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Leighton cycle and chemical system equations

Kinetic derivation · steady state · photochemical anticorrelation

1. Basic chemical system (NO–NO2–O3)

The so-called Leighton cycle is the dynamic closure between three species (NO, NO2 and O3), involved in the three fundamental reactions of the tropospheric photo-oxidative cycle:

(R1) — nitrogen dioxide photolysis
  • hν: UV radiation
  • O(3P): ground-state atomic oxygen
(R2) — ozone formation
  • M: third body (air, N2, O2), stabilises the reaction energy
(R3) — ozone titration
Leighton Cycle
Fig. 1 — The three fundamental reactions of the photo-oxidative cycle

2. Complete kinetic equations

Definitions:

  • \(\ce{NO}\), \(\ce{NO2}\), \(\ce{O3}\)
  • J: photolysis coefficient of \(\ce{NO2}\) (s-1)
  • k3: rate constant of the \(\ce{NO}\)+\(\ce{O3}\) reaction
  • loss: photolysis
  • production: NO oxidation
  • production from photolysis
  • loss via reaction with ozone

3. Elimination of O(³P)

Applying the steady-state approximation to atomic oxygen:

The ozone production rate therefore becomes:

4. Final equation for O3

5. Steady state

At photochemical equilibrium, production equals destruction:

6. Leighton relationship

7. Physical meaning

The ratio \([\ce{NO2}]/[\ce{NO}]\) depends on:

  • solar radiation intensity \((J)\)
  • available ozone concentration
  • kinetic constant \(k_3\) of the titration reaction

As a direct consequence, if \(\ce{O3}\) increases:

  • the conversion \( \ce{NO -> NO2} \) increases
  • therefore \( [\ce{NO2}]/[\ce{NO}] \) increases

8. Origin of the NO2/O3 anticorrelation

NO emission (e.g. traffic, volcanism)

  • \([\ce{NO}]\uparrow\) → \([\ce{O3}]\downarrow\) by titration (R3)
  • \([\ce{NO2}]\uparrow\) as product of (R3)

Strong solar irradiance

  • \(J\uparrow\) → \([\ce{NO2}]\downarrow\) by photolysis (R1)
  • \([\ce{O3}]\uparrow\) through production via (R2)
The \(\ce{NO2}\)/\(\ce{O3}\) anticorrelation is therefore a direct consequence of photo-stationary cycle conservation, not a statistical coincidence.
NO₂/O₃ anticorrelation
Fig. 2 — NO2/O3 anticorrelation

9. Nocturnal regime

At night \(J = 0\): photolysis stops and the system is governed by (R3) alone:

The inverse proportionality follows directly:

Day and night regime
Fig. 3 — Daytime and nocturnal regime

10. When the Leighton cycle is not sufficient

Volatile Organic Compounds (VOCs)

Peroxy radicals \(\ce{RO2}\) convert \(\ce{NO}\) to \(\ce{NO2}\) without consuming ozone:

This produces \(\ce{O3}\) in excess of the Leighton prediction (breaking the anticorrelation).

Other perturbing factors

  • \(\ce{HO_x}\) radicals (\(\ce{OH}\), \(\ce{HO2}\), radical chains): introduce strong non-linearities
  • Long-range atmospheric transport (non-local \(\ce{O3}\), local \(\ce{NO2}\)): decouples the variables
  • Volcanic emissions (\(\ce{SO2}\), secondary oxidations, aerosol formation): alters ozone chemistry

11. Complete system

Including the additional terms due to VOCs:

\(P_{\text{background}}\) represents background ozone production (tropospheric transport, stratosphere); \(L_{\text{chem}}\) denotes the loss terms: reaction with \(\ce{OH}\) (chemical) and dry deposition (physical removal at the surface, not a reaction).

12. Conclusions

The Leighton cycle provides a fundamental framework for understanding ozone chemistry under steady-state conditions, but is only a starting point for describing the complexity of real atmospheric chemistry, which includes numerous additional species and processes.

References

  • Leighton, P. A. (1961). Photochemistry of Air Pollution (Vol. 9). Academic Press.
  • Seinfeld, J. H., & Pandis, S. N. (2016). Atmospheric Chemistry and Physics: From Air Pollution to Climate Change (3rd ed.). John Wiley & Sons.
  • Finlayson-Pitts, B. J., & Pitts Jr, J. N. (2000). Chemistry of the Upper and Lower Atmosphere: Theory, Experiments, and Applications. Academic Press.
  • Mannschreck, K., Gilge, S., Plass-Duelmer, C., Fricke, W., & Berresheim, H. (2004). Assessment of the applicability of NO-NO2-O3 photostationary state to long-term measurements at the Hohenpeissenberg GAW Station, Germany. Atmospheric Chemistry and Physics, 4(5), 1265–1277. https://doi.org/10.5194/acp-4-1265-2004 (Mannschreck et al., 2004)

Moreno Comelli, Ugo Cortesi, Valentina Colcelli & Alessandra Langella, CNR-IFAC, 2022-2026


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