| MONT1
|
|
Table 1. MONT1 ammonium sulfate trajectory
regression attribution
assessment using a zero intercept. |
|
|
|
Intercept |
|
|
|
|
|
|
|
NWUS |
0.1903 |
0.0348 |
32.4 |
5.9 |
32.4 |
0.0000 |
|
Canada |
0.1103 |
0.0152 |
18.8 |
2.6 |
51.2 |
0.0000 |
|
SwMontana |
0.0947 |
0.0248 |
16.1 |
4.2 |
67.3 |
0.0002 |
|
Pacific Ocean |
0.0809 |
0.0312 |
13.8 |
5.3 |
81.1 |
0.0100 |
|
NeMontana |
0.0315 |
0.0118 |
5.4 |
2.0 |
86.4 |
0.0077 |
|
SWUS |
0.0298 |
0.0121 |
5.1 |
2.1 |
91.5 |
0.0145 |
|
SeMontana |
0.0252 |
0.0104 |
4.3 |
1.8 |
95.8 |
0.0161 |
|
NEUS |
0.0147 |
0.0218 |
2.5 |
3.7 |
98.3 |
0.5009 |
|
South Dakota |
0.0066 |
0.0113 |
1.1 |
1.9 |
99.4 |
0.5621 |
|
Mexico |
0.0041 |
0.0039 |
0.7 |
0.7 |
100.1 |
0.2885 |
|
Pacific Coast |
-0.0005 |
0.0294 |
-0.1 |
5.0 |
100.0 |
0.9863 |
|
NorthDakota |
-0.0008 |
0.0039 |
-0.1 |
0.7 |
99.9 |
0.8452 |
|
Wyoming |
-0.0046 |
0.0069 |
-0.8 |
1.2 |
99.1 |
0.5121 |
|
Idaho |
-0.0118 |
0.0234 |
-2.0 |
4.0 |
97.1 |
0.6153 |
|
SEUS |
-0.0140 |
0.0254 |
-2.4 |
4.3 |
94.7 |
0.5814 |
|
NwMontana |
-0.0188 |
0.0172 |
-3.2 |
2.9 |
91.5 |
0.2772 |
|
|
Table 2. MONT1 ammonium sulfate trajectory regression attribution
assessment including an intercept. |
|
| Source Regions |
Contributions (ug/m3) |
Uncertainty (ug/m3) |
Fraction (%) |
Uncertainty (%) |
Cumulative (%) |
Significance (p value) |
|
|
Intercept |
0.5362 |
0.0637 |
91.3 |
10.8 |
91.3 |
0.0000 |
|
NWUS |
0.0684 |
0.0344 |
11.7 |
5.8 |
102.9 |
0.0473 |
|
Canada |
0.0493 |
0.0154 |
8.4 |
2.6 |
111.3 |
0.0015 |
|
SwMontana |
0.0286 |
0.0235 |
4.9 |
4.0 |
116.2 |
0.2259 |
|
Pacific Ocean |
-0.0190 |
0.0303 |
-3.2 |
5.2 |
113.0 |
0.5304 |
|
NeMontana |
0.0229 |
0.0106 |
3.9 |
1.8 |
116.8 |
0.0312 |
|
SWUS |
0.0013 |
0.0113 |
0.2 |
1.9 |
117.1 |
0.9087 |
|
SeMontana |
0.0293 |
0.0093 |
5.0 |
1.6 |
122.1 |
0.0019 |
|
NEUS |
0.0144 |
0.0194 |
2.5 |
3.3 |
124.5 |
0.4584 |
|
South Dakota |
0.0042 |
0.0101 |
0.7 |
1.7 |
125.2 |
0.6814 |
|
Mexico |
0.0050 |
0.0035 |
0.8 |
0.6 |
126.1 |
0.1530 |
|
Pacific Coast |
-0.0250 |
0.0264 |
-4.3 |
4.5 |
121.8 |
0.3442 |
|
NorthDakota |
0.0009 |
0.0035 |
0.1 |
0.6 |
122.0 |
0.8053 |
|
Wyoming |
-0.0043 |
0.0062 |
-0.7 |
1.1 |
121.2 |
0.4864 |
|
Idaho |
-0.0643 |
0.0218 |
-10.9 |
3.7 |
110.3 |
0.0035 |
|
SEUS |
-0.0141 |
0.0227 |
-2.4 |
3.9 |
107.9 |
0.5370 |
|
NwMontana |
-0.0463 |
0.0157 |
-7.9 |
2.7 |
100.0 |
0.0036 |
|
|
Table 3. MONT1 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 |
|
|
|
|
|
|
|
SwMontana |
8.2973 |
3.2676 |
35.0 |
13.8 |
35.0 |
0.0117 |
|
NWUS |
7.9504 |
4.5903 |
33.6 |
19.4 |
68.6 |
0.0844 |
|
Canada |
2.6077 |
1.9959 |
11.0 |
8.4 |
79.6 |
0.1925 |
|
NwMontana |
1.2881 |
2.2696 |
5.4 |
9.6 |
85.1 |
0.5708 |
|
Pacific Coast |
1.1990 |
3.8690 |
5.1 |
16.3 |
90.2 |
0.7569 |
|
Pacific Ocean |
0.8910 |
4.1086 |
3.8 |
17.4 |
93.9 |
0.8285 |
|
NeMontana |
0.7839 |
1.5481 |
3.3 |
6.5 |
97.2 |
0.6130 |
|
SEUS |
0.5933 |
3.3514 |
2.5 |
14.2 |
99.7 |
0.8596 |
|
SWUS |
0.1585 |
1.5961 |
0.7 |
6.7 |
100.4 |
0.9210 |
|
Wyoming |
0.1057 |
0.9137 |
0.4 |
3.9 |
100.9 |
0.9080 |
|
Mexico |
0.0435 |
0.5117 |
0.2 |
2.2 |
101.0 |
0.9322 |
|
NorthDakota |
-0.0511 |
0.5162 |
-0.2 |
2.2 |
100.8 |
0.9212 |
|
South Dakota |
-0.1094 |
1.4941 |
-0.5 |
6.3 |
100.4 |
0.9417 |
|
SeMontana |
-0.2344 |
1.3728 |
-1.0 |
5.8 |
99.4 |
0.8645 |
|
NEUS |
-0.5555 |
2.8652 |
-2.3 |
12.1 |
97.0 |
0.8464 |
|
Idaho |
-2.5775 |
3.0848 |
-10.9 |
13.0 |
86.1 |
0.4041 |
|
|
Table 4. MONT1 aerosol extinction trajectory regression attribution
assessment including an intercept. |
|
| Source Regions |
Contributions (1/Mm) |
Uncertainty (1/Mm) |
Fraction (%) |
Uncertainty (%) |
Cumulative (%) |
Significance (p value) |
|
