NZ223232A - Destroying chlorinated organic products using chloroaluminates - Google Patents

Destroying chlorinated organic products using chloroaluminates

Info

Publication number
NZ223232A
NZ223232A NZ223232A NZ22323288A NZ223232A NZ 223232 A NZ223232 A NZ 223232A NZ 223232 A NZ223232 A NZ 223232A NZ 22323288 A NZ22323288 A NZ 22323288A NZ 223232 A NZ223232 A NZ 223232A
Authority
NZ
New Zealand
Prior art keywords
chloroaluminate
products
bath
chlorinated
chlorinated organic
Prior art date
Application number
NZ223232A
Inventor
Jacques Dugua
Original Assignee
Atochem
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Atochem filed Critical Atochem
Publication of NZ223232A publication Critical patent/NZ223232A/en

Links

Classifications

    • 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
    • A62D2101/00Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/20Organic substances
    • A62D2101/22Organic substances containing halogen

Landscapes

  • Business, Economics & Management (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • General Health & Medical Sciences (AREA)
  • Emergency Management (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
  • Developing Agents For Electrophotography (AREA)
  • Dental Preparations (AREA)
  • Manufacturing Of Magnetic Record Carriers (AREA)
  • Photoreceptors In Electrophotography (AREA)
  • Paper (AREA)
  • Food Preservation Except Freezing, Refrigeration, And Drying (AREA)
  • Pharmaceuticals Containing Other Organic And Inorganic Compounds (AREA)
  • Glass Compositions (AREA)
  • Fire-Extinguishing Compositions (AREA)
  • Luminescent Compositions (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

1. Process for destroying chlorinated organic products containing more than 2 carbon atoms, in which these products are brought into contact with a bath of at least one chloroaluminate, characterized in that the initial concentration of the chlorinated organic products in the bath is 4000 ppm or less and preferably 2000 ppm or less.

