DESTRUCTION
TECHNOLOGIES FOR OZONE DEPLETING SUBSTANCES :
The
purpose of destruction of CFCs, halons, 1,1,1 trichloroethane and carbon tetrachloride
is to convert them into safe materials. Technologies in this regard are in the
research stage and as yet there are no commercially available plants. Only thermal
destruction of PCB at high temperature is a proven technology for treating chlorinated
organic compounds.
In principle, the safe destruction of CFCs and other
halogenated compounds requires three steps.
-
dissociation of C-F and C-CI bonds in the molecules
-
conversion of constituent atoms to stable molecules, i.e. C to CO2, F to HF, CI
to HCI, Br to HBr.
-
neutralization of the acids; since CFCs and other fullyhalogenated carbon compounds
have no hydrogen, it is necessary to treat them with hydrogen containing substance
such as petroleum.
|
For the destruction of CFCs and relevant compounds, energy or promoter is required
to dissociate the strong C-F, C-CI and C-Br bonds in the molecules. Depending
on the means of initiating the dissociation, the technologies are classified as
follows:
Energy-oriented destruction
- Incineration/Thermal
decomposition
| (Thermal
energy) |
| | (Electric
energy) |
| | (Chemical
energy) |
- Photochemical/Radioactive
Ray decomposition
| (Radiation
energy) |
Promoter-oriented
destruction
-
Catalytic decomposition
- Biological
decomposition
|
CFCs
are thermally and chemically stable substances. It is extremely difficult to decompose
them, when compared with hydrocarbons, and there has been no necessity to do so,
either. Consequently, extensive research has not been done in this respect. Transformation
of CFCs includes (a) returning to raw materials such as hydrogen chloride and
hydrogen fluoride by decomposing constituent elements and (b) synthesis of alternatives
to CFCs such as HCFs, as well as polymers such as Teflon from CFCs.
In
the Incineration and Thermal Decomposition, CFCs are decomposed in internal combustion
or external burners with burning petroleum. Thermal decomposition of CFCs requires
a temperature of more than 700oC.
Under the Plasma Decomposition Method,
it is possible to have continuo0us decomposition reaction in a radio-frequency
inductive-coupling plasma reactor. In this method, inductive heating at radio
frequency around the tubular plasma torch under atmospheric pressure in presence
of Argon produces plasma within the torch. Plasma, having temperature distribution,
reaches a maximum temperature of nearly 10,000oC at its center. When gaseous CFCs
are introduced into this flow, CFCs are decomposed rapidly.
In Catalytic
Decomposition Method, CFCs are decomposed by continuously circulating CFCs and
steam on a solid catalyst. The high performance solid catalysts include zeolite,
alumina, binary oxide of TiO2 - ZrO2 and iron oxide supported on activated carbon.
In Reagent Decomposition Method, CFCs are reductively decomposed by
a sodium naphthalene reagent dissolved in an organic solvent, which reacts with
gaseous or liquid CFCs and thereby gives NaCl and NaF through the neutralization
between Na+ ions in the reagent and Cl and F in CFCs.
The Super Critical
Water Decomposition Method utilizes the fact that a super critical state is formed
in water beyond the critical point of water, state-facilitating hydrolysis. It
is reported that CFC-11 and CFC-113 are almost completely decomposed at 400oC
and 320 atm.
Study is being conducted on synthesizing chlorotrifluoroethylene
monomers by dechlorinating or hydrogenationdehydrochlorinating of CFC-113 to make
fluorine polymers (polychlorotrifluoroethylene). For these processes, various
technologies are being studied, including thermal decomposition, catalysis and
electrochemistry.