(1) NOx emissions (P)
|
0 |
4 |
The surface NOx emissions field as a function of latitude and longitude was multiplied by a scaling factor between 0 and 4, to explore the sensitivity of tropospheric ozone to a range of NOx emissions. |
(2) CH4 concentrations (P)
|
0 |
4 |
The global-mean CH4 mixing ratio was multiplied by a scaling factor between 0 and 4, to explore the sensitivity of tropospheric ozone to a range of CH4 concentrations. |
(3) CO+NMVOC (P) emissions |
0 |
4 |
As for (1), but the scaling factor was applied to CO and NMVOC emissions simultaneously. |
(4) ELEV for NOx and CO+NMVOCs (P)
|
1 |
6 |
Emissions were prescribed on the lowermost 1–6 levels (between the surface and ~2.5 km), to test whether the number of levels is important for tropospheric ozone abundances. |
(5) CLEV for CH4
(P)
|
1 |
6 |
CH4 concentrations were prescribed on the lowermost 1–6 levels (between the surface and ~2.5 km), similar to (4). |
(6) CMF (P+L)
|
0.25 |
1 |
1 implies clear-sky photolysis, whereas 0 would imply no photolysis. As photolysis rates of 0 do not occur during daytime, we selected a lower bound of 0.25 to represent cloudy sky conditions. |
(7) HNO3 washout (L)
|
0 |
0.5 |
To test the sensitivity of tropospheric ozone to HNO3 removal, we removed between 0–50% of tropospheric gas-phase HNO3 at each chemical time step. |
(8) N2O5 hydrolysis (L)
|
0.001 |
0.3 |
The probability of N2O5 hydrolysis occurring. Since the default is 0.1, we explored the sensitivity of tropospheric ozone to a range from 0.001–0.3. |
(9) O3 dry deposition (L)
|
0 |
1 |
A specific reactivity of 0 stands for a nearly non-reactive gas, while 1 stands for a gas similarly reactive to ozone. |