Description

New Zealand Paient Spedficaiion for Paient Number £23232 . •' . . . 1A .' ..yZSH' ■ - r- '.'x J,,., ^ NO DRAWINGS Priority Date(s): ... ^.V. ).'&! Complete Specification Filed: ......9^r.
Classr /<5Cr Publication Date: ^.8. .MAY. .193) P.O. Journal, Nor.... 16A.V i.
NEW ZEALAND 22 3 2 3 2 N/43383 \J *f& ■ THE PATENTS ACT 1953 PATENTS FORM NO. 5 COMPLETE SPECIFICATION "PROCESS FOR DESTROYING AT LEAST ONE CHLORINATED PRODUCT CONTAINING MORE THAN TWO CARBON ATOMS" WE, ATOCHEM, a French body corporate (France) of La Defense , 4 & 8 Cours Michelet, 92800 PUTEAUX, France, hereby declare the invention for which we pray that a patent may be granted to us and the method by which it is to be performed, to be particularly described in and by the following statement:- - 1 - (followed by page la) \ 22 3 2 3 2 - l PROCESS FOR-&SSTROYIMC AT LEAST ONE CHLORINATED PROB3€T CONTAINING MORE THAN TWO CARDOH ATOMS The present invention relates to a process for destroying at least one chlorinated organic product 5 containing more than 2 carbon atoms and more particularly chlorinated aromatic products and polychlorobiphenyls.
Certain dielectric liquids contain chlorinated organic products and after a certain period of operation 10 they decompose and need to be replaced. It is sometimes possible to regenerate them completely or partially but it is often necessary to destroy a proportion of these liquids.
Chlorinated organic products, as well as certain pesticides and chlorinated aromatics such as hexachloro-15 benzene or polychlorobiphenyls (PCB) can give rise to toxic products when they are burnt like an ordinary flammable product.
In order to avoid generating toxic products these chlorinated products are destroyed at a high temperature 20 under specific conditions.
A paper in Sci. Total Environ. 1978, 10 (1) 51-9 describes the destruction of polychlorobiphenyls (PCB) by incineration with a residence time of more than 2 seconds.
Another paper, Proc. Ann. Meet - Air Pollut. Control 25 Assoc. 1977 (Vol 2) paper No. 33, describes a 99.9995% destruction of PCBs at 1000°C with a residence time of 2 223232 2 seconds.
European Patent EP 170,714 describes the destruction of PCBs by reaction with molten aluminium or an aluminium-based eutectic; the reaction takes place above 382° C.
A much simpler process for destroying these products, capable of operating below 3 00° C, has now been found according to the present invention.
The present invention provides a process for destroying chlorinated organic products containing more than 2 carbon atoms, characterised in that these products are placed in contact with a bath of at least one chloroaluminate (as hereinafter defined) at a temperature not exceeding 300° C, the quantity of chlorinated organic product being less than 5,000 ppm of the chloroaluminate.
Various chloroaluminates or their mixtures can be employed, for example, potassium, lithium, sodium, calcium, strontium or ammonium chloroaluminates. As used herein,*the name "chloroaluminate" is given to any mixture of anhydrous aluminium chloride and one or more metal chlorides.
"Sodium chloroaluminate", which is preferably employed, denotes a mixture of aluminium chloride and of sodium chloride in any proportions and not only an equimolar mixture. Sodium chloroaluminate may also contain lithium and/or potassium chlorides. It is therefore possible to have a mixture of aluminium chloride, sodium chloride and lithium chloride, which is called sodium lithium. u 223232 chloroaluminate.
It is also preferred that the sodium chloroaluminate should contain at least 50 mol% of aluminium chloride and should have a melting point below 200°C. 5 The invention applies to all chlorinated organic products containing more than 2 carbon atoms, but it is, first and foremost, usable in the case of aliphatic, cyclic, mono- or polycyclic aromatic and heterocyclic products, most especially perchlorinated aliphatic products and 10 polychlorobiphenyls. The quantity of chlorinated organic products is less than 5000 ppm of chloroaluminate and preferably less than 2000 ppm.
These products may be in any form. They may, in particular, be in a solid phase, for example absorbed on 15 active charcoal.
The process according to the invention consists in placing the chlorinated product in contact with the bath of chloroaluminate.
When the chlorinated product is in a solid phase, 20 this solid phase may be poured into the bath of chloroaluminate, preferably stirred. Care should be taken to keep the bath molten, by heating if necessary. The procedure is similar if the chlorinated products are in a liquid phase. In most cases the chlorinated products which 22 3 2 3 2 mixed with light chlorinated products and/or carrier gases. For example, the gas may be one produced by combustion, consisting of nitrogen containing carbon dioxide, carbon monoxide, chlorinated products and possibly oxygen.
However, it may be any gaseous mixture taken from any process.
It is preferable that the chlorinated products should be in an anhydrous phase. The gas containing the chlorinated products may be dried by contact with an 10 absorbent, for example alumina or glycol.
This gaseous phase containing the chlorinated products to be destroyed is then placed in contact with the chloroaluminate using any means for placing a liquid phase in contact with a gaseous phase. This may be a plate- or packed column. The gaseous phase may also be introduced into a stirred vat of chloroaluminate through a dip tube or through a tube entering via the bottom of the vat.
