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Effects of Jackson Lake Dam and Tributaries on the Snake River in ...

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<str<strong>on</strong>g>Effects</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>Jacks<strong>on</strong></str<strong>on</strong>g> <str<strong>on</strong>g>Lake</str<strong>on</strong>g> <str<strong>on</strong>g>Dam</str<strong>on</strong>g> <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

<str<strong>on</strong>g>Tributaries</str<strong>on</strong>g> <strong>on</strong> <strong>the</strong> <strong>Snake</strong> <strong>River</strong> <strong>in</strong> Gr<str<strong>on</strong>g>and</str<strong>on</strong>g><br />

Tet<strong>on</strong> Nati<strong>on</strong>al Park: a c<strong>on</strong>t<strong>in</strong>u<strong>in</strong>g analysis<br />

John (Jack) Schmidt, Nicholas Nels<strong>on</strong>,<br />

Susannah Erw<strong>in</strong><br />

Department <str<strong>on</strong>g>of</str<strong>on</strong>g> Watershed Sciences<br />

Utah State University<br />

(funded by Nati<strong>on</strong>al Park Service <str<strong>on</strong>g>and</str<strong>on</strong>g> U. S.<br />

Geological Survey


•What are <strong>the</strong> geomorphic impacts <str<strong>on</strong>g>of</str<strong>on</strong>g> JLD <strong>on</strong><br />

<strong>the</strong> <strong>Snake</strong> <strong>River</strong>? Have <strong>the</strong>se impacts<br />

changed through time? Do <strong>the</strong>se impacts<br />

change with distance downstream from<br />

<str<strong>on</strong>g>Jacks<strong>on</strong></str<strong>on</strong>g> <str<strong>on</strong>g>Lake</str<strong>on</strong>g> <str<strong>on</strong>g>Dam</str<strong>on</strong>g> <str<strong>on</strong>g>and</str<strong>on</strong>g> from significant<br />

tributaries?


History <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>Jacks<strong>on</strong></str<strong>on</strong>g> <str<strong>on</strong>g>Lake</str<strong>on</strong>g> <str<strong>on</strong>g>Dam</str<strong>on</strong>g><br />

•1908 – log crib dam completed<br />

•1910 – failure <str<strong>on</strong>g>of</str<strong>on</strong>g> log crib dam<br />

•1916 – permanent c<strong>on</strong>crete dam completed<br />

– raised lake level 39 ft<br />

•1980s – dismantled <str<strong>on</strong>g>and</str<strong>on</strong>g> rebuilt<br />

C<strong>on</strong>structi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> Palisades <str<strong>on</strong>g>Dam</str<strong>on</strong>g>: 1958


Predict<strong>in</strong>g channel change downstream<br />

from dams<br />

sediment load<br />

water discharge


<strong>Snake</strong> <strong>River</strong> below <str<strong>on</strong>g>Jacks<strong>on</strong></str<strong>on</strong>g> <str<strong>on</strong>g>Lake</str<strong>on</strong>g> <str<strong>on</strong>g>Dam</str<strong>on</strong>g><br />

<strong>Snake</strong> <strong>River</strong> below <str<strong>on</strong>g>Jacks<strong>on</strong></str<strong>on</strong>g> <str<strong>on</strong>g>Lake</str<strong>on</strong>g> <str<strong>on</strong>g>Dam</str<strong>on</strong>g><br />

1.2 10 4 2-Mar 3-May 4-Jul 4-Sep 5-Nov<br />

1 10 4<br />

A<br />

1916-1958 - regulated<br />

1916-1958 - estimated unregulated<br />

1959-2005 - regulated<br />

1959-2005 - estimated unregulated<br />

8000<br />

6000<br />

4000<br />

2000<br />

0<br />

Date


Reducti<strong>on</strong> <strong>in</strong> floods immediately<br />

below dam<br />

<str<strong>on</strong>g>Jacks<strong>on</strong></str<strong>on</strong>g> <str<strong>on</strong>g>Lake</str<strong>on</strong>g> reservoir<br />

capacity<br />

0.85 x 10 6 af<br />

actual<br />

no dam<br />

1917-1956: actual flood regime is -4% (2-yr) <str<strong>on</strong>g>and</str<strong>on</strong>g> -6% (10-yr) less than without JLD<br />

