Scientific Investigations Report 2006–5106
U.S. GEOLOGICAL SURVEY
Scientific Investigations Report 2006–5106
Table 12. Monthly dissolved inorganic nitrogen load from the 26 river and 24 shoreline basins, and total annual dissolved inorganic nitrogen loads from streams and ground water, Hood Canal drainage basin, western Washington., 1971-2002.
[Locations of subbasins are shown in figure 2. Hydroclimatic region: Monthly distribution over the annual cycle: 1, lowland streams; 2, North Olympic rivers; 3, Skokomish. Empirical regression parameters from equation 4. Abbreviations: N, nitrogen; DIN, dissolved inorganic nitrogen; m3/s, cubic meter per second; kg, kilogram; MT/yr, metric ton per year]
River and shoreline subbasins | Mean streamflow for entire basin for 1971-2002 (m3/s) | Hydro-climatic region | Empirical regression parameters | Dissolved inorganic nitrogen load (kg) | DIN load (MT/yr) | |||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
m | B | Oct. | Nov. | Dec. | Jan. | Feb. | Mar. | Apr. | May | June | July | Aug. | Sept. | Stream | Ground water |
|||||
Skokomish River | ||||||||||||||||||||
Skokomish1 | 36.13 | 3 | 0.11 | 0.16 | 8,790 | 15,700 | 23,200 | 18,800 | 15,100 | 12,100 | 10,100 | 7,740 | 6,280 | 4,660 | 4,110 | 4,900 | 131.4 | 0.0 | ||
Other Olympic Rivers | ||||||||||||||||||||
Duckabush | 13.69 | 2 | 0.05 | 0.11 | 1,000 | 2,040 | 2,350 | 2,040 | 1,950 | 1,960 | 1,860 | 2,600 | 2,420 | 1,520 | 631 | 389 | 20.8 | 0.0 | ||
Dosewallips | 17.49 | 2 | .08 | .62 | 1,750 | 5,010 | 6,100 | 4,940 | 4,850 | 4,660 | 4,410 | 7,060 | 6,450 | 3,220 | 889 | 445 | 49.8 | .0 | ||
Hamma Hamma | 16.36 | 2 | .10 | .23 | 2,360 | 5,210 | 6,090 | 5,190 | 4,990 | 4,960 | 4,720 | 6,810 | 6,310 | 3,750 | 1,410 | 826 | 52.6 | .0 | ||
Little Quilcene | 2.23 | 1 | .11 | .16 | 259 | 869 | 1,520 | 1,690 | 1,530 | 993 | 568 | 345 | 217 | 155 | 118 | 114 | 8.4 | .5 | ||
Big Quilcene | 5.29 | 2 | .10 | .16 | 772 | 1,630 | 1,890 | 1,630 | 1,560 | 1,560 | 1,484 | 2,100 | 1,950 | 1,190 | 474 | 286 | 16.5 | 19.5 | ||
North Olympic lowlands | ||||||||||||||||||||
Thorndyke | 0.69 | 1 | 0.11 | 0.16 | 79.7 | 268 | 467 | 520 | 471 | 306 | 175 | 106 | 66.8 | 47.7 | 36.3 | 35.1 | 2.6 | 0.0 | ||
Tarboo | .64 | 1 | .11 | .16 | 74.6 | 251 | 437 | 487 | 441 | 287 | 164 | 99.5 | 62.6 | 44.7 | 34.0 | 32.9 | 2.4 | .0 | ||
Spencer | .15 | 1 | .11 | .16 | 17.9 | 60.0 | 105 | 117 | 106 | 68.6 | 39.3 | 23.8 | 15.0 | 10.7 | 8.1 | 7.9 | .6 | 2.5 | ||
Shore 1 | .45 | 1 | .11 | .16 | 52.8 | 177 | 310 | 344 | 312 | 203 | 116 | 70.4 | 44.3 | 31.6 | 24.1 | 23.2 | 1.7 | 8.1 | ||
Shore 19 | .07 | 1 | .11 | .16 | 7.8 | 26.3 | 45.8 | 51.0 | 46.2 | 30.0 | 17.2 | 10.4 | 6.6 | 4.7 | 3.6 | 3.4 | .3 | 3.1 | ||
