NO
3
•
can compete with omnipotent
•
OH/SO
4
•–
in decomposing
aqueous pollutants because of its lengthy lifespan and significant
tolerance to background scavengers present in H
2
O matrices,
albeit with moderate oxidizing power. The generation of NO
3
•
, however, is of grand demand due to the need
of NO
2
•
/O
3
, radioactive element,
or NaNO
3
/HNO
3
in the presence of highly energized
electron/light. This study has pioneered a singular pathway used to
radicalize surface NO
3
–
functionalities
anchored on polymorphic α-/γ-MnO
2
surfaces
(α-/γ-MnO
2
-N), in which Lewis acidic Mn
2+/3+
and NO
3
–
served to form
•
OH via H
2
O
2
dissection and NO
3
•
via radical transfer from
•
OH to NO
3
–
(
•
OH →
NO
3
•
), respectively. The elementary steps
proposed for the
•
OH → NO
3
•
route could be energetically favorable and marginal
except for two stages such as endothermic
•
OH desorption
and exothermic
•
OH-mediated NO
3
–
radicalization, as verified by EPR spectroscopy experiments and
DFT calculations. The Lewis acidic strength of the Mn
2+/3+
species innate to α-MnO
2
-N was the smallest among
those inherent to α-/β-/γ-MnO
2
and α-/γ-MnO
2
-N. Hence, α-MnO
2
-N prompted the rate-determining
stage of the
•
OH → NO
3
•
route (
•
OH desorption) in the most efficient manner,
as also evidenced by the analysis on the energy barrier required to
proceed with the
•
OH → NO
3
•
route. Meanwhile, XANES and
in situ
DRIFT spectroscopy experiments corroborated that α-MnO
2
-N provided a larger concentration of surface NO
3
–
species with
bi
-dentate binding
arrays than γ-MnO
2
-N. Hence, α-MnO
2
-N could outperform γ-MnO
2
-N in improving the collision
frequency between
•
OH and NO
3
–
species and in facilitating the exothermic transition of NO
3
–
functiona...