CA2026506C - Process for the reductive dehalogenation of polyhaloaromatics using calcium and methanol - Google Patents
Process for the reductive dehalogenation of polyhaloaromatics using calcium and methanolInfo
- Publication number
- CA2026506C CA2026506C CA002026506A CA2026506A CA2026506C CA 2026506 C CA2026506 C CA 2026506C CA 002026506 A CA002026506 A CA 002026506A CA 2026506 A CA2026506 A CA 2026506A CA 2026506 C CA2026506 C CA 2026506C
- Authority
- CA
- Canada
- Prior art keywords
- halogenated aromatics
- process according
- methanol
- sodium
- calcium
- Prior art date
- Legal status (The legal status 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 status listed.)
- Expired - Lifetime
Links
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 title claims abstract description 159
- 238000000034 method Methods 0.000 title claims abstract description 73
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 title claims abstract description 24
- 239000011575 calcium Substances 0.000 title claims abstract description 24
- 229910052791 calcium Inorganic materials 0.000 title claims abstract description 24
- 238000005695 dehalogenation reaction Methods 0.000 title claims abstract description 23
- 230000002829 reductive effect Effects 0.000 title claims abstract description 11
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims abstract description 54
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 claims abstract description 33
- 239000011734 sodium Substances 0.000 claims abstract description 33
- 229910052708 sodium Inorganic materials 0.000 claims abstract description 33
- 150000003071 polychlorinated biphenyls Chemical class 0.000 claims abstract description 25
- 238000006243 chemical reaction Methods 0.000 claims abstract description 20
- KFZMGEQAYNKOFK-UHFFFAOYSA-N Isopropanol Chemical compound CC(C)O KFZMGEQAYNKOFK-UHFFFAOYSA-N 0.000 claims abstract description 18
- 239000000203 mixture Substances 0.000 claims abstract description 15
- 229910052736 halogen Inorganic materials 0.000 claims abstract description 6
- 150000002367 halogens Chemical class 0.000 claims abstract description 6
- 239000003921 oil Substances 0.000 claims description 10
- 239000002904 solvent Substances 0.000 claims description 8
- 238000002844 melting Methods 0.000 claims description 5
- 230000008018 melting Effects 0.000 claims description 5
- 239000002689 soil Substances 0.000 claims description 5
- 238000007514 turning Methods 0.000 claims description 5
- 239000002480 mineral oil Substances 0.000 claims description 4
- 235000010446 mineral oil Nutrition 0.000 claims description 4
- 238000000354 decomposition reaction Methods 0.000 claims description 3
- 239000000284 extract Substances 0.000 claims description 3
- 239000012299 nitrogen atmosphere Substances 0.000 claims description 3
- 238000006116 polymerization reaction Methods 0.000 claims description 3
- 238000010438 heat treatment Methods 0.000 claims 2
- 239000000401 methanolic extract Substances 0.000 claims 1
- 230000000382 dechlorinating effect Effects 0.000 abstract 1
- WYURNTSHIVDZCO-UHFFFAOYSA-N Tetrahydrofuran Chemical compound C1CCOC1 WYURNTSHIVDZCO-UHFFFAOYSA-N 0.000 description 25
- BTAGRXWGMYTPBY-UHFFFAOYSA-N 1,2,3-trichloro-4-(2,3,4-trichlorophenyl)benzene Chemical compound ClC1=C(Cl)C(Cl)=CC=C1C1=CC=C(Cl)C(Cl)=C1Cl BTAGRXWGMYTPBY-UHFFFAOYSA-N 0.000 description 19
- 150000001875 compounds Chemical class 0.000 description 19
- 229910052751 metal Inorganic materials 0.000 description 19
- 239000002184 metal Substances 0.000 description 19
- VLKZOEOYAKHREP-UHFFFAOYSA-N n-Hexane Chemical compound CCCCCC VLKZOEOYAKHREP-UHFFFAOYSA-N 0.000 description 15
- DKGAVHZHDRPRBM-UHFFFAOYSA-N Tert-Butanol Chemical compound CC(C)(C)O DKGAVHZHDRPRBM-UHFFFAOYSA-N 0.000 description 9
- 150000001298 alcohols Chemical class 0.000 description 9
- 150000004820 halides Chemical class 0.000 description 7
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 6
- -1 aromatic organic compounds Chemical class 0.000 description 6
- 238000006298 dechlorination reaction Methods 0.000 description 6
- 229960004592 isopropanol Drugs 0.000 description 5
- 150000003254 radicals Chemical class 0.000 description 5
- KLYCPFXDDDMZNQ-UHFFFAOYSA-N Benzyne Chemical compound C1=CC#CC=C1 KLYCPFXDDDMZNQ-UHFFFAOYSA-N 0.000 description 4
- 150000001450 anions Chemical class 0.000 description 4
- 239000003795 chemical substances by application Substances 0.000 description 4
- 239000000460 chlorine Substances 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- UTMWFJSRHLYRPY