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Johanna Weston - Cal Poly Center for Coastal Marine Sciences

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Evaluation of the Benewah<br />

Creek Restoration Project<br />

<strong>Johanna</strong> <strong>Weston</strong><br />

University of Dallas<br />

Dr. Chris Peery<br />

University of Idaho<br />

Dr. Dale Chess<br />

Angelo Vitale<br />

Coeur d’Alene Tribe Fisheries Program


Benewah Creek Restoration<br />

Evaluation<br />

‣ Benewah Creek Long-term<br />

Goals<br />

‣ Summer 2007 Monitoring Project<br />

• Stream Temperature Patterns<br />

• Macroinvertebrate Communities<br />

• Trout Populations<br />

• Snorkeling<br />

• Electroshocking<br />

‣ Conclusions


Coeur d'Alene Indian Reservation<br />

µ<br />

0 10<br />

Miles<br />

Plummer<br />

Benewah Creek<br />

US HWY 95<br />

£¤<br />

Moscow<br />

STATE HWY 8<br />

¬«<br />

http://inside.uidaho.edu<br />

http://seamless.usgs.gov


Benewah Creek<br />

‣ Splash Dam, Logging, and<br />

Grazing<br />

‣ Physical stream degradation<br />

‣ Non-native native brook trout (S.(<br />

fontinalis)<br />

‣ Coeur D’Alene D<br />

Tribe Fisheries<br />

Program<br />

‣ 3.2 miles of stream restoration<br />

Overall Goal: : Holistic revival<br />

westslope cutthroat trout (O. clarki lewisi)


Other Monitoring Methods<br />

‣ Habitat quality and physical changes<br />

measurements<br />

‣ Temperature patterns<br />

‣ O. clarki lewisi population assessments


Summer 2007 Project Goals<br />

‣ University of Idaho - NSF REU<br />

‣ Evaluate biological response of restoration<br />

ef<strong>for</strong>ts<br />

• Stream temperature patterns<br />

• Macroinvertebrate communities<br />

• Fish density and trout populations<br />

‣ Provide baseline data <strong>for</strong> index sites<br />

‣ Present methods <strong>for</strong> monitoring


Specific Study Sites<br />

‣ Completed restoration sections <strong>for</strong> 2005 and 2006<br />

‣ Started restoration section <strong>for</strong> 2007<br />

‣ Monitoring Sites 2007<br />

• Restored 2005<br />

• Restored 2006<br />

• Un-restored 2007<br />

• Highly Disturbed Reference - Meadow<br />

• Minimally Disturbed Reference - Pristine


Benewah Creek Restoration<br />

Evaluation<br />

‣ Benewah Creek Long-term Goals<br />

‣ Summer 2007 Monitoring Project<br />

• Stream Temperature Patterns<br />

• Macroinvertebrate Communities<br />

• Trout Populations<br />

• Snorkeling<br />

• Electroshocking<br />

‣ Conclusions


Stream Temperature<br />

‣ Temporal temperature patterns<br />

• Five Hobo Temperature Sensors<br />

• Air temperature<br />

• Every hour from 18 June to 20 July 2007<br />

‣ Spatial temperature patterns<br />

• Temperature probe<br />

• 19 June 2007


Temporal Steam Temperature<br />

Pattern<br />

30.00<br />

25.00<br />

20.00<br />

15.00<br />

R2005<br />

R2006<br />

Meadow<br />

Site 17<br />

Pristine<br />

10.00<br />

5.00<br />

0.00<br />

Date and Time


Temporal Air Temperature<br />

Pattern<br />

40.00<br />

35.00<br />

30.00<br />

25.00<br />

20.00<br />

15.00<br />

10.00<br />

5.00<br />

0.00<br />

-5.00<br />

Time and Date


Spatial Temperature Pattern<br />

Nine Mile Bridge<br />

!<br />

!<br />

Benewah Road<br />

Whitetail Creek<br />

! !!<br />

! ! !!<br />

!<br />

!<br />

! !<br />

! !! !<br />

! !<br />

!!<br />

!! !!! !!<br />

! !<br />

!<br />

!<br />

!<br />

!<br />

! !<br />

B e n e w a h C r e e k<br />

Temperature (oC) from 19 June 2007<br />

Temp<br />

! 0.0<br />

9.9<br />

10.0 - 10.5<br />

10.6 - 10.9<br />

11.0 - 11.1<br />

11.2 - 11.4<br />

11.5 - 11.7<br />

11.8 - 11.9<br />

12.0 - 12.2<br />

12.6 - 13.0<br />

14.0 - 14.2<br />

14.3 - 14.5<br />

14.6 - 14.7<br />

14.8 - 15.0<br />

15.1 - 15.3<br />

15.4 - 15.6


Stream Temperature Results<br />

‣ Same stream = same temperature patterns<br />

‣ Diurnal Cycle: 5 – 10 o C variation<br />

‣ Substantial variation moving downstream<br />

- More than just air temperature<br />

- Differences in riparian cover<br />

- Water depth, flow levels, and groundwater<br />

interaction


Benewah Creek Restoration<br />

Evaluation<br />

‣ Benewah Creek Long-term Goals<br />

‣ Summer 2007 Monitoring Project<br />

• Stream Temperature Patterns<br />

• Macroinvertebrate Communities<br />

• Fish and Trout Populations<br />

• Snorkeling<br />

• Electroshocking<br />

‣ Conclusions


Macroinvertebrates<br />

‣ 20 samples from 5 different stream<br />

reaches<br />

• Two pools and two riffles<br />

• Restored 2005, Restored 2006, Unrestored<br />

2007, Meadow, Pristine<br />

‣ 3-minute kicks with a d-netd<br />

‣ Samples sorted and identified to family


Abundance of Macroinvertebrates<br />

350<br />

300<br />

250<br />

200<br />

150<br />

100<br />

50<br />

0<br />

Restored 2005<br />

Unrestored 2007<br />

Pristine<br />

Restored 2006<br />

Meadow<br />

0 1 2 3 4 5 6<br />

Stream Section (Downstream to Upsteam)


