GB2299080A - Process for the destruction of halocarbons - Google Patents

Process for the destruction of halocarbons Download PDF

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Publication number
GB2299080A
GB2299080A GB9506067A GB9506067A GB2299080A GB 2299080 A GB2299080 A GB 2299080A GB 9506067 A GB9506067 A GB 9506067A GB 9506067 A GB9506067 A GB 9506067A GB 2299080 A GB2299080 A GB 2299080A
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Prior art keywords
sodium
halocarbon
reaction
contacting
halocarbons
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GB9506067A
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GB9506067D0 (en
Inventor
Maurice Raymond Hillis
David Alan Gardner
David James Ambrose
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EA Technology Ltd
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EA Technology Ltd
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Priority to GB9506067A priority Critical patent/GB2299080A/en
Publication of GB9506067D0 publication Critical patent/GB9506067D0/en
Priority to AU51513/96A priority patent/AU5151396A/en
Priority to PCT/GB1996/000684 priority patent/WO1996030084A1/en
Publication of GB2299080A publication Critical patent/GB2299080A/en
Withdrawn legal-status Critical Current

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    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D3/00Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
    • A62D3/30Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
    • A62D3/32Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents by treatment in molten chemical reagent, e.g. salts or metals
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D3/00Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
    • A62D3/30Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
    • A62D3/36Detoxification by using acid or alkaline reagents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/68Halogens or halogen compounds
    • B01D53/70Organic halogen compounds
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/20Organic substances
    • A62D2101/22Organic substances containing halogen

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Health & Medical Sciences (AREA)
  • General Chemical & Material Sciences (AREA)
  • Business, Economics & Management (AREA)
  • Toxicology (AREA)
  • General Health & Medical Sciences (AREA)
  • Emergency Management (AREA)
  • Engineering & Computer Science (AREA)
  • Biomedical Technology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Analytical Chemistry (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)

Abstract

A process for the destruction of halocarbons comprises supporting metallic sodium at a temperature above its melting point on a solid particulate carrier material and contacting the halocarbon or halocarbons in a gaseous state with the supported sodium to react the halocarbon or halocarbons with the sodium to form elemental carbon and sodium halide or halides.

