PAOR SYSTEM

NOX / SOX Ozone treatment technology

What is NOx / SOx ozone treatment technology?

NO and SO2 are oxidized, by adding ozone, into highly soluble oxides (NO2, N2O3, N2O5, SO3 etc.) which can be treated by wet scrubbers

Principles of ozone treatment reaction

  1. Main scheme

    • NO2 + O3 → O2 + NO3
    • 2NO2 + O3 → N2O5 + O2
    • NO2+NO3 → N2O5
    • NO + O3 → NO2 + O2
    • 2NO + 3O3 → N2O5 + 3O2
    • NO is the main component of NOX in the combustion gas
    • Highly soluble NO2, N2O3and N2O5 are produced by the reaction between NOx and ozone, which are absorbed in to an alkaline solution
  2. Reaction rate and solubility

    Scheme Relative reaction rate
    NO + O3 → NO2 + O2 62780 fast
    2NO2 + O3 → N2O5 + O2 135 little fast
    SO2 + O3 → SO3 + O2 8 slow
    CO + O3 → CO2 + O2 1 very slow
    Substance NO NO2 SO2 N2O5
    Solubility(25℃) 0.063 1.26 126 >126
    • NOxis rapidly converted into a water-soluble substance because the reaction rate with ozone is very fast compared to other substances
    • Easily adsorbed by washing with water after becoming NO2, N2O5

Process chart

Features

  • High temperature not required unlike SCR(300~420℃) and SNCR(850~1,100℃)
  • Inexpensive maintenance cost as an expensive catalyst is not required
  • No need for a large site because ozone is injected into the existing wet scrubber
  • Treatment of various pollutants such as dioxin, carbon monoxide, etc.
  • Highly efficient treatment at 80% or higher
  • Nearly no secondary pollution
  • Possible combination with other treatment methods such as SCR and SNCR
  • Interconnected operation depending on the concentration level of pollutants
  • Simple operation and easy maintenance because the management is mostly required for ozone generators

Comparison with the conventional treatment method

Item SCR SNCR Ozone
Installation scale Renovating the exhaust gas piping Add SCR reactor Modification of piping inside the incineration facility.
Increased ammonia/urea injection piping
Only one exhaust gas pipe is renovated
Impact on incineration facility No effect on incineration facilities Incineration facility in case of trouble.
Stop and check
No effect on incineration facilities
Installation period Relatively long Relatively long Relatively short
Operation risk evaluation Catalyst poisoning during driving, presence of ammonia leaks, ets. Blockage of urea gun, rupture of pipe, presence of ammonia leaks, ets. After the reaction,
the residual gas is oxygen
no additional pollution due to
secondary conversion
Treatment efficiency 80~90% 40~60% 80~95%

Actual installation

  1. ○○ paper mill : Removal NOx / SOx

    • Treatment : 65,000N㎥/h
    • Ozone generation : 14.5㎏/h, 16wt%
    • NOx treatment efficiency : 90%

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