Richness of Macroinvertebrates<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

R2005 R2006 UR2007 Meadow Pristine<br />

Stream Section (downstream to upstream)


Macroinvertebrates Diversity and<br />

Evenness<br />

2.500<br />

2.000<br />

1.500<br />

Shannon<br />

Diversity<br />

Evenness<br />

1.000<br />

0.500<br />

0.000<br />

R2005 R2006 UR2007 Meadow Pristine<br />

Section (downstream to upstream)


Macroinvertebrates Results<br />

‣ Pristine section has the greatest abundance,<br />

richness, and diversity values<br />

‣ Restored and degraded sections have lower and<br />

similar values<br />

‣ Upstream restoration<br />

impacts downstream<br />

communities


Benewah Creek Restoration<br />

Evaluation<br />

‣ Benewah Creek Long-term Goals<br />

‣ Summer 2007 Monitoring Project<br />

• Stream Temperature Patterns<br />

• Macroinvertebrate Communities<br />

• Trout Populations<br />

• Snorkeling<br />

• Electroshocking<br />

‣ Conclusions


Fish: Snorkeling<br />

‣ R-2005, R-2006, R<br />

Meadow, and Pristine<br />

reaches<br />

‣ Overlaps with macroinvertebrate sampling<br />

‣ Estimates population size and interaction<br />

‣ Counting and identification of all fish seen


Snorkeling Density and Population<br />

Section R2005 R2006 Meadow Pristine<br />

Area 555.3 m 2 743.6 m 2 177.1 m 2 226.1 m 2<br />

Count Density Count Density Count Density Count Density<br />

Cutthroat Trout 0 0 0.0 0 4 0.02 27 0.12<br />

Brook Trout 0 0 0.0 0 4 0.02 0 0.00<br />

Non-salmonid 332 0.71 550.0 0.74 92 0.51 10 0.04<br />

Total 332 0.71 550.0 0.74 100 0.55 37 0.16<br />

% Density of<br />

Salmonids *** 0 0 7.3 75<br />

% Density of Cutthroat 0 0 3.6 75<br />

% Density of Non Trout 100 100 92.7 25


Fish: Electroshocking<br />

‣ Three pass electroshocking<br />

‣ All surfaced fish collected and counted<br />

‣ WCT and BT were weighed and<br />

measured<br />

‣ Brook trout were<br />

exterminated


Electroshocking Density and Population<br />

R-2005 R-2006 Meadow Pristine<br />

Area 555.3 m 2 743.6 m 2 177.1 m 2 226.1 m 2<br />

Fish Count Density Count Density Count Density Count Density<br />

Sculpin 13 0.023 1 0.001 11 0.062 19 0.084<br />

Longscale Sucker 0 0 3 0.004 0 0 0 0.000<br />

Red Sided Shiner 55 0.099 9 0.012 92 0.519 2 0.009<br />

Longnose Dace 1 0.002 1 0.001 11 0.062 1 0.004<br />

Brook Trout 1 0.002 3 0.004 18 0.102 23 0.102<br />

Cutthroat Trout 0 0 0 0.000 0 0 9 0.040<br />

Total 70 0.126 17 0.022 132 0.745 54 0.239<br />

% Density of<br />

Salmonids *** 1.6 18.2 14.9 59.4<br />

% Density of<br />

Cutthroat 0.0 0.0 0.0 16.7<br />

% Density of Non Trout 98.4 81.8 85.1 23.9


Fish Results<br />

‣ Pristine significantly showed highest<br />

percent density of salmonids<br />

• Cutthroats only seen in the pristine section<br />

• Increased trout density in the pristine<br />

‣ Snorkeling and electroshocking give<br />

similar trends


Benewah Creek Restoration<br />

Evaluation<br />

‣ Benewah Creek Long-term Goals<br />

‣ Summer 2007 Monitoring Project<br />

• Stream Temperature Patterns<br />

• Macroinvertebrate Communities<br />

• Trout Populations<br />

• Snorkeling<br />

• Electroshocking<br />

‣ Conclusions


Conclusions<br />

‣ Restoration affects stream temperature<br />

‣ Pristine trended to higher abundance,<br />

richness, and diversity of<br />

macroinvertebrate communities<br />

‣ Restoration limiting trout habitat<br />

• Pristine contains physical and biological<br />

factors to provide cutthroat trout habitat


Discussion<br />

‣ Trends in stream condition post-restoration not<br />

as strong as expected<br />

‣ Pristine sections still best <strong>for</strong> WCT recovery<br />

‣ Restored sections experience lasting restoration<br />

disturbances<br />

‣ Restoration that has a shorter recovery time a<br />

better option than no intervention


Recommendations<br />

‣ Analyze habitat qualities<br />

‣ Measure flow, stream depth,<br />

and groundwater interaction<br />

‣ Larger sample sizes<br />

‣ Seasonal changes in macroinvertebrate and fish<br />

communities<br />

‣ Fish growth and spawning locations


Evaluation of the Benewah Creek<br />

Restoration Project<br />

Dr. Chris Peery<br />

Coeur d’Alene d<br />

Tribe<br />

Fisheries Program<br />

Kal Johnson<br />

REU Students<br />

University of Idaho<br />

National Science<br />

Foundation<br />

RRNW <strong>for</strong> this opportunity

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