Description

PROCESS FOR THE DESTRUCTION OF RALOCARBONS This invention relates to a process for the destruction of halocarbons.
In recent years the effect of halogenated hydrocarbons (hereinafter referred to as halocarbons) on the environment has been the cause of considerable concern throughout the world with much attention being given both to the reduction of production of halogenated hydrocarbons and also the disposal of the considerable stocks of these compounds which exist worldwide, for example-for use in refrigeration equipment, fire extinguishers, etc. Due to the international agreement reached in the Montreal Protocol and subsequent national legislation there has been considerable interest in particular in finding effective ways of destroying these compounds in an environmentally acceptable manner.
It has been realised for some time that destruction of halocarbons by reaction with sodium is theoretically environmentally desirable because potentially it enables halocarbons to be converted entirely to benign solid products that have no deleterious properties and thus volatile compounds which are capable of depleting ozone in the earth's ozone layer and contributing to the greenhouse effect are effectively completely disposed of without any risk to the environment.
Thus, for example, bromo-trifluoro methane, which is commonly known as Halon 1301, is used as a fire extinguisher agent. However, it has a very high ozone depletion potential and is a powerful greenhouse gas.
There is therefore considerable interest in finding an effective means for disposing of stocks of this halon.
It is known that Halon 1301 can be reacted with molten sodium to convert it into carbon, sodium fluoride and sodium bromide by the following reaction CF3Br+4Na5C+3NaF+NaBr.
Thus all of the products of the reaction are solid and, moreover, have potential value. Also they have no adverse environmental effects.
However, there are several practical problems in carrying out the above-mentioned chemical reaction.
The reaction with molten sodium is very exothermic and complex in that the gaseous halocarbon reacts with the liquid sodium to produce solids. The exothermic nature of the reaction means that unless the mixture is kept well stirred, hot spots with sparking and glowing can develop. Furthermore, the reaction mixture becomes sticky and very viscous as more and more solid products build up and the mixture tends to bind into a solid mass.
The resulting mixture can become very difficult to stir and sodium can become trapped and inaccessible to halocarbon in the body of the sticky, solid mass.
Unreacted sodium remaining at the end of a reaction is both an economic loss and potentially hazardous and it must therefore be neutralised, typically by reaction with methanol.
It has now been discovered that if the molten sodium is dispersed on a solid particulate support material the reaction is much more controllable. Hot spots sparking and glowing do not develop and the temperature in the reactor can easily be controlled by limiting the flow of halocarbon gas entering the reactor. Alternatively or additionally the reactor can be jacketed and a cooling medium circulated through the jacket to control the reaction temperature.
Moreover, the reaction mixture remains free flowing and easily stirrable throughout the reaction.
This means that low-power motors can be used or a fluidised bed system can be employed. Moreover, very high utilisations of sodium can be achieved particularly, as the Applicants have discovered, if the process is carried out under pressure. As the reaction is mass transfer limited, the increased pressure generates greater driving force and therefore maintains a high overall reaction rate. The supported sodium is in thin layers and therefore there is no opportunity for thick product layers to form that could inhibit the reaction.
It has also been found that it is possible to operate the process so that at the end of a reaction it is unnecessary to destroy any unreacted sodium. It is also possible to admit more molten sodium and disperse it on the solid support together with the solid products and repeat the halocarbon destruction reaction again and again. It has been shown experimentally that the same support can be re-used at least twenty times.
Thus, according to the present invention there is provided a process for the destruction of halocarbons which process comprises supporting metallic sodium at a temperature above its melting point on a solid particulate carrier material and contacting the halocarbon or halocarbons in a gaseous state with the supported sodium to react the halocarbon or halocarbons with the sodium to form elemental carbon and sodium halide or halides.
As will be realised, the process of the present invention can be applied to any halocarbon which exists in, or can be brought into, the vapour state for contact with the supported sodium in accordance with the method of this invention. However, the invention has particular applicability to halons, CFCs (chlorofluorocarbons), HCFCs (hydrochlorofluorocarbons), HFCs (hydrofluorocarbons) and halogenated solvents. These particular halocarbons are those which have given particular concern from an environmental point of view.
As mentioned above, the sodium metal used in the method of the invention is at a temperature above its melting point. It is preferred that the sodium is held at a temperature in the range from 980C to 5000C, and more preferably at a temperature in the range of 980C to 3000C.
The solid particulate carrier material may, for example, be silica, alumina, sand, glass beads, carbon, salts or any other similar solid materials in a finely divided form. Preferably the particle size is below 500 Hm. Sand has been found to be a particularly useful carrier material being relatively inexpensive and freely available. However, it is envisaged that other support materials may have particular usefulness for certain applications, for example carbon, this of course being one of the products of the chemical reaction which forms the basis of the process.