The various chlorinated organic products may partition between the liquid and vapour phases of the 20 chloroaluminate bath. Similar comments apply to the products which accompany these chlorinated products. A plate- or packed column may be employed in order to ensure continuous circulation and stirring of the liquid and gaseous phases and good contact between the gaseous products and the chloroaluminate bath. It is also possible to 22 3 2 32 operate using a cascade of stirred reactors. The chlorinated organic products are kept in contact with the chloroaluminate bath for the period required to destroy them. The residence time may vary within wide limits but is 5 generally from a few minutes to a few hours.
Although it is possible to operate at any temperature, provided that the chloroaluminate is liquid, it is preferable for this to be done at a temperature not exceeding 300°C and preferably at 200° to 300°C. 10 The rate of destruction of the chlorinated products, especially aromatic products, increases with the temperature of the chloroaluminate.
Light products of decomposition of the chlorinated products which it was intended to destroy may be found in 15 the gaseous phase of the chloroaluminate bath, for example carbon tetrachloride and/or hexachloroethane. The chlorinated organic products which it was intended to destroy are not to be found in the vapour phase of the chloroaluminate bath. When the chloroaluminate bath is 20 analysed after contact between the chlorinated products and the chloroaluminate, the organic products which it was intended to destroy are generally not found.
The chloroaluminate bath may also be purged at regular intervals to avoid the accumulation of products 25 which are insoluble or which cannot remain in suspension in 22 3 2 32 the bath.' Generally no trace of the chlorinated organic products is found in this purge either. It can be concluded, therefore, that the chlorinated products which it was intended to destroy have disappeared.
In a preferred embodiment of the invention, one or more powdered metals chosen from reducing metals such as aluminium or zinc, are added to the chloroaluminate bath. It is preferable to employ a powder whose mean particle size is less than 500 p. When metals are employed, the 10 chlorinated organic products can be completely eliminated as previously but at a markedly higher rate, of the order of several times to several tens of times the previous rate.
A consumption of the powdered metal (or metals) is observed, and this may mean that chloride has formed, taking 15 up chlorine from the chlorinated organic products. There is no limit to the quantity of metal powder to be introduced into the chloroaluminate. It is preferable to employ aluminium powder; typically up to 5 or 10% by weight of aluminium powder may be placed in the chloroaluminate bath. 20 it has been found that the rate of destruction of the chlorinated products increases with the quantity of aluminium powder and with the temperature of the chloroaluminate bath. It is preferable to stir the bath so that the metal powder is well dispersed in the bath. The 25 metal chloride or chlorides which have been produced may mix 22 3 2 3 2 with the chloroaluminate bath and may partition between the liquid and gaseous phases. If necessary, the metal chlorides may be removed from the gaseous phase by treating them with a hydroxide, such as sodium hydroxide or potassium hydroxide.
The following Examples further illustrate the present invention: EXAMPLE 1 500 g of sodium chloroaluminate in which the mole ratio AlClj/NaCl = 1 are introduced into an electrically heated 1-litre Pyrex round flask fitted with a propeller stirrer rotating at 300 rev/min. The product is heated to 200°C, stirred, and then 0.2 g of hexachlorobenzene and 0.1 g of decachlorobiphenyl are introduced. After 1 hour at 200°C, 22 32 3 2 the molten bath is purged for 15 minutes with a stream of SO l/h of N2/ which is washed in a bubbler containing 100 ml of hexane.
The chlorinated organic compounds in the final 5 bath and in the' hexane are determined by gas phase chromatography.
The results are shown in Table 1.
EXAMPLE 2 The same test is carried out, but 5X of fine alum-10 inium powder (Pechiney XY 49 grade) are additionally introduced into the chloroaluminate bath. After 1 hour at 200°C followed by purging with 50 l/h of N£ for 15 min, a sample of the bath and of hexane is taken for quantitative analys i s.
TABLE 1 ! ! ru.Scft ! WITHOUT Al ! WITH 5% Al INATED j j 0RGANIC ! I ! X of 1 I 1 X of PRODUCTS | BATH fhexane I product \ BATH f hexane J product 'I <. J { | removed .! j start jfinalj | j start ! ! 1 I ! I 1 ! C,C1, ! 200 till I 13.2 1 37.7 Z! 200 129 ! 3.5 ! 83.7 6 6 , ! 1 I 1 ! ! ! DCBP* I 100 141.3 ! 0.40! 58.3 Z! 100 1 3.8 ! 0.2 ! 96 ! ! ! I ! ! ! ! * OCBP: decachlorobiphenyl - Values in wg 22 3 2 3 2 EXAMPLE 3 The operation is carried out in the same apparatus as employed for Examples 1 and 2, but the operating conditions are changed: - bath temperature: 250°C - weight of the chloroaluminate bath: 500 g - addition of 5% of Al powder (Pechiney XY 49) - duration of the test: 2 hours - nitrogen purge after 2 hours: 15 min - initial addition of: 500 mg of hexachlorobenzene 500 mg of decachlorobiphenyI The results are given in Table 2.
EXAMPLE 4 Same test as in Example no. 3 but the duration of the test is 4 hours.
The results are shown in Table 2.
TABLE 2 ! CHL0R- J INATED j DURATION Z h DURATION 4 h ]ORGANIC f 1 1 * of;!;;;I;X of !;(PRODUCTS!;BATH {;hexane;(product!;BATH;[ hexane.! product];! 1;1 1;]removed |;1;!;jrenoved j;! Is tart;] final!;I;!;start;!fInal {;!;! 1;I I;I;!;I;!;j;:Wh];I 2.5 I;0.7;I;I;! 0.3;!;0.1;!;! I;! 1;!;!;•;!;!;!C6HC1S !;110 I;5;!;!;I 1.5;1;1.3;j;! 6 5 !;! I;!;!;I;!;i;J CC1 1;500;! 8 1;3;!;97.8;1;500;I 1.3;!;3;!;99,15 I;I t;I I;!;!;!;I;I;! DCBP 1;500;I 6 1;0.2;1;98.8;I;500;I 3;!;0.16;!;99.4 !;! I;1 I;!;!;!;!;I;! PS* I I 0.02! 0.002! I ! 0.1 t 0.008! ! 1 1 1 ! ! J ! ! i - PS: perchlorostyrene - Values in mg 223232