Shore 20 | .12 | 1 | .11 | .16 | 13.7 | 46.0 | 80.3 | 89.4 | 81.0 | 52.6 | 30.1 | 18.3 | 11.5 | 8.2 | 6.2 | 6.0 | .4 | 5.5 | ||
Shore 21 | .24 | 1 | .11 | .16 | 27.7 | 93.0 | 162 | 181 | 164 | 106 | 60.8 | 36.9 | 23.2 | 16.6 | 12.6 | 12.2 | .9 | 6.7 | ||
Shore 22 | .44 | 1 | .11 | .16 | 51.7 | 174 | 303 | 337 | 305 | 198 | 114 | 68.9 | 43.3 | 30.9 | 23.5 | 22.8 | 1.7 | 8.1 | ||
Shore 23 | .26 | 1 | .11 | .16 | 30.6 | 103 | 179 | 200 | 181 | 118 | 67.2 | 40.8 | 25.7 | 18.3 | 13.9 | 13.5 | 1.0 | 1.2 | ||
Jackson | .01 | 1 | .11 | .16 | 11.1 | 37.3 | 65.2 | 72.6 | 65.7 | 42.7 | 24.4 | 14.8 | 9.3 | 6.7 | 5.1 | 4.9 | .4 | 2.1 | ||
South Olympic, South-Shore, Kitsap lowlands | ||||||||||||||||||||
Union | 1.89 | 1 | 0.38 | 0.25 | 693 | 2,560 | 4,640 | 5,210 | 4,720 | 2,940 | 1,620 | 944 | 575 | 399 | 298 | 287 | 24.9 | 5.7 | ||
Mission | .98 | 1 | .11 | .16 | 113 | 380 | 663 | 738 | 66 | 434 | 249 | 151 | 94.9 | 67.7 | 51.6 | 49.8 | 3.7 | 3.7 | ||
Tahuya | 4.01 | 1 | .14 | .16 | 562 | 1,880 | 3,270 | 3,640 | 3,300 | 2,150 | 1,230 | 748 | 471 | 337 | 257 | 248 | 18.1 | 5.9 | ||
Dewatto | 2.38 | 1 | .13 | .16 | 319 | 1,070 | 1,860 | 2,070 | 1,870 | 1,220 | 698 | 424 | 268 | 191 | 146 | 141 | 10.3 | .0 | ||
Big Beef | 1.12 | 1 | .11 | .16 | 130 | 435 | 759 | 844 | 765 | 497 | 284 | 173 | 109 | 77.5 | 59.0 | 57.0 | 4.2 | .0 | ||
Anderson 1 | .45 | 1 | .11 | .16 | 52.3 | 176 | 306 | 341 | 309 | 201 | 115 | 69.7 | 43.9 | 31.3 | 23.8 | 23.0 | 1.7 | .0 | ||
Anderson 2 | .59 | 1 | .11 | .16 | 69.0 | 232 | 404 | 450 | 408 | 265 | 152 | 92.0 | 57.9 | 41.3 | 31.4 | 30.4 | 2.2 | .0 | ||
Eagle | .77 | 1 | .11 | .16 | 89.8 | 302 | 526 | 586 | 531 | 345 | 197 | 120 | 75.3 | 53.7 | 40.9 | 39.5 | 2.9 | 2.6 | ||
Finch | .31 | 1 | .14 | .20 | 41.3 | 144 | 256 | 286 | 259 | 165 | 93 | 55.5 | 34.5 | 24.3 | 18.3 | 17.7 | 1.4 | 2.2 | ||
Fulton | .87 | 1 | .11 | .16 | 101 | 340 | 594 | 661 | 599 | 389 | 222 | 135 | 85.0 | 60.6 | 46.2 | 44.6 | 3.3 | 1.2 | ||
Jorsted | .45 | 1 | .11 | .16 | 51.9 | 174 | 304 | 339 | 307 | 199 | 114 | 69.2 | 43.6 | 31.1 | 23.7 | 22.9 | 1.7 | 2.1 | ||
Lilliwaup | 1.74 | 1 | .11 | .16 | 201 | 677 | 1,180 | 1,320 | 1,190 | 774 | 443 | 269 | 169 | 121 | 91.9 | 88.8 | 6.5 | 9.5 | ||
Rendsland | 0.90 | 1 | 0.11 | 0.16 | 105 | 351 | 613 | 682 | 618 | 402 | 230 | 139 | 87.7 | 62.6 | 47.7 | 46.1 | 3.4 | 0.0 | ||
Seabeck | .53 | 1 | .11 | .16 | 61.6 | 207 | 361 | 402 | 364 | 236 | 135 | 82.1 | 51.7 | 36.9 | 28.1 | 27.1 | 2.0 | .0 | ||
Stavis | .99 | 1 | .11 | .16 | 114 | 385 | 671 | 747 | 676 | 440 | 252 | 153 | 96.0 | 68.5 | 52.2 | 50.4 | 3.7 | .0 | ||
Waketickeh | .76 | 1 | .11 | .16 | 88.7 | 298 | 520 | 579 | 524 | 341 | 195 | 118 | 74.4 | 53.1 | 40.4 | 39.1 | 2.9 | 2.0 | ||