The halocarbon will usually be passed in gaseous form into a reactor vessel containing the supported molten sodium. If the halocarbon is in liquid form it will be vaporised before being passed into the reactor vessel.
Although both of the main steps of the method of the invention, as defined above, can be carried out in the same reactor vessel the molten sodium may be dispersed on a heated solid support material in a preparation vessel preferably under a blanket of inert gas such as nitrogen, the supported molten sodium being then passed into the main reactor vessel where it is contacted with the gaseous halocarbon.
Alternatively, the sodium may be dispersed on the heated solid particulate support material under a blanket of inert gas in the same reactor as that in which the halocarbon destruction is subsequently to be carried out. Then, the halocarbon in gaseous or vaporised form may be admitted to a reactor which is filled with inert gas and which contains the supported molten sodium.
Although the reactor, or main reactor, may have a fixed bed of supported sodium it is usually preferred that the particulate support material with sodium supported thereon is kept in motion, e.g. by stirring or by use of a fluidised bed technique, this having the advantage that reaction products are not permitted to combine into a continuous phase and therefore cause the bed to solidify.
Preferably the amount of sodium dispersed on the particulate support material prior to the halocarbon destruction reaction is from 1 to 50 weight percent, and more preferably from 5 to 15 weight percent.
The temperature of the supported sodium may be controlled by controlling the rate at which halocarbon is admitted to the reaction chamber and/or by use of a cooling jacket placed around the reactor. It is necessary, from time to time, to remove the solid products of the reaction, namely carbon and sodium halides, from the reactor. This can be done in a semi-batch mode by removing a proportion of the solid material at the end of a halocarbon reaction phase and quenching it in water or alcohol to remove any residual sodium. The sodium halides can be dissolved away and the carbon removed. The particulate base support material can then be removed, dried and then re-used. An equivalent amount of support material may be added each time solid product and support material is removed from the reactor. The products can then be worked up for value.For example, bromine can be recovered from aqueous sodium bromide by passing in chlorine gas.
An operation in semi-batch manner can also involve dispersing further sodium on the support material in the reactor vessel when the majority of the sodium has been consumed in a first batch.
Alternatively, when the majority of the sodium has been consumed in a first batch further supported sodium can be added from a sodium preparation vessel to the reactor vessel and the halocarbon destruction reaction repeated. As mentioned above, some of the solid material (i.e. particulate support material and products) may be withdrawn from the reactor vessel and this may be done before an addition of sodium or supported sodium so as to maintain the percentage of sodium dispersed on the support materials within a preferred range, as indicated above.
As an alternative to a batch or semi-batch mode of operating the method, the process can be operated in a continuous manner in which supported sodium is continuously fed from a sodium preparation vessel into the main reactor vessel at such a rate that the sodium is largely consumed by the time the solid materials (i.e. the particulate support material together with solid products) flow out of the reactor vessel.
As also indicated above, solid materials may be withdrawn from the reactor and thereafter quenched in water or an alcohol to remove any residual sodium and to dissolve sodium halides, the particulate support material being then treated as desired and returned for re-use in the process.
A factor which has been found to be important in the operation of the method of the present invention has been the pressure at which the process is performed. Bearing in mind that the reaction between molten sodium and gaseous halocarbons tends to be very vigorous and exothermic it is perhaps surprising that any suggestion should be made that the reaction be carried out at a pressure greater than atmospheric pressure. However, the Applicants have found that by carrying out the method of the invention above atmospheric pressure, or by causing or allowing the pressure to increase above atmospheric pressure as the reaction proceeds, has an effect that the reaction proceeds more completely and that little or no sodium remains in the solid mixture after reaction which has to be disposed of as described above by reaction with water or alcohol.This clearly has considerable advantages in that the process is not only simplified but more efficient use is made of the sodium. It is not entirely understood how the increase in pressure should have this desirable effect but, as mentioned hereinbefore, it is conjectured as the reaction is mass transfer limited, the increased pressure generates greater driving force and therefore maintains a high overall reaction rate. Preferably the increase in pressure over atmospheric pressure is at least d Bar absolute. The effect of operating under pressure as compared with a similar process in which the destruction of the halocarbon is not under pressure is shown in the following specific examples.
Example 1 Non-Pressurised Destruction of Halon 1301 (Bromo-trifluoro methane) The reactor as shown diagrammatically in Figure 1 consists of a 500 ml reaction flask complete with flange head with several inlets into the reactor. One inlet is for the stirrer, another inlet is a combined thermocouple and gas delivery point for the direct introduction of nitrogen and halon into the support.