1957-2002: actual flood regime is -42% (2-yr) <str<strong>on</strong>g>and</str<strong>on</strong>g> -36% (10-yr) less than without JLD


25000<br />

<strong>Snake</strong> <strong>River</strong> at Moose<br />

DISCHARGE, IN CUBIC FEET PER SECOND<br />

20000<br />

15000<br />

10000<br />

5000<br />

<strong>Snake</strong><br />

<strong>River</strong><br />

at<br />

Flagg<br />

Ranch<br />

Buffalo Fork<br />

Pacific Creek<br />

1996<br />

<strong>Snake</strong> <strong>River</strong> near Moran<br />

0<br />

1/1/96 3/3/96 5/4/96 7/5/96 9/5/96 11/6/96 1/7/97


C<strong>on</strong>tributi<strong>on</strong>s from tributaries<br />

Pacific Creek<br />

64% 13% 23%<br />

Buffalo Fork<br />

width <str<strong>on</strong>g>of</str<strong>on</strong>g> arrow<br />

proporti<strong>on</strong>al<br />

to total annual<br />

water flow


<strong>Snake</strong> <strong>River</strong> below Buffalo Fork<br />

Discharge, cubic feet per sec<strong>on</strong>d<br />

1 10 10 44<br />

8000<br />

6000<br />

4000<br />

1916-1958 - estimated unregulated<br />

1959-2005 - estimated unregulated<br />

1916-1958 - regulated<br />

1959-2005 - regulated<br />

1.2 10 44 2-Mar 3-May 4-Jul 4-Sep 5-Nov<br />

2000<br />

00<br />

Date


<strong>Snake</strong> <strong>River</strong> below Buffalo Fork<br />

<strong>Snake</strong> <strong>River</strong> below Buffalo Fork<br />

2.5 10 4<br />

3 10 4 1920 1940 1960 1980 2000<br />

regulated<br />

estimated unregulated<br />

B<br />

Estimated 2-yr<br />

flood<br />

2 10 4<br />

1.5 10 4<br />

1 10 4<br />

5000<br />

0<br />

2-yr flood: 1916-1958 1959-2005<br />

regulated: 12,002 9753<br />

est. unregulated: 15,340 15,316<br />

Year<br />

Regulated 2-yr flood<br />

1958: completi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> Palisades <str<strong>on</strong>g>Dam</str<strong>on</strong>g> -22% 1916-1958<br />

-36% 1959-2005


Absolute changes <strong>in</strong> <strong>the</strong> sediment supply are unknown.<br />

?<br />

?<br />

Sediment comes<br />

from tributaries<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> channel banks


Balance <str<strong>on</strong>g>of</str<strong>on</strong>g> Water <str<strong>on</strong>g>and</str<strong>on</strong>g> Sediment<br />

sediment<br />

degrade aggrade<br />

water<br />

Assum<strong>in</strong>g that <strong>the</strong>re have been no l<strong>on</strong>g term changes<br />

<strong>in</strong> sediment supply, <strong>the</strong>re should be accumulati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

sediment <strong>in</strong> channel <str<strong>on</strong>g>and</str<strong>on</strong>g> floodpla<strong>in</strong>.


Anticipated channel changes where sediment surplus<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> reduced floods<br />

•Cross-secti<strong>on</strong><br />

•Channel narrow<strong>in</strong>g; <strong>in</strong>set floodpla<strong>in</strong>s<br />

How do <strong>the</strong>y vary downstream?<br />

What flows are necessary to <strong>in</strong>undate <strong>the</strong> alluvial deposits?<br />

