The present invention relates to a method for reducing the emission of gaseous nitrogen oxides according to the preamble of claim 1. Furthermore, it relates to a reactor arrangement for executing the method.
Nitrogen oxides are generated e.g. by oxidation reactions with nitric acid (HNO3) as one reactant. The acid may be used in a pure state, i.e. as an aqueous solution of appropriate concentration, or mixed with other components. One of the most prominent partners is hydrochloric acid yielding aqua regia for solving precious metals like gold. However, also oxidation reactions of organic substances are performed in applying nitric acid as the oxidizing agent.
By the oxidation reaction, the nitric acid is reduced, whereby nitrogen oxides are generated which leave the reaction medium as gases. However, due to health and environment protection provisions, these gases shall not be emitted into the air.
Hence, the waste gases from such reactors are cleaned by gas washers, where the nitrogen oxides are absorbed and bound. The active component of the gas washers has a certain life time and/or has to be exchanged regularly.
Another possibility of avoiding the emission of nitrogen oxides is the oxidation in situ by adding hydrogen peroxide (H2O2aq) to the reaction medium. However, thereby, water is added to the reaction medium which negatively influences the reaction conditions and has to be removed eventually. Furthermore, if no stabilizers are present in the hydrogen peroxide solution, it is difficult to handle and can not be preserved. The stabilizers, on the other hand, may disturb the chemical reaction and have to be removed later on.
Accordingly, it is one object of the present invention to propose a method for suppressing the generation of nitrogen oxide generation in situ and to less disturb the oxidation reaction.
Such a method is defined in claim 1. The further claims present preferred embodiments and reactor arrangements for executing the method.
Generally, the invention is based on the suprising discovery that ozone may be used to reoxidize the reaction products of the reduction of nitric acid (HNO3) in situ. Particularly, it has been found that supplying e.g. oxygen with an effective content of ozone may be supplied to a reaction solution for oxidatively solving metals without disturbing the oxidation reaction of nitric acid.
Furthermore, ozone containing gas may also be supplied to reaction mixtures for oxidizing organic substances. In these applications, however, depending on the reaction and the reaction partners, the ozone may interfere with the desired oxidation process, so the use of ozone at all or the composition of the ozone charged gas has to be tested more carefully as in the inorganic applications.
A preferred manner of supplying the ozone containing gas is a conduit or tube extending into the reaction medium. The ozone containing gas emanates from the end of the conduit and bubbles through the reaction medium, thereby reoxidizing the nitrogen oxides.
Advantageously, the end of the conduit is provided with means like a frit for creating many small bubbles in order to increase the exchange rate of ozone between the bubbles and the solution.
The invention will be explained by means of execution examples. The only
The reactor arrangement 1 consists of the reactor 3, which is provided with a supply unit 5 for the ozone containing gas. Otherwise, the reactor may be of conventional structure. Here, it is provided with a stirrer 7, driven by a motor 8, and a drop funnel 10 with valve 11, which allows the adjustable addition of e.g. HNO3 or aqua regia (nitrohydrochloric acid). In this example, a tube 13 guides the agent well below the surface 15 of the reaction solution 17 near the blade 19 of the stirrer 7 for immediate and effective mixing.
The ozone supply unit 5 comprises a gas supply 21 providing air, oxygen or a mixture thereof. The gas passes the ozone generator 23 according to arrow 25. Inter alia, the ozone generator is provided with a tubing 26 for a cooling liquid.
At the exit 29 of the ozone generator 23, an ozone measuring instrument 31 is connected as well as the conduit 33 to the reactor 3. For security reasons, a nonreturn valve 35 is integrated in the conduit 33. The gas conduit 33 extends into the interior of the reactor with its end 36 below the surface 15 of the reaction solution 17. The end 36 is provided with a frit body 37 for subdividing the exiting gas into small bubbles.
The reactor 3 is further provided with a venting tube 39, which is provided with an ozon destroyer unit 40 for removing residual ozone from the exiting gas. Ahead of the destroyer unit 40, the ozone measuring instrument 31 is connected with the venting tube 39. By measuring the difference of ozone contents before and after the reactor, the reoxidation reaction and indirectly the main reaction can be observed.
Obviously, due to the instability of ozone and its decay into oxygene, the destroying of residual ozone is possible without effort. The elements of the ozone supply unit 5 and the residual ozone destroyer unit 40 are known per se and, therefore, do not need to be described in detail. The destruction of the ozone may be done thermically and without use of any chemical agents.
One application example for oxidation by nitric acid is the production of nitrate salts of metals and of chlor compounds (complexes) of precious metals. Some exemplary reactions will be given.
Ex. 1: Copper
Oxidation
Cu+4HNO3=Cu(NO3)2+2NO2+2H2O
Ozonisation (Reoxidation NO2)
2NO2+O3=N2O5+O2
Reaction with water
N2O5+H2O=2HNO3
Total reaction (non-reduced)
Cu+4HNO3+O3=Cu(NO3)2+2HNO3+O2+H2O
As a result, half of the nitric acid is recycled and no nitrogen oxide is produced.
Ex. 2: Gold/Aqua Regia
Oxidation
Au+HNO3+4HCl=H[AuCl4]+NO+2H2O
Ozonisation (Reoxidation of NO2)
a) 2NO+2O3=2NO2+2O2
b) 2NO2+O3=N2O5+O2
Reaction with Water
N2O5+H2O=2 HNO3
Total Reaction (Non-Reduced)
2Au+2HNO3+8HCl+3O3+H2O=2 H[AuCl]+HNO3+4H2O+3 O2
The nitric acid is recycled in its entirety and no nitrogen oxide gas is produced.
Regarding the overall reaction, oxygen appears as the reduction product of ozone. In contrast, if the same reactions are performed using H2O2, water results, hence the reaction solution is diluted and for obtaining the products, the addtionally created water has to be removed by vaporization, requiring considerable energy.
For best results, the addition rate of ozone is stoichiometric with regard to the addition of the other agents, e.g. the addition of nitric acid resp. aqua regia. Of course, alternatively, the metal may be added continuously to the acid, e.g. as metal flakes.
For this purpose, a photometer (not shown) may be used that is sensitive to the colour of nitrogen dioxide (NO2). The photometer examines the exhaust gas of the reactor. If it detects NO2, it creates an appropriate signal which is used to increase the rate of ozone addition. The rate of addition of ozone may be adjusted by regulating the total-flux of ozone containing gas, and/or by changing the ozone content.
A preferred range of ozone content is 2 to 15% by weight of ozone in the gas.
On the basis of the examples given above, the one skilled in the art may conceive numerous variants and applications of the invention without leaving the scope of protection which is defined by the claims.
For instance, as mentioned in the beginning, the method may also be used for oxidation processes of organic components. The necessary preliminary experiments for determining the correct process conditions, as ozone may react undesirably with one of the other agents, particularly an organic reactance, are a routine measure.
Another aspect consists in that the reaction rate of ozone with any nitrogen oxide NOx is of first order. Hence, by varying the concentration of the nitric acid concentration and/or the ozone concentration, the selectivity of the reaction of ozone with either NO, or other components of the reaction mixture may be adjusted for best results and yield.
It is still conceivable that the carrier gas for the ozone has another composition: E.g. it may contain inert gases like argon.
Filing Document | Filing Date | Country | Kind | 371c Date |
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PCT/CH03/00310 | 5/14/2003 | WO | 11/14/2005 |