Another inlet is used for charging sand and sodium to the reactor, and one is used for the gas exit stream from the reactor to the wash bottle.
A charge of 202.58 g of pre-dried sand (average particle size 145 pm) was added to the reactor vessel and heated under a nitrogen purge and gentle agitation to 2000C. When the sand had attained this temperature, a charge of 10.45 g of sodium was added to the sand through the inlet. The support was maintained at 2000C while the sodium charge was allowed to disperse evenly over the support, at 125 rpm. After 10 mins. when an even dispersion had been achieved the nitrogen flow and heating mantle were shut off in preparation for the halon introduction.
The halon flow was set at approx. 250 cc/min and the halon was allowed to flow into the reactor, where it reacted with the sodium and was destroyed. The agitation was set and maintained at 125 rpm through the course of the experiment. At 60 secs. into the reaction an exotherm had been observed and the support temperature had risen from 2030C to 2140C. This exotherm continued and the support temperature rose steadily until it peaked after 14 mins. at a temperature of 2870C. The temperature of the support then fell steadily. After 30 mins. and at a temperature of 2240C the halon flow to the bed was stopped. The reaction was deemed complete and the vessel was allowed to cool to room temperature under nitrogen.
226.58 g of support, products and any unreacted sodium were recovered from the vessel.
A 55.98 g sample was taken for analysis.
The sample contained 0.54 g of unreacted sodium.
Therefore the total unreacted sodium remaining on the support was 2.19 g.
The sodium added at the start of reaction was 10.45 g.
Therefore 8.26 g of sodium reacted with 13.53 g of halon 1301.
Consumption of sodium was 79%.
Example 2 Pressurised destruction of the halon 1301.
The reactor consists of a 500 ml reaction flask complete with flange head with several inlets into the reactor. One inlet is for the stirrer, another inlet is a combined thermocouple and gas delivery point for the direct introduction of nitrogen and halon into the support. Another inlet is used for charging sand and sodium to the reactor, and one is used for the gas exit stream from the reactor to the recirculating pump, which recirculates the gas to the gas inlet port.
Essentially the equipment is the same as for Example 1. However this experiment was operated in a sealed system, with the pressure of the system being controlled by the regulator on the halon cylinder.
Also a recirculating pump was used to continually recirculate the gas in the reactor through the support.
The particulate support for this experiment consisted of 170.6 g from the support used in Example 1, which remained after the 55.98 g sample was removed for analysis. In addition 57.45 g of fresh pre-dried sand was added, giving a total support weight of 228.05 g. There was 1.65 g of unreacted sodium remaining on the support from the 170.6 g portion used from Example 1.
This support of 228.05 g was added to the vessel and heated under a nitrogen purge and gentle agitation to 2000C. When the support had attained this temperature, a charge of 11.99 g of sodium was added to the support through the inlet. The support was maintained at 2000C while the sodium charge was allowed to disperse evenly over the support, at 100 rpm. After 10 mins. when an even dispersion had been achieved the nitrogen flow and heating mantle were shut off in preparation for the halon introduction.
The pressure in the reactor at this stage is 1 atm. (absolute) of nitrogen and any pressures referred to hereinafter are gauge pressures.
The regulator on the halon 1301 cylinder was set at 0.5 Bar and the recirculating pump connected to seal the reactor system. The stirrer was set at 100 rpm and the halon flowrate set at approx. 250 cc/min.
At the start of the halon introduction when the pump was switched on and the halon flowrate set, a drop in temperature reading was observed. This was due to the pressure created from the pump displacing the support from around the thermocouple. Therefore it was a few minutes before equilibrium was established and the temperature rise due to the exotherm truly recorded. At 2 mins. the temperature of the support was 1900C and the pressure in the reactor had risen to 0.2 Bar. At 4 mins. the temperature of the support was 1970C and the pressure in the reactor had risen to 0.3 Bar. The support continued to rise steadily in temperature and pressure until at 27 mins. the exotherm peaked at a temperature of 2870C and a pressure of 0.45 Bar. Then the support temperature steadily fell, but the pressure in the reactor gradually increased to match the set cylinder pressure of 0.5 Bar.After 40 mins. at a temperature of 1380C and a pressure of 0.5 Bar the reaction was stopped and the reactor allowed to cool to room temperature under nitrogen.
258.35 g of support, products and any unreacted sodium were recovered from the reaction vessel.
A 58.24 g sample was taken for analysis.
The sample contained 0.23 g of unreacted sodium.
Therefore the total unreacted sodium remaining on the support was 1.02 g.
The sodium present on the support from Example 1 was 1.65 g, the sodium added was 11.99 g, giving a total of 13.64 g of sodium available.
Therefore the total sodium used in this reaction was 13.64 - 1.02 = 12.62 g.
Therefore 100% utilisation of the 11.99 g sodium added this experiment was achieved, plus an additional 0.63 g of sodium bound on the support from the previous experiment Example 1 was consumed, destroying in total 20.43 g of the halon 1301.
This indicates that the pressurised system, of Example 2, is a significant improvement over the nonpressurised system. Not only was the fresh charge of sodium completely consumed in the reaction, but also the sodium remaining on the support from the previous experiment, Example 1, had been more efficiently reacted.