Shore 2 | .15 | 1 | .11 | .16 | 17.1 | 57.4 | 100 | 112 | 101 | 65.6 | 37.6 | 22.8 | 14.3 | 10.2 | 7.8 | 7.5 | .6 | .3 | ||
Shore 3 | .41 | 1 | .11 | .16 | 47.2 | 158 | 276 | 308 | 279 | 181 | 104 | 62.9 | 39.6 | 28.2 | 21.5 | 20.8 | 1.5 | .6 | ||
Shore 4 | .31 | 1 | .11 | .16 | 35.8 | 120 | 210 | 234 | 212 | 138 | 78.6 | 47.7 | 30.0 | 21.4 | 16.3 | 15.8 | 1.2 | .7 | ||
Shore 5 | .22 | 1 | .11 | .16 | 25.7 | 86.4 | 151 | 168 | 152 | 98.7 | 56.5 | 34.3 | 21.6 | 15.4 | 11.7 | 11.3 | .8 | 1.7 | ||
Shore 6 | .23 | 1 | .11 | .16 | 27.1 | 91.1 | 159 | 177 | 160 | 104 | 59.6 | 36.2 | 22.8 | 16.2 | 12.4 | 11.9 | .9 | 2.4 | ||
Shore 7 | .67 | 1 | .11 | .16 | 77.8 | 261 | 456 | 508 | 460 | 299 | 171 | 104 | 65.2 | 46.5 | 35.4 | 34.2 | 2.5 | 5.4 | ||
Shore 8 | .06 | 1 | .11 | .16 | 6.7 | 22.4 | 39.0 | 43.5 | 39.4 | 25.6 | 14.6 | 8.9 | 5.6 | 4.0 | 3.0 | 2.9 | .2 | .4 | ||
Shore 9 | 1.26 | 1 | .11 | .16 | 146.1 | 490 | 856 | 953 | 863 | 561 | 321 | 195 | 122 | 87.4 | 66.6 | 64.3 | 4.7 | 10.4 | ||
Shore 10 | 223.8 | 1 | .11 | .16 | 2,770 | 9,290 | 16,200 | 18,000 | 16,300 | 10,600 | 6,080 | 3,690 | 2,320 | 1,660 | 1,260 | 1,220 | 389.5 | 9.6 | ||
Shore 11 | .52 | 1 | .11 | .16 | 60.2 | 202 | 353 | 393 | 356 | 231 | 132 | 80.3 | 50.5 | 36.0 | 27.4 | 26.5 | 1.9 | 7.9 | ||
Shore 12 | .07 | 1 | .11 | .16 | 8.6 | 28.8 | 50.3 | 56.0 | 50.7 | 32.9 | 18.8 | 11.4 | 7.2 | 5.1 | 3.9 | 3.8 | .3 | .8 | ||
Shore 13 | .11 | 1 | .11 | .16 | 12.8 | 42.9 | 74.8 | 83.3 | 75.4 | 49.0 | 28.0 | 17.0 | 10.7 | 7.6 | 5.8 | 5.6 | .4 | .8 | ||
Shore 14 | .04 | 1 | .11 | .16 | 4.7 | 15.7 | 27.3 | 30.4 | 27.6 | 17.9 | 10.2 | 6.2 | 3.9 | 2.8 | 2.1 | 2.1 | .2 | .3 | ||
Shore 15 | .02 | 1 | .11 | .16 | 2.7 | 9.1 | 15.8 | 17.6 | 16.0 | 10.4 | 5.9 | 3.6 | 2.3 | 1.6 | 1.2 | 1.2 | .1 | .2 | ||
Shore 16 | .45 | 1 | .11 | .16 | 52.9 | 178 | 310 | 345 | 312 | 203 | 116 | 70.5 | 44.4 | 31.7 | 24.1 | 23.3 | 1.7 | 3.7 | ||
Shore 17 | .18 | 1 | .11 | .16 | 21.4 | 71.9 | 125 | 140 | 126 | 82.2 | 47.0 | 28.5 | 18.0 | 12.8 | 9.8 | 9.4 | .7 | 1.0 | ||
Shore 18 | .29 | 1 | .11 | .16 | 33.3 | 112 | 195 | 218 | 197 | 128 | 73.2 | 44.4 | 28.0 | 19.9 | 15.2 | 14.7 | 1.1 | .2 | ||
Shore 24 | .06 | 1 | .11 | .16 | 6.9 | 23.3 | 40.6 | 45.3 | 41.0 | 26.6 | 15.2 | 9.2 | 5.8 | 4.2 | 3.2 | 3.1 | .2 | .0 | ||
Total | 142 | 493 | 138 |
1Streamflow was scaled for the 1971-2002 as described in “Estimates of Streamflow” in section “Annual Freshwater and Saline Loads in Dissolved Inorganic Nitrogen to Hood Canal, 1971-2002.”
2 Streamflow includes 0.636 m3/s from shore 10 and 23.2 m3/s from Lake Cushman Diversion.
3Stream nitrogen loadings includes 0.5 MT/yr from shore 10 plus 89.0 MT/yr from Lake Cushman Diversion.
4Total is slightly different than the sum due to rounding.
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