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Mitigation for the Construction and Operation of Libby Dam

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Chapter 2 Tables<br />

Table 1. Design specifications <strong>for</strong> <strong>the</strong> upper <strong>Libby</strong> Creek (Clevel<strong>and</strong>’s) channel restoration<br />

project. ...............................................................................................................................130<br />

Table 2. Mean bankfull width, depth, width to depth ratio <strong>and</strong> cross sectional area <strong>for</strong> 5 cross<br />

sectional surveys in 1999 <strong>and</strong> 9 different cross sectional surveys in 2002 <strong>and</strong> 2003.<br />

Variance estimates <strong>for</strong> annual mean values are presented in paren<strong>the</strong>ses. An analysis <strong>of</strong><br />

variance (ANOVA) was pre<strong>for</strong>med <strong>for</strong> each parameter, <strong>and</strong> <strong>the</strong> P value is presented <strong>for</strong><br />

each ANOVA. The results <strong>of</strong> subsequent multiple comparisons (Fisher’s Least Significant<br />

Difference) are also presented (alpha = 0.05)....................................................................133<br />

Table 3. Mean bankfull width, depth, maximum bankfull depth, <strong>and</strong> length measured from 20<br />

pools in 2002 <strong>and</strong> 2003. Variance estimates <strong>for</strong> annual mean values are presented in<br />

paren<strong>the</strong>ses. A statistical comparison <strong>of</strong> annual mean values was not per<strong>for</strong>med because <strong>the</strong><br />

20 pools represented all pools within <strong>the</strong> project area, <strong>and</strong> <strong>the</strong>re<strong>for</strong>e represents a complete<br />

census. The percent change <strong>for</strong> each parameter from 2002 to 2003 is also presented. ....133<br />

Table 4. Design specifications <strong>for</strong> <strong>the</strong> Grave Creek Phase I Restoration Project.....................136<br />

Table 5. Mean bankfull width, depth, width to depth ratio, cross sectional area, <strong>and</strong> maximum<br />

depth <strong>for</strong> 6 permanent cross sectional surveys in 1999, 2002 <strong>and</strong> 2003. Variance estimates<br />

<strong>for</strong> annual mean values are presented in paren<strong>the</strong>ses. A repeated measures analysis <strong>of</strong><br />

variance (RPANOVA) was pre<strong>for</strong>med <strong>for</strong> each parameter, <strong>and</strong> <strong>the</strong> P value is presented <strong>for</strong><br />

each RPANOVA. The results <strong>of</strong> subsequent multiple comparisons are also presented...137<br />

Table 6. Mean bankfull width, maximum bankfull depth, <strong>and</strong> length measured from 27 pools in<br />

2002 <strong>and</strong> 2003. Variance estimates <strong>for</strong> annual mean values are presented in paren<strong>the</strong>ses. A<br />

statistical comparison <strong>of</strong> annual mean values was not per<strong>for</strong>med because <strong>the</strong> 27 pools<br />

represented all pools within <strong>the</strong> project area, <strong>and</strong> <strong>the</strong>re<strong>for</strong>e represents a complete census.<br />

The percent change <strong>for</strong> each parameter from 2002 to 2003 is also presented...................137<br />

Table 7. Mean cross sectional area, bankfull width, depth, maximum bankfull depth, <strong>and</strong> width<br />

to depth ratio measured <strong>for</strong> 4 riffles in <strong>the</strong> existing stream channel <strong>and</strong> 10 riffles in <strong>the</strong><br />

stream channel shortly after construction in <strong>the</strong> fall <strong>of</strong> 2003 (as built) <strong>for</strong> <strong>the</strong> Young Creek<br />

State L<strong>and</strong>s Stream Restoration Project. Variance estimates <strong>for</strong> annual mean values are<br />

presented in paren<strong>the</strong>ses. Mean values between treatments were compared using a t-test,<br />

<strong>and</strong> <strong>the</strong> one tailed p-value <strong>for</strong> each comparison is presented. The percent change <strong>for</strong> each<br />

parameter between treatments is also presented................................................................142<br />

Table 8. Mean cross sectional area, bankfull width, depth, maximum bankfull depth, <strong>and</strong> width<br />

to depth ratio measured <strong>for</strong> 2 pools in <strong>the</strong> existing stream channel <strong>and</strong> 8 pools in <strong>the</strong> stream<br />

channel shortly after construction in <strong>the</strong> fall <strong>of</strong> 2003 (as built) <strong>for</strong> <strong>the</strong> Young Creek State<br />

L<strong>and</strong>s Stream Restoration Project. Variance estimates <strong>for</strong> annual mean values are presented<br />

in paren<strong>the</strong>ses. Mean values between treatments were compared using a t-test, <strong>and</strong> <strong>the</strong> one<br />

tailed p-value <strong>for</strong> each comparison is presented. The percent change <strong>for</strong> each parameter<br />

between treatments is also presented.................................................................................142<br />

Appendix Tables<br />

Table A1. Therriault Creek depletion population estimates <strong>for</strong> fish > 75 mm per 1,000 feet using<br />

95 % confidence intervals. Upper confidence intervals are in paren<strong>the</strong>sis. .....................149<br />

Table A2. Lower Grave Creek Demonstration Project area electr<strong>of</strong>ishing. Numbers are total<br />

catch within <strong>the</strong> 1,000 foot section. ...................................................................................150<br />

Table A3. Young Creek depletion population estimates <strong>for</strong> fish > 75 mm per 1,000 feet using 95<br />

% confidence intervals. Upper confidence intervals are in paren<strong>the</strong>sis. ..........................151<br />

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