Claims (10)

CLAIMS:
1. A process for the destruction of halocarbons which process comprises supporting metallic sodium at a temperature above its melting point on a solid particulate carrier material and contacting the halocarbon or halocarbons in a gaseous state with the supported sodium to react the halocarbon or halocarbons with the sodium to form elemental carbon and sodium halide or halides.
2. A process as claimed in claim 1 wherein the contacting of the halocarbon with the sodium is performed at an elevated pressure.
3. A process as claimed in claim 1 wherein the pressure is caused or permitted to rise during the contacting step.
4. A process as claimed in any one of the preceding claims wherein the particle size of the solid particulate material is below 500 ,um.
5. A process as claimed in any one of the preceding claims wherein the step of supporting the metallic sodium on a solid particulate material is performed in a reaction vessel separate from that in which the contacting of halocarbon with the sodium is performed.
6. A process as claimed in any one of the preceding claims when performed as a semi-batch process in which a part of the solid reaction mixture is removed after a first reaction phase and/or fresh sodium alone or supported sodium is added before a second reaction phase.
7. A process as claimed in any one of claims 1 to 5 when performed as a continuous process in which supported sodium is continuously supplied to the reaction vessel and solid reaction product material is continuously removed from the reaction vessel.
8. A process as claimed in any one of the preceding claims wherein the solid particulate carrier material is maintained in motion during the contacting of the halocarbon with the sodium, for example by stirring or by a fluidised bed procedure.
9. A process as claimed in any one of the preceding claims wherein the amount of sodium dispersed on the particulate support material prior to contacting with the halocarbon is from 1 and 50 weight percent, preferably from 5 to 15 weight percent.
10. A process as claimed in claim 1 substantially as hereinbefore described in each of the Examples and with reference to the accompanying drawing.
GB9506067A 1995-03-24 1995-03-24 Process for the destruction of halocarbons Withdrawn GB2299080A (en)

Priority Applications (3)

Application Number Priority Date Filing Date Title
GB9506067A GB2299080A (en) 1995-03-24 1995-03-24 Process for the destruction of halocarbons
AU51513/96A AU5151396A (en) 1995-03-24 1996-03-22 Process for the destruction of halocarbons
PCT/GB1996/000684 WO1996030084A1 (en) 1995-03-24 1996-03-22 Process for the destruction of halocarbons

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GB9506067A GB2299080A (en) 1995-03-24 1995-03-24 Process for the destruction of halocarbons

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GB9506067D0 GB9506067D0 (en) 1995-05-10
GB2299080A true GB2299080A (en) 1996-09-25

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1997022386A1 (en) * 1995-12-19 1997-06-26 The University Of Manchester Institute Of Science & Technology Destruction of halocarbons
US11512013B2 (en) * 2019-09-18 2022-11-29 Ralph Birchard Lloyd System and method of reducing oxidants in a chemical stream

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4639309A (en) * 1985-09-18 1987-01-27 Hydro-Quebec Process for the dehalogenation of polyhalogenated hydrocarbon containing fluids
EP0467053A1 (en) * 1990-07-16 1992-01-22 Degussa Aktiengesellschaft Process for the dehalogenation of organic compounds by alkali metals on solid supports
WO1994003237A1 (en) * 1992-08-06 1994-02-17 Ea Technology Limited A process for the destruction of halocarbons

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE4236382A1 (en) * 1992-10-28 1994-05-05 Degussa Process for the implementation of CFCs with dispersions of alkali metals

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4639309A (en) * 1985-09-18 1987-01-27 Hydro-Quebec Process for the dehalogenation of polyhalogenated hydrocarbon containing fluids
EP0467053A1 (en) * 1990-07-16 1992-01-22 Degussa Aktiengesellschaft Process for the dehalogenation of organic compounds by alkali metals on solid supports
WO1994003237A1 (en) * 1992-08-06 1994-02-17 Ea Technology Limited A process for the destruction of halocarbons

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO1997022386A1 (en) * 1995-12-19 1997-06-26 The University Of Manchester Institute Of Science & Technology Destruction of halocarbons
US11512013B2 (en) * 2019-09-18 2022-11-29 Ralph Birchard Lloyd System and method of reducing oxidants in a chemical stream

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WO1996030084A1 (en) 1996-10-03
AU5151396A (en) 1996-10-16
GB9506067D0 (en) 1995-05-10

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