveys.

Recent Surveys

The Lower Great Lakes Unionid Database contains 15 recent (1997-2007) records for the Fawnsfoot from the Grand, Thames and Sydenham rivers, Muskrat Creek in the Saugeen River watershed, and Lake St. Clair. All but one of these records is accompanied by information on sampling methodology and search effort. The remaining record, from Muskrat Creek, is from a survey targeting other benthic invertebrates. Southwestern Ontario, which encompasses the range of the Fawnsfoot, has been extensively surveyed for freshwater mussels over the past ten years. Surveys have been conducted at approximately 300 different sites in 11 systems. Table 2 provides a summary of the sampling methods and search effort used in these surveys. It should be noted that different sampling techniques may provide different types of data. Semi-quantitative methods (timed-search surveys while wading, snorkelling or using SCUBA gear) provide data on the presence/absence of species and their relative abundance. Quantitative methods, i.e., methods that sample a defined area of the substrate surface using quadrats, grabs, circular plots or line transects, provide additional data on mussel densities. The above-described methods detect only those mussels visible at the sediment surface, all of which would be adults. Quadrat surveys with excavation, i.e., where the substrate in each quadrat is searched to a depth of about 10 cm, have been used at ~ 10% of the sites surveyed to date. This very time-consuming technique detects both adult mussels occurring at the sediment surface and juvenile mussels that tend to burrow deeply in the substrate (see Biology). The latter method can therefore provide additional data on recruitment.

Table 1. Summary of historical (1930-1996) mussel sampling effort within the range of the Fawnsfoot
Water body Number of sites Year Effort Notes Source
Lake St. Clair 29 1986, 1990, 1992, 1994 10 x 0.5 m² quadrats per site per year   Nalepa et al. 1996
Lake St. Clair 2 1990, 1992 20 x 1 m² quadrats includes 2 of Nalepa et al.’s (1996) sites Gillis and Mackie 1994
Detroit River 13 1982-83 SCUBA searches over 500 m² area over 60 minute period. Additional 15-30 min if live unionids detected.   Schloesser et al. 1998
Detroit River 17 1992 SCUBA searches over 500 m² area over 60 minute period. Additional 15-30 min if live unionids detected.   Schloesser et al. 1998
Detroit River 9 1994 SCUBA searches over 500 m² area over 60 minute period. Additional 15-30 min if live unionids detected.   Schloesser et al. 1998
Lake Erie 40 1930 drag-dredge?   Wright 1955
Lake Erie ? 1951-52 204 samples taken from an unknown number of sites using a 42 x 16 cm drag-dredge   Wood 1963
Lake Erie 15 1973-74 29 samples taken from 15 sites using a 42 x 16 cm drag-dredge   Wood and Fink 1984
Lake Erie 17 1961, 1972, 1982 3-5 benthic grabs per site with either a Ponar or Peterson sampler.   Nalepa et al. 1991
Lake Erie 17 1991 3 x 0.05 m² Ponar grabs and 5 min tow with 0.46 x 0.26 cm epibenthic sled   Schloesser and Nalepa 1994
Saugeen River 6 1993-94 1 person-hour while wading   Morris and Di Maio 1998-1999
Sydenham River 12 1971 0.7-> 4 person-hours while wading   Clarke 1972
Sydenham River 22 1985 minimum 1 person-hour while wading includes 12 of Clarke’s (1972) sites Mackie and Topping 1988
Sydenham River 16 1991 0.4-8.0 person-hours while wading most productive of Clarke’s (1972) sites Clarke 1992
Thames River 1 1983 240 x 0.5 m² quadrats   Salmon and Green 1983
Thames River ? 1993 1 person-hour   Bowles 1994
Thames River 16 1994 1 person-hour while wading   Morris and Di Maio 1998-1999
Thames River 16 1995 1 person-hour while wading includes site of Salmon and Green (1983) and overlap with Bowles (1994) Morris 1996
Grand River 115 1970-72 no precise effort reported per site but description of methods reported   Kidd 1973
Grand River 70 1995 1.5 person-hours while wading and extra 1.5 person-hours when stream order greater than 4 (using SCUBA) extra effort directed at surveying deeper areas Mackie 1996

