Connectivity of Tributary Habitat to Lake Huron Troy Zorn Michigan Department of Natural Resources Fisheries Division David Reid and Lloyd Mohr Ontario.

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Presentation transcript:

Connectivity of Tributary Habitat to Lake Huron Troy Zorn Michigan Department of Natural Resources Fisheries Division David Reid and Lloyd Mohr Ontario Ministry of Natural Resources

Overall objective “Over the next two decades, restore an ecologically balanced fish community dominated by top predators and consisting largely of self-sustaining indigenous and naturalized species...” Source: Fish-Community Objectives for Lake Huron (1995)

Migrations have been described for at least 61 of 114 fishes in the Great Lakes region Examples Sources: Becker (1983); Trautman (1981); Scott and Crossman (1973)

Now Then Inland habitats available to fishes

Fish-Community Objectives for Lake Huron Highlights Salmonines- “Anadromous (stream-spawning) species should have a prominent place.” Percids- Saginaw Bay and eastern Georgian Bay walleye stocks “have suffered from environmental degradation or from overfishing and require rehabilitation.” Esocids- “preservation and enhancement of spawning and nursery habitat will be critical” for maintaining populations

Fish-Community Objectives for Lake Huron Highlights Lake sturgeon- Lake Huron population was “..aggravated by damming of larger rivers, which provided spawning and nursery habitat.” Species diversity- protect and rehabilitate habitat “..stocking of fish must not be regarded as a substitute for nurturing natural populations and care of habitat.” Habitat manipulation options are usually limited to nearshore environments and tributary streams.

Dams alter river functions and the Lake Huron fish community Dams impound highest-gradient rapids and block migrations of Lake Huron fishes to existing rapids further upstream. Taxa affected include trout, salmon, lake sturgeon, whitefish, walleye. Dams disrupt sediment transport needed to maintain delta wetlands at river mouths. Species affected include yellow perch, northern pike, muskellunge. Major dam locations

What can we do? Develop decision support tools Use them to target effort and build consensus Without dams With dams

Our basin-level “toolbox” is presently limited Lake Huron GIS Project will help

What else can we do? Be opportunistic in regards to fish passage and dam removal Provide incentives for dam-owners considering these options Take advantage of existing opportunities

Lake Sturgeon Objective: To increase the species’ abundance to the extent that it no longer has threatened status in U.S. waters.

Extinct spawning habitat for lake sturgeon

Lake Sturgeon Potential Adapted from Seelbach et al. (1997) Yellow = High Red = Medium Green = Low Gray = No data See notes

Lake sturgeon potential Yellow= high Red= medium Source: Lake Sturgeon Rehabilitation Strategy (MDNR Fish Division)

Lake sturgeon potential and dams Yellow= high Red= medium Source: Lake Sturgeon Rehabilitation Strategy (MDNR Fish Division)

Hydroelectric project locations

Au Sable River Gradient Distribution from South Branch Au Sable River to river mouth

Biological potential of existing high-gradient habitats between Mio and Foote dams for Lake Huron fishes Adult lake sturgeon run 12.2 km of >0.95 m/km x 1,180 fish per km = 14,440 fish June young-of-year chinook salmon 18.8 km of >0.87 m/km x 551,195 fish per km = 10,382,360 fish September young-of-year steelhead 18.8 km of >0.87 m/km x 15,443 fish per km = 290,908 fish

Michigan’s Golden Opportunity: Consumers Energy has agreed to provide for design, construction, operation, and maintenance of fish passage facilities on the Au Sable River. …IF Source: Settlement Agreement (1992)

…agencies and public can agree on how it should be done.

Fish Passage Concerns Contaminants Art credit: Department of Fisheries and Oceans

Productivity of bald eagles in the Lower Peninsula Source: D. Best, USFWS, 2000

Average number of bald eagles fledged per nest type in Michigan’s Lower Peninsula Source: D. Best, USFWS, 2000 Nest type Inland 1.15 Anadromous 1.06 Great Lakes = Stable and 1.0 = Healthy (Sprunt et al. 1973)

Fish Passage Concerns Contaminants Social issues Possible solutions Monitor wildlife Limit salmon runs Close ladders in Fall Regulate salmon fishery upstream of dams Art credit: Department of Fisheries and Oceans

Fish Passage Concerns Contaminants Social issues Sea lamprey Possible solutions Monitor wildlife Limit salmon runs Close ladders in Fall Manage sea lamprey Art credit: Department of Fisheries and Oceans

Fish Passage Concerns Potential competition with wild trout stocks

What’s needed to restore Lake Huron fish migrations to the Au Sable River? Cooperation Effort Compromise Flexibility

Conclusions Connections between habitats are important for many Lake Huron fishes Connections between Lake Huron and its tributaries are very limited Tools such as the Lake Huron GIS Project are needed to show problems, identify opportunities, and direct rehabilitation efforts We need to foster efforts by others and fully utilize existing opportunities to restore connections between Lake Huron and its tributaries

Lower Peninsula bald eagle productivity Young fledged per nest Nest type Inland Anadromous Great Lakes = Stable and 1.0 = Healthy (Kubiak and Best 1991)

Estimated potential production of three Lake Huron fishes in the Au Sable River between Mio and Foote dams Whelan estimated >5 ft/mi gradient on a cfs river would support adult lake sturgeon runs of 1900 fish per mile (Thuemler 1985; Auer 1995; Auer 1996). Estimated production from a 4.6 ft/mi gradient reach on Manistee River was 887,000 June YOY chinook salmon and 24,800 September YOY steelhead per mile (Rutherford et al. 1997)

Bald eagles fledged from inland and anadromous and Great Lakes nests in the Lower Peninsula

Number of occupied bald eagle nests in the Lower Peninsula

Potamodromous fishery of the Au Sable River Occurs in 10 of 152 miles of the river’s mainstem In 1987: 33,599 angler days spent >12,600 Great Lakes salmonids harvested Estimated value of $1,814,000

Estimated annual value of resident trout and potamodromous fisheries between Mio and Foote dams Potamodromous fishery 82.8 miles x 3,168 angler days per mile x $54 per angler day = $14,164,762 Conservative estimate = $5 million Resident trout fishery 82.8 miles x 685 angler days per mile x $54 per angler day = $3,062,772 Conservative estimate = $2 million Conservative total = $7 million

Economics with and without dams Annual values in millions of dollars

Dams on the Lower Au Sable River: Inundate rare, very-high gradient habitats Disrupt sediment and woody debris transport Increase summer temperatures and prevent night- time cooling Reduce aquatic insect diversity and density Produce marginally productive, cool ponds Reduce populations of coldwater fishes Block fish migrations Eliminate/impair natural reproduction of coldwater fishes Affect human use of the river