Scientific Investigations Report 2006-5188

U.S. GEOLOGICAL SURVEY
Scientific Investigations Report 2006-5188

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Table 2. Regression coefficients and coefficients of determination (R2) used to estimate dissolved and total cadmium, lead, and zinc loads at 10 streamflow-gaging stations in the Spokane River basin, Idaho and Washington, water years 1999–2004.

[Gaging station locations are shown in figures 1 and 2. Regression equation is ln(L) = a + b(ln Q) + c(ln Q2) + d[sin(2•T)] + e[cos(2•T)] + fT + gT2, where L is constituent load; Q is streamflow; T is time in decimal years from beginning of calibration period; a, b, c, d, e, f, and g are regression coefficients. Symbols: –, explanatory variable not used in regression; <, less than]

Gaging station No. Gaging station name Regression coefficient R2 (percent)
a b c d e f p-value
of f
g p-value
of g
Dissolved cadmium (DCd)
1 Canyon Creek 0.6008 0.6817 -0.0712 -0.1205 0.3826 -0.0688 0.028 87.1
2 Ninemile Creek -.5595 .7737 -.1230 .2380 -.0759 .009 92.6
3 Elizabeth Park 1.0269 .5743 -.0637 .0154 .0336 -.0569 <.001 0.0236 0.0080 96.8
4 Amy Gulch -2.3365 .9049 .0337 .1811 98.3
5 Pinehurst 1.9199 .5719 -.0785 .0344 -.2288 -.0655 <.001 94.2
6 Enaville -2.3963 1.0208 93.8
7 Harrison 1.8232 .8408 -.1047 -.2305 -.0058 -.0649 .031 .0496 .0308 96.3
8 Outlet .2334 1.1621 -.1219 .136 98.3
9 Post Falls .5099 1.1001 -.0375 .1454 .2112 97.9
10 Long Lake .1045 1.6900 .4741 .6026 -.2017 .023 84.5
Total cadmium (TCd)
1 Canyon Creek 0.5374 0.7350 -0.1634 0.3522 -0.0707 0.045 86.9
2 Ninemile Creek -.4732 .8761 -.2349 .1934 -.0521 .107 92.6
3 Elizabeth Park 1.0808 .7157 -.0380 .0015 .1456 -.0627 .0018 0.0240 0.0410 95.5
4 Amy Gulch -2.3283 1.0044 .0138 -.0965 .1151 .1977 <.001 -.1089 .002 97.6
5 Pinehurst 1.9876 .8189 .2659 -.1850 74.3
6 Enaville -2.7061 1.2194 .1678 95.4
7 Harrison 2.0707 1.0881 -.3835 .0169 91.8
8 Outlet .0350 1.1977 -.1230 .040 99.2
9 Post Falls .7253 1.1318 .1774 .1474 -.0542 .052 97.7
10 Long Lake .2041 1.0004 .1834 .9167 -.0511 .131 95.6
Dissolved lead (DPb)
1 Canyon Creek 0.9883 0.9365 -0.1679 <0.001 96.3
2 Ninemile Creek .0933 .9595 -0.095 -.1014 <.001 97.8
3 Elizabeth Park .5524 .6525 -0.0734 -0.3841 -.0925 95.9
4 Amy Gulch -2.3582 1.2459 .0747 95.5
5 Pinehurst 1.4363 .7143 .0519 -.2162 .2869 -.0999 <.001 93.7
6 Enaville -1.3537 1.1351 .1263 86.3
7 Harrison 3.2026 1.2784 88.0
8 Outlet .1119 1.1162 -.4152 -.2898 -.4273 .060 92.0
9 Post Falls .5045 1.3779 .1794 .2774 .009 84.7
10 Long Lake .9372 2.2135 -.1964 .054 75.7
Total lead (TPb)
1 Canyon Creek 1.6834 1.567 0.3162 -0.2964 <0.001 93.2
2 Ninemile Creek .7112 1.5924 .2343 -.1343 .001 96.8
3 Elizabeth Park 1.6364 1.7137 .3457 88.7
4 Amy Gulch -2.3381 1.8454 .4037 93.6
5 Pinehurst 3.1628 1.8606 .4051 0.5561 -0.0612 -.1068 .0317 90.0
6 Enaville -.4893 1.9066 .3115 91.7
7 Harrison 4.4844 1.5341 .3381 91.6
8 Outlet 1.9154 1.1945 89.5
9 Post Falls 2.2820 1.4423 .1874 .2101 -.4583 95.1
10 Long Lake 2.4961 2.2704 92.7
Dissolved zinc (DZn)
1 Canyon Creek 5.7756 0.7615 -0.1145 -0.0403 0.5307 -0.0364 0.264 -0.057 0.069 86.3
2 Ninemile Creek 4.5379 .82 -.2289 .3347 -.0859 .021 88.9
3 Elizabeth Park 6.0871 .6176 -.0896 .0677 .0472 -.0595 <.001 .0227 .0230 96.5
4 Amy Gulch 3.3121 .868 -.0204 .3607 97.2
5 Pinehurst 6.8909 .5413 -.0431 .0484 -.1875 -.0652 <.001 94.8
6 Enaville 2.9204 1.2150 -.0919 93.6
7 Harrison 7.0699 .7142 -.0750 -.1846 .1819 -.0644 .004 97.0
8 Outlet 5.6784 1.0963 .2530 -.1315 99.5
9 Post Falls 6.2192 1.0794 .0487 .3295 -.0544 <.001 99.5
10 Long Lake 5.7269 1.1329 -.007 .9901 -.076 .010 97.3
Total zinc (TZn)
1 Canyon Creek 5.4991 0.7975 -0.2311 0.4613 86.3
2 Ninemile Creek 4.5792 .9167 -.3632 .2502 -0.0663 0.098 89.7
3 Elizabeth Park 6.0733 .7258 -.0409 .0644 .1397 -.0523 .00918 0.0202 0.0901 95.6
4 Amy Gulch 3.4019 .961 -.1631 .2743 96.5
5 Pinehurst 6.8546 .6726 .0597 .1023 -.2355 -.0505 .078 80.7
6 Enaville 2.9576 1.4643 93.5
7 Harrison 7.0231 .9963 .0466 -.4025 .0801 93.1
8 Outlet 5.7451 1.0763 .1994 -.1721 -.1200 .013 99.6
9 Post Falls 6.2629 1.1028 .0365 .2954 -.0232 .102 99.1
10 Long Lake 6.2721 1.4376 -.2892 -.0054 .8105 -.0724 .028 -.073 .012 97.7

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