•Planform<br />

–Has <strong>the</strong> rate <str<strong>on</strong>g>of</str<strong>on</strong>g> avulsi<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> channel change <strong>in</strong>creased or decreased<br />

with time? Where?<br />

Before flow regime change<br />

terrace floodpla<strong>in</strong> Channel at<br />

bank full<br />

terrace<br />

After flow regime change<br />

ab<str<strong>on</strong>g>and</str<strong>on</strong>g><strong>on</strong>ed<br />

floodpla<strong>in</strong><br />

Channel at<br />

new bank full<br />

<strong>in</strong>set<br />

floodpla<strong>in</strong>


Analysis <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

channel change<br />

us<strong>in</strong>g aerial<br />

photographs:<br />

•Aerial photographs<br />

•1945<br />

•1969<br />

•1990/1991<br />

•2002


1945-1969<br />

Many reaches with high channel<br />

activity<br />

Most reaches more depositi<strong>on</strong><br />

than erosi<strong>on</strong><br />

2 reaches more narrow; 1 reach<br />

wider<br />

Several reaches more braided<br />

Changes occurred close <str<strong>on</strong>g>and</str<strong>on</strong>g> far<br />

from tribs<br />

Cott<strong>on</strong>wood Creek<br />

Schwabachers L<str<strong>on</strong>g>and</str<strong>on</strong>g><strong>in</strong>g<br />

19<br />

18<br />

Moose<br />

W<br />

17<br />

N<br />

16<br />

Ditch Creek<br />

Downstream <str<strong>on</strong>g>of</str<strong>on</strong>g> JLD<br />

Deadmans Bar<br />

-<br />

1 2<br />

0 0.5 1 2 3 4 5 6 7 8<br />

15<br />

12<br />

14<br />

N<br />

13<br />

3<br />

11<br />

9<br />

4<br />

6<br />

W<br />

Kilometers<br />

10<br />

5<br />

8<br />

Pacific Creek to<br />

Buffalo Fork<br />

7<br />

Pacific Creek<br />

Buffalo Fork<br />

Spread Creek<br />

1 dam release > post-1958 10-yr RI<br />

Blw BF: 1 flood > post-1958 10-yr RI<br />

N<br />

Channel activity<br />

Change <strong>in</strong> braid<br />

<strong>in</strong>dex<br />

Change <strong>in</strong> width


1969-1990<br />

Many reaches with high activity<br />

Reaches ei<strong>the</strong>r had more erosi<strong>on</strong> or no net<br />

change<br />

2 reaches wider<br />

1 reach less braided; no significant<br />

changes elsewhere<br />

Changes occurred close <str<strong>on</strong>g>and</str<strong>on</strong>g> far from tribs<br />

Downstream <str<strong>on</strong>g>of</str<strong>on</strong>g> JLD<br />

1 2<br />

12<br />

14<br />

15<br />

3<br />

W<br />

9<br />

11<br />

13<br />

4<br />

6<br />

10<br />

5<br />

8<br />

Pacific Creek to<br />

Buffalo Fork<br />

7<br />

Pacific Creek<br />

Buffalo Fork<br />

Spread Creek<br />

16<br />

Deadmans Bar<br />

Cott<strong>on</strong>wood Creek<br />

Schwabachers L<str<strong>on</strong>g>and</str<strong>on</strong>g><strong>in</strong>g<br />

18<br />

19<br />

Moose<br />

17<br />

W<br />

Ditch Creek<br />

-<br />

0 0.5 1 2 3 4 5 6 7 8<br />

4 dam release > post-1958 10-yr RI<br />

Blw BF: 3 flood > post-1958 10-yr<br />

RI<br />

1974 big trib flood<br />

Kilometers


1990-2002<br />

Many reaches with high activity<br />

More reaches with net loss <str<strong>on</strong>g>of</str<strong>on</strong>g> floodpla<strong>in</strong><br />

1 reach wider; 1 reach narrower<br />

2 reaches more braided; 1 reach less<br />

braided<br />

Downstream <str<strong>on</strong>g>of</str<strong>on</strong>g> JLD<br />

1 2<br />

12<br />

14<br />

13<br />

3<br />

11<br />

9<br />

4<br />

6<br />

10<br />

5<br />

8<br />

Pacific Creek to<br />

Buffalo Fork<br />

7<br />

Pacific Creek<br />

Buffalo Fork<br />

Spread Creek<br />

Changes occurred close <str<strong>on</strong>g>and</str<strong>on</strong>g> far<br />

from tribs<br />

16<br />

15<br />

Deadmans Bar<br />

Schwabachers L<str<strong>on</strong>g>and</str<strong>on</strong>g><strong>in</strong>g<br />

