|
Lostwood Wilderness Area
|
|
Table 1. LOST1 ammonium sulfate trajectory
regression attribution
assessment using a zero intercept. |
|
|
| Intercept |
|
|
|
|
|
|
| Canada |
0.7838 |
0.0680 |
49.7 |
4.3 |
49.7 |
0.0000 |
| SwNorth Dakota |
0.2180 |
0.0472 |
13.8 |
3.0 |
63.5 |
0.0000 |
| SeNorth Dakota |
0.1381 |
0.0514 |
8.8 |
3.3 |
72.3 |
0.0076 |
| Montana |
0.1079 |
0.0536 |
6.8 |
3.4 |
79.1 |
0.0449 |
| NWUS |
0.0689 |
0.0494 |
4.4 |
3.1 |
83.5 |
0.1639 |
| SEUS |
0.0611 |
0.0134 |
3.9 |
0.9 |
87.4 |
0.0000 |
| nwNorth Dakota |
0.0557 |
0.0416 |
3.5 |
2.6 |
90.9 |
0.1813 |
| South Dakota |
0.0489 |
0.0360 |
3.1 |
2.3 |
94.0 |
0.1758 |
| SWUS |
0.0422 |
0.0268 |
2.7 |
1.7 |
96.7 |
0.1159 |
| Minnesota |
0.0314 |
0.0213 |
2.0 |
1.3 |
98.7 |
0.1406 |
| Gulf |
0.0071 |
0.0128 |
0.5 |
0.8 |
99.2 |
0.5786 |
| Pacific Ocean |
0.0006 |
0.0441 |
0.0 |
2.8 |
99.2 |
0.9887 |
| Atlantic |
-0.0101 |
0.0064 |
-0.6 |
0.4 |
98.6 |
0.1142 |
| Mexico |
-0.0131 |
0.0119 |
-0.8 |
0.8 |
97.7 |
0.2705 |
| Pacific Coast |
-0.0294 |
0.0492 |
-1.9 |
3.1 |
95.9 |
0.5507 |
| NEUS |
-0.0307 |
0.0275 |
-1.9 |
1.7 |
93.9 |
0.2660 |
| NeNorth Dakota |
-0.0916 |
0.0320 |
-5.8 |
2.0 |
88.1 |
0.0045 |
|
|
Table 2. LOST1 ammonium sulfate trajectory regression attribution
assessment including an intercept. |
|
| Source Regions |
Contributions (ug/m3) |
Uncertainty (ug/m3) |
Fraction (%) |
Uncertainty (%) |
Cumulative (%) |
Significance (p value) |
|
| Intercept |
1.1050 |
0.1117 |
70.1 |
7.1 |
70.1 |
0.0000 |
| Canada |
0.2273 |
0.0817 |
14.4 |
5.2 |
84.5 |
0.0057 |
| SwNorth Dakota |
0.1759 |
0.0413 |
11.2 |
2.6 |
95.7 |
0.0000 |
| SeNorth Dakota |
0.0999 |
0.0449 |
6.3 |
2.8 |
102.0 |
0.0269 |
| Montana |
0.0813 |
0.0468 |
5.2 |
3.0 |
107.2 |
0.0829 |
| NWUS |
-0.0161 |
0.0439 |
-1.0 |
2.8 |
106.1 |
0.7147 |
| SEUS |
0.0463 |
0.0118 |
2.9 |
0.7 |
109.1 |
0.0001 |
| nwNorth Dakota |
-0.0229 |
0.0371 |
-1.5 |
2.4 |
107.6 |
0.5376 |
| South Dakota |
0.0184 |
0.0316 |
1.2 |
2.0 |
108.8 |
0.5605 |
| SWUS |
0.0155 |
0.0235 |
1.0 |
1.5 |
109.8 |
0.5107 |
| Minnesota |
0.0382 |
0.0185 |
2.4 |
1.2 |
112.2 |
0.0403 |
| Gulf |
0.0070 |
0.0112 |
0.4 |
0.7 |
112.6 |
0.5313 |
| Pacific Ocean |
-0.0542 |
0.0388 |
-3.4 |
2.5 |
109.2 |
0.1639 |
| Atlantic |
-0.0076 |
0.0056 |
-0.5 |
0.4 |
108.7 |
0.1709 |
| Mexico |
-0.0107 |
0.0104 |
-0.7 |
0.7 |
108.0 |
0.3026 |
| Pacific Coast |
-0.0357 |
0.0429 |
-2.3 |
2.7 |
105.8 |
0.4060 |
| NEUS |
-0.0213 |
0.0240 |
-1.3 |
1.5 |
104.4 |
0.3762 |
| NeNorth Dakota |
-0.0698 |
0.0279 |
-4.4 |
1.8 |
100.0 |
0.0130 |
|
|
Table 3. LOST1 aerosol extinction trajectory regression attribution
assessment using a zero intercept. |
|
| Source Regions |
Contributions (1/Mm) |
Uncertainty (1/Mm) |
Fraction (%) |
Uncertainty (%) |
Cumulative (%) |
Significance (p value) |
| Intercept |
|
|
|
|
|
|
| Canada |
16.5169 |
1.4535 |
50.3 |
4.4 |
50.3 |
0.0000 |
| NWUS |
3.0418 |
1.0559 |
9.3 |
3.2 |
59.6 |
0.0042 |
| SwNorth Dakota |
2.9172 |
1.0093 |
8.9 |
3.1 |
68.5 |
0.0041 |
| South Dakota |
2.2269 |
0.7708 |
6.8 |
2.3 |
75.3 |
0.0041 |
| Montana |
2.0911 |
1.1457 |
6.4 |
3.5 |
81.6 |
0.0690 |
| nwNorth Dakota |
1.6800 |
0.8895 |
5.1 |
2.7 |
86.7 |
0.0599 |
| SWUS |
1.3955 |
0.5726 |
4.3 |
1.7 |
91.0 |
0.0154 |
| SeNorth Dakota |
1.2639 |
1.0985 |
3.9 |
3.3 |
94.8 |
0.2508 |
| SEUS |
0.9702 |
0.2875 |
3.0 |
0.9 |
97.8 |
0.0008 |
| Pacific Coast |
0.4427 |
1.0517 |
1.3 |
3.2 |
99.1 |
0.6741 |
| Minnesota |
0.2626 |
0.4550 |
0.8 |
1.4 |
99.9 |
0.5642 |
| Gulf |
-0.0575 |
0.2741 |
-0.2 |
0.8 |
99.8 |
0.8341 |
| Mexico |
-0.1337 |
0.2543 |
-0.4 |
0.8 |
99.4 |
0.5995 |
| Atlantic |
-0.1484 |
0.1361 |
-0.5 |
0.4 |
98.9 |
0.2764 |
| Pacific Ocean |
-0.3697 |
0.9433 |
-1.1 |
2.9 |
97.8 |
0.6954 |
| NEUS |
-1.3962 |
0.5890 |
-4.3 |
1.8 |
93.5 |
0.0184 |
| NeNorth Dakota |
-1.4892 |
0.6838 |
-4.5 |
2.1 |
89.0 |
0.0302 |
|
|
Table 4. LOST1 aerosol extinction trajectory regression attribution
assessment including an intercept. |
|
| Source Regions |
Contributions (1/Mm) |
Uncertainty (1/Mm) |
Fraction (%) |
Uncertainty (%) |
Cumulative (%) |
Significance (p value) |
|