Claims (8)

WHAT WE CLAIM IS:
1. Process for destroying at least one chlorinated organic product containing more than 2 carbon atoms, which comprises placing the product in contact with at least one liquid chloroaluminate (as hereinbefore defined) at a temperature not exceeding 300° C, the quantity of chlorinated organic product being less than 5,000 ppm of the chloroaluminate.
2. Process according to claim 1 in which the chloroaluminate is sodium chloroaluminate.
3. Process according to claim 2 in which the sodium chloroaluminate contains at least 50 mol% of aluminium chloride.
4. Process according to any one of claims 1 to 3 in which the said temperature is from 200° to 300° C.
5. Process according to any one of claims 1 to 4 in which the chloroaluminate contains at least one reducing metal powder.
6. Process according to claim 5 in which the reducing metal is aluminium.
7. Process according to claim 5 or 6 in which the mean particle size of the powder does not exceed 500 (i.
8. Process according to claim 1 substantially as described in any one of the Examples. „ , By MMHer/Their Authorised Agerifei A. J. PARK & SON
NZ223232A 1987-01-21 1988-01-19 Destroying chlorinated organic products using chloroaluminates NZ223232A (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
FR8700669A FR2609652B1 (en) 1987-01-21 1987-01-21 PROCESS FOR THE DESTRUCTION OF LOW TEMPERATURE CHLORINE PRODUCTS

Publications (1)

Publication Number Publication Date
NZ223232A true NZ223232A (en) 1991-05-28

Family

ID=9347122

Family Applications (1)

Application Number Title Priority Date Filing Date
NZ223232A NZ223232A (en) 1987-01-21 1988-01-19 Destroying chlorinated organic products using chloroaluminates

Country Status (17)

Country Link
EP (1) EP0277858B1 (en)
JP (1) JPS63192468A (en)
CN (1) CN1012142B (en)
AT (1) ATE51531T1 (en)
AU (1) AU610552B2 (en)
CA (1) CA1333404C (en)
DE (1) DE3860064D1 (en)
DK (1) DK166432B1 (en)
ES (1) ES2014508B3 (en)
FI (1) FI880241A (en)
FR (1) FR2609652B1 (en)
GR (1) GR3000437T3 (en)
IE (1) IE60535B1 (en)
IN (1) IN170563B (en)
NO (1) NO174088C (en)
NZ (1) NZ223232A (en)
PT (1) PT86577B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4931167A (en) * 1987-10-13 1990-06-05 Advanced Refinery Technology Degradation of polychlorinated biphenyls
US5490919A (en) * 1990-08-14 1996-02-13 State Of Isreal, Atomic Energy Commission Process for the dehalogenation of organic compounds
JP4458585B2 (en) * 1999-09-09 2010-04-28 祝治 朝倉 Methods for decomposing and detoxifying harmful organic compounds

