For CN55 fuels, the NOx emission showed strong dependence on the location of MFB50% regardless of fuel types, i.e. NOx decreases as the MFB50% location retards.
With increasing temperatures, NOx decreases by about 20% and CO decreases by nearly a factor of two [ 17].
Here, we report that the increase in the hydrophobicity of the middle block B, from barely hydrophobic BuOx to highly hydrophobic NOx, decreases the solubilization capacity for PTX by more than half.
When area-level confounding was taken into account, the effect estimate for NOx decreased and was no longer statistically significant (2.5%; 95% CI: –0.6, 5.6) (Table 3, Area-level model).
These negative influences coincided with NOx-inhibited atmospheric conditions where O3 production increases as NOx availability decreases; thus reducing NOx emissions-increased O3-related mortality.
While consuming a restricted diet for 3 days to eliminate the effects of oral intake of NOx, 24 hour urinary NOx excretion decreased in both RA patients and healthy controls.
When the hydrocarbon contribution to the NOx reduction reaction was large, NOx emission decreased with increasing burning temperature; however, hydrocarbon content in volatile matter was small for low-rank coals.
Only in Group A did NOx levels decrease significantly from day 3. NOx levels in the plasma did not change significantly.
We considered that NOx in the CSF has a role as an inhibitor for cerebral vasospasm following SAH, because NOx levels decreased significantly only in the vasospasm group, while plasma NOx levels did not change significantly.
Serum NOx levels decreased to an even greater degree with dietary NOx restriction (as much as 42% decrease) and stabilized over 72 hours.