 

Table 2. Summary of current (1997-2007) mussel sampling effort within the range of the Fawnsfoot
Water body Number of sites Year Effort Notes Source
Grand River 4 2007 48-65 x 1 m² quadrats with excavation all sites included in Metcalfe-Smith et al. 2000b Morris unpublished data
Lake St. Clair 3 1998 10 transects at 3 depths (1, 2.5 and 4 m) with 5 x 1 m² quadrats and 20 Ekman grabs in each transect   Zanatta et al. 2002
Lake St. Clair 60 1999 sites < 2.0 m deep employed 0.75 person-hours of snorkelling effort and if mussels present an additional 0.75 person-hours was spent; sites > 2.0 m deep employed 0.5 person-hours of SCUBA effort includes 10 locations surveyed in 1998 Zanatta et al. 2002
Lake St. Clair 10 2000 1.5 person-hours of snorkelling includes 10 sites from previous years Zanatta et al. 2002
Lake St. Clair 9 2001 5-21 x 65 m² circular plots surveyed using snorkellers includes 4 previously sampled sites Zanatta et al. 2002
Lake St. Clair 18 2003 10 x 195 m² circular plots surveyed using snorkellers 9 sites in Canadian waters of delta, 9 sites in U.S. waters Metcalfe-Smith et al. 2004
Lake St. Clair 10 2003 1 person-hour of snorkelling 2 sites in Canadian waters of delta, 8 sites in U.S. waters Metcalfe-Smith et al. 2004
Lake St. Clair 4 2005 3-4 person-hours of snorkelling   Metcalfe-Smith et al. 2005c
Detroit River 1 1997 4 x 120 m² line transects   Schloesser et al. 2006
Detroit River 4 1998 500 m² area searched for 60 minutes using SCUBA; second 500 m² area searched for 25 minutes sites where live unionids were observed in 1992 and 1994 Schloesser et al. 2006
Detroit River 1 1998 10 x 1 m² quadrats within a 10 m x 10 m grid   Schloesser et al. 2006
Lake Erie 6 2001 approximately 2 person-hours of snorkelling   D. Zanatta and D. Woolnough unpublished data
Lake Erie 12 2005 1.5 person-hours of snorkelling   D. McGoldrick unpublished data
Lake Erie 5 2005 beach search for shells   D. McGoldrick unpublished data
Niagara River 22 2001-2002 0.5 person-hours of snorkelling plus 0.5 person-hours if mussels found during first effort U.S. waters near Grand Island New York Power Authority 2003
Saugeen River 8 2006 4.5 person hours while wading timed-search sampling technique used in this and other inland rivers is described in Metcalfe-Smith et al. 2000a Morris et al. 2007
Maitland River 11 1998, 2003 4.5 person hours while wadsing   McGoldrick and Metcalfe-Smith 2004
Bayfield River 18 2007 4.5 person hours while wading   Morris unpublished data
Ausable River 21 1993-94, 1998-02 4.5 person hours while wading    
Ausable River 7 2006 69-75 x 1 m² quadrats with excavation   Staton pers. comm. 2007
Sydenham River 17 1997-98 4.5 person hours while wading   Metcalfe-Smith et al. 2003
Sydenham River 15 1999-03 60-80 x 1 m² quadrats with excavation includes 12 sites surveyed in 1997-98 Metcalfe-Smith et al. 2007
Thames River 48   4.5 person hours while wading   Morris and Edwards 2007 and unpublished data
Thames River 5 2004-05 60-80 x 1 m² quadrats with excavation sites included in Morris and Edwards 2007 Morris unpublished data
Grand River 24   4.5 person hours while wading   Metcalfe-Smith et al. 2000b

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