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5257149A (en) * 1975-11-07 1977-05-11 Gunma Daigakuchiyou Method of decomposing halogenated aromatic compounds to carboneous substance using molten salts
US4469661A (en) * 1982-04-06 1984-09-04 Shultz Clifford G Destruction of polychlorinated biphenyls and other hazardous halogenated hydrocarbons
US4447262A (en) * 1983-05-16 1984-05-08 Rockwell International Corporation Destruction of halogen-containing materials

Also Published As

Publication number Publication date
NO174088B (en) 1993-12-06
EP0277858A1 (en) 1988-08-10
FI880241A (en) 1988-07-22
GR3000437T3 (en) 1991-06-28
AU610552B2 (en) 1991-05-23
FI880241A0 (en) 1988-01-20
DK23288A (en) 1988-07-22
DE3860064D1 (en) 1990-05-10
NO880104D0 (en) 1988-01-12
DK23288D0 (en) 1988-01-20
IE880137L (en) 1988-07-21
EP0277858B1 (en) 1990-04-04
IN170563B (en) 1992-04-11
PT86577B (en) 1991-12-31
FR2609652A1 (en) 1988-07-22
IE60535B1 (en) 1994-07-27
CN1012142B (en) 1991-03-27
FR2609652B1 (en) 1992-05-15
JPS63192468A (en) 1988-08-09
DK166432B1 (en) 1993-05-24
ATE51531T1 (en) 1990-04-15
NO880104L (en) 1988-07-22
CN88100299A (en) 1988-08-03
CA1333404C (en) 1994-12-06
NO174088C (en) 1994-03-16
AU1062188A (en) 1988-07-28
PT86577A (en) 1988-02-01
ES2014508B3 (en) 1990-07-16

Similar Documents

Publication Publication Date Title
US4246255A (en) Disposal of PCB
EP0208592A1 (en) Process for the destruction of toxic organic products
DE3513731A1 (en) METHOD FOR DESTRUCTING HAZARDOUS WASTE
EA000631B1 (en) Method and apparatus to destroy chemical warfare agents
JPH02500006A (en) Method for dehalogenating halogenated hydrocarbons
NZ223232A (en) Destroying chlorinated organic products using chloroaluminates
Sakai et al. Formation and emission of non-ortho CBs and mono-ortho CBs in municipal waste incineration
DE4042028A1 (en) Plasma chemical disposal of problem substances using alkali metal - or alkaline earth metal or alloy to form solid reaction prod. converted to useful prod.
EP0467053B1 (en) Process for the dehalogenation of organic compounds by alkali metals on solid supports
JPH0626626A (en) Method of decomposing harmful substance generated during removal of organic waste component
JP2918542B1 (en) Method for treating organic halogen compounds
US5174985A (en) Process for the oxidation of water-insoluble organic compounds
RU2068719C1 (en) Method of dehalogenation of halogen-containing organic or organoelemental compounds
JP2001347159A (en) Method for transforming halogen of organic halide and organic compound to inorganic substance and apparatus for the same
Hitchman et al. A feasibility study of the destruction of chemical weapons by photocatalytic oxidation
JP4938931B2 (en) Method for decomposing a hardly decomposable halogen compound
JP4019558B2 (en) Method for decomposing halogenated organic compounds in soil
RU2106168C1 (en) Method for destruction of lewisite
GB2210867A (en) Destruction of environmentally hazardous halogenated hydrocarbons, with lead
RU2064130C1 (en) Method for dehalogenation of halogen-containing organic and organoelemental compounds
DE69713626T2 (en) METHOD FOR THE THERMAL DECOMPOSITION OF POLLUTANTS
CZ286315B6 (en) Decomposition process of toxic and halogenated organic compounds
CASSEL et al. Zinc and titanium smoke: Chemical composition and physical characteristics(Zink-och titanroek: Kemisk sammansaettning och fysikaliska egenskaper)
JPH11114517A (en) Method for decomposing pcb