Restoration of Chamberlain Creek
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Transcript Restoration of Chamberlain Creek
Restoration
of
Chamberlain
Restoration of Chamberlain
Creek
Creek
Amy Clinefelter
Amy
Clinefelter
Riparian Wetland Research Program
Riparian Wetland Research Program
Presentation Outline
Describe the restoration efforts in the
Chamberlain Creek basin to date
Discuss restoration recommendations and
monitoring objectives
Describe one proposed restoration project
Discuss the impacts of whirling disease and
the need for future monitoring
Location of the Blackfoot
Watershed in Montana
Chamberlain Creek
•Chamberlain Creek originates in a wet meadow
complex at 6,000 feet
•Chamberlain Creek flows through a confined
valley with large boulders and dense instream
woody debris in the upper reaches
•The lower 4 miles have been impacted by
road building, water diversions, and improper
cattle management
•Chamberlain Creek joins the Blackfoot River
in what was once a large beaver complex
Chamberlain Creek Fishery
A stronghold for native westslope cutthroat
trout
A 1990 survey conducted by Fish, Wildlife
and Parks showed the highest density of
cutthroat in this tributary out of 20 sampled
Restoration objectives were developed to
protect the westslope cutthroat, a species of
concern
Restoration Objectives for
Chamberlain Creek
Restore stream channel to allow fish access
from the Blackfoot River
Improve recruitment of juvenile westslope
cutthroat to the Blackfoot River
Maintain fish passage and connectivity of
Chamberlain Creek to the Blackfoot River
Restoration Projects
Deferred grazing from riparian corridors
Leasing of water rights
Removal of irrigation ditch and diversions
Restoration of channel diversion for pond
development
1.5 miles of instream channel enhancement
Conservation easements on private land
through the Nature Conservancy
Location of former diversions and the
restored Pearson Creek tributary
Pearson Creek
Irrigation
Canal
•Fish Ladder installed to allow passage
upstream and downstream of a water
diversion
•This diversion feeds a pond on private land.
The fish ladder is immediately to the right
and the pond has overflow structures to
allow fish to return to the creek downstream.
•300 feet of the channel were severely
altered by heavy machinery to develop
a pond, and had to be regraded for
restoration.
•Newly constructed channel to restore
connectivity with the Blackfoot River.
Cottonwoods were placed at downstream
angles to produce fish habitat complexity.
•Other instream enhancements were done
to create habitat and prevent bank erosion.
Chamberlain Creek Westslope Cutthroat
Trout Catch per 1,000 feet
400
300
200
100
0
0.1
0.5
2.8
Stream Mile
3.8
Restored Connectivty
In 1998 the number of fish caught became
more balanced between reaches suggesting
that restoration efforts that removed fish
barriers and improved management helped
restore the connectivity of the creek.
Further Restoration
Recommendations
Evaluate culvert sizing and leaking
Erosion control program
Cross section monitoring
Continued monitoring of fish populations,
species genetics, and whirling disease
spread and infection intensity
Improvements to instream habitat diversity
in heavily channelized areas (addition of
instream wood)
•Old road crossings are areas that may benefit
from an erosion control plan or riparian
plantings.
•Road encroachment may allow the
establishment of invasive weeds and
excess sediment input to the stream.
Future Restoration Plans
In 2001, the USDI Bureau of Land
Management in cooperation with Fish,
Wildlife and Parks will begin restoration of
instream wood to Chamberlain Creek.
Many lower reaches of the creek were
cleared of instream wood when road
building occurred.
The Function of Coarse Woody
Debris in Fish Habitat
Provides cover
critical in high flow and winter
rearing habitat
Creates important hydrologic features such
as pools and backwaters
Stores organic sediment
Channel stability
Objectives for Restoring Woody
Debris to Chamberlain Creek
Increase the abundance and quality of
rearing habitat for fishes
Increase deposition of spawning gravels
Increase overall habitat complexity
Project Methods
Project will use 35 whole conifer trees
Wood will be added to nine cross sections
Placement will follow a random design to
mimic and enhance natural recruitment
Use of draft horse teams instead of heavy
machinery to minimize impacts
Project Monitoring
Evaluate and document changes in fish
populations in response to project
Fish population counts
Fish use of newly created habitat
Number of redds
• pebble counts
Cross section monitoring
aggradation and log movement
stream invertebrate assemblages
Other considerations
Whirling disease is a parasitic infection of
salmonid species effecting the spinal and
nervous systems and can be fatal in young
fish
Fish sampled from the Blackfoot River
tested positive for the first time in 1998
The following grading system was
developed to evaluate disease severity
Whirling Disease Grading
System
Average Infection Grade
Salmonid Population Impacts
Grade 0.00 - 1.00
No significant impacts
Grade 1.00 - 2.00
Minor population impacts
Grade 2.00 - 2.50
Possible problems in streams
of low recruitment
Fish population declines may
occur
Fish population declines will
occur
Grade 2.50 - 3.00
Grade 3.00 - 4.00
Chamberlain Creek Whirling Disease
Infection Rates
1997
1998
1999
Average Infection
Grade
0.00
0.16
2.71
Percent of fish
infected
0%
16%
93%
Whirling Disease Management
The average infection grade increased
greatly from 1998 to 1999.
Continued monitoring of the spread and
grade of the disease in the Blackfoot and its
tributaries is necessary.