17<br />

W<br />

2 dam release > post-1958<br />

10-yr RI<br />

Cott<strong>on</strong>wood Creek<br />

-<br />

Blw BF: 3 flood > post-1958<br />

10-yr RI<br />

19<br />

18<br />

N<br />

Ditch Creek<br />

1999 big trib flood<br />

Moose<br />

0 0.5 1 2 3 4 5 6 7 8<br />

Kilometers


Lower Floodpla<strong>in</strong><br />

Before 1958: 3-5 yr recurrence <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

<strong>in</strong>undati<strong>on</strong><br />

1-3m<br />

0.25-0.75m<br />

Post-1958: 9-17 yr recurrence<br />

Upper Floodpla<strong>in</strong><br />

Inundated ~1/yr before<br />

1958<br />

Now <strong>in</strong>undated ~ 1.5 yrs


Where does <strong>the</strong> sediment come from?<br />

?<br />

Sediment comes<br />

from tributaries<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> channel<br />

banks<br />

?


Bed mobility<br />

•Bed mobility – determ<strong>in</strong><strong>in</strong>g what moves <str<strong>on</strong>g>and</str<strong>on</strong>g> what flows are<br />

necessary to mobilize <strong>the</strong> bed<br />

•ability to move gravels <strong>in</strong>creases downstream<br />

•Bed not fully mobile immediately below dam<br />

•<strong>River</strong> is capable <str<strong>on</strong>g>of</str<strong>on</strong>g> fully mobiliz<strong>in</strong>g porti<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> <strong>the</strong> bed below<br />

tributaries


How do we calculate sediment transport rates?<br />

Qs = aQ b<br />

Pacific Creek Sediment Rat<strong>in</strong>g Curve<br />

10000<br />

1. Transport formulae<br />

q<br />

s<br />

( s −1)<br />

gD<br />

Inputs:<br />

- gra<strong>in</strong> size<br />

- channel dimensi<strong>on</strong>s<br />

- channel slope<br />

⎛<br />

= 8⎜<br />

⎝<br />

τ<br />

−<br />

τ<br />

c<br />

3<br />

( s −1)<br />

ρgD<br />

( s −1)<br />

ρgD<br />

⎞<br />

⎟<br />

⎠<br />

3/ 2<br />

Transport Rate (t<strong>on</strong>s/d<br />

1000<br />

100<br />

10<br />

2. Direct Measurement<br />

1<br />

100 1000 10000<br />

Discharge (cfs)


2006 Bedload Transport Measurements<br />

Pacific Creek:<br />

- 24 measurements<br />

3500<br />

3000<br />

2500<br />

2000<br />

1500<br />

1000<br />

500<br />

0<br />

April May June July<br />

Buffalo Fork:<br />

- 37 measurements<br />

4000<br />

3500<br />

3000<br />

2500<br />

2000<br />

1500<br />

1000<br />

500<br />

0<br />

April May June July


TR2 – Toutle <strong>River</strong> Bedload Sampler<br />

• Designed for sampl<strong>in</strong>g under c<strong>on</strong>diti<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> high velocity, turbulence <str<strong>on</strong>g>and</str<strong>on</strong>g> high<br />

sediment transport rate<br />

• Improved bedload sampl<strong>in</strong>g efficiency relative to Helley-Smith<br />

• Provides most representative bedload samples for sediment 1.0mm to<br />

128.0mm (Ryan, 2003)


C<strong>on</strong>clud<strong>in</strong>g thoughts…<br />

• Hydrology has been modestly affected<br />

• Absence <str<strong>on</strong>g>of</str<strong>on</strong>g> l<strong>on</strong>g term progressive channel<br />

change<br />

• Proposals for changes <strong>in</strong> dam operati<strong>on</strong>s to alter<br />

physical habitat must be based <strong>on</strong> analysis <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

sediment delivered from tributaries.

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