Cee Cee Ah Creek Westslope Cutthroat Trout Restoration Project Jason Olson - PowerPoint PPT Presentation

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Cee Cee Ah Creek Westslope Cutthroat Trout Restoration Project Jason Olson

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Title: Cee Cee Ah Creek Westslope Cutthroat Trout Restoration Project Jason Olson


1
Cee Cee Ah Creek Westslope Cutthroat Trout
Restoration Project Jason Olson
  • A partnership of the Kalispel Tribe of Indians,
    the Washington Department of Fish and Wildlife,
    and Washington State University Extension

2
Why Restoration of Westslope Cutthroat?
  • Important to the Kalispel Tribe and WDFW
  • KT and WDFW have a goal to recover native fish
  • WCT are Species of Concern, additional ESA
    listings unwarranted (Petitioned for ESA listing
    in 2002)

3
Why Cee Cee Ah Creek
  • Lower end of Cee Cee Ah Creek flows through the
    Kalispel Reservation.
  • Previous investment in instream habitat
    (structures, and planned culvert replacements and
    riparian improvements).
  • Decline of westslope cutthroat densities.
  • - 1996 baseline fish surveys found 118 BKT and 1
    WCT in snorkel stations upstream of the
    falls.
  • - 1997 to 2004 instream restoration monitoring
    found 1,767 BKT and 3 WCT.
  • - 2002 electrofishing to collect genetic samples
    could not find any WCT.
  • - WCT functionally extinct upstream of Cee Cee
    Ah Falls.

4
Options For Brook Trout Removal in Cee Cee Ah
Creek
  • Liberalized angling regulations
  • Physical removal via electrofishing
  • Dewatering
  • Explosives
  • Piscicides

With the exception of dewatering, the other
alternatives rarely result in complete
eradication. Alternatives require much more
time, labor and money.
5
Advantages of Cee Cee Ah Creek for a Piscicide
Treatment?
  • Suitable habitat for WCT to thrive
  • No grazing or range livestock nearby
  • No known domestic water rights that might be
    affected
  • Limited land owners downstream (U.S. Forest
    Service, Stimson Lumber Company, Riley Creek
    Timber and Kalispel Tribal land).
  • Little fishing in this section of the stream.
  • WCT are functionally extinct, so efforts to
    salvage WCT would not required.
  • Cee Cee Ah Falls to prevent reinvasion.

6
Study Area
7
Treatment Area
  • 5.2 miles of treatment
  • 31 drip stations
  • 1 hour travel time between stations
  • 4 hour treatment time
  • 37 staff members for first treatment

8
Treatments
  • Total of 4 treatments
  • - Two treatments 2 weeks apart in fall of 2008.
  • - One treatment in the fall of 2009.
  • - Final treatment in the fall of 2010.
  • Treatment 1,2 - removed approximately 6,700 BKT.
  • Treatment 3 - removed a handful of remaining BKT.
  • Treatment 4 - no fish were observed.

9
Tools Used in Cee Cee Ah Removal
Drip Station
Detox Station 2008, 2009
Detox Station 2010
Backpack Sprayer
10
Re-Introduction
  • Considerations
  • - Genetics
  • - Purity
  • Donor population
  • - Size
  • - Age structure
  • - Spawning timing
  • - Fecundity
  • Methods
  • - Translocations
  • - RSI (remote streamside Incubators)
  • - Egg tubes (buried in the gravel)
  • - Hatchery

11
Re-Introduction of Cee Cee Ah
  • Middle Creek and East Fork Smalle Creek were both
    determined to be pure WCT and in close proximity
    of the Cee Cee Ah watershed.
  • Middle Creek was chosen as the primary donor
    population.
  • In 2011, initial collection began on April 1st
    and went until May 3rd. (n14)
  • Collections were moved to East Fork Smalle
    Creek.(n86)
  • In 2012, 39 WCT were collected to spawn from
    Smalle Creek, only 18 were spawned.
  • - Size ranged from 149 to 208 mm.
  • - Fecundity ranged from 66 to 291 eggs.
  • - Total egg take was 2,086 eggs.

12
Tools Used in Cee Cee Ah Translocations
Electro-fishing
Spawning
Transportation
Otoliths
13
Results
  • Brook trout were successfully eradicated from Cee
    Cee Ah Creek above the falls.
  • 100 WCT successfully translocated to Cee Cee Ah
    Creek in 2011.
  • 2,086 Eggs were collected and fertilized in 2012
    producing 178 fry for release (despite poor flow
    conditions)
  • Natural recruitment documented in 2013.

14
Lesson Learned
  • Education and outreach (the good, bad, and ugly)
  • Plan and strategize for challenges presented by
    complex channel habitats (beaver ponds, springs,
    and side channels)
  • Staffing ability to implement project with less
    staff
  • - Treatment one 30-36 people.
  • - Treatment two and three 25 people.
  • Weather and stream flows unpredictable however
    we now know that we can have success in the worst
    case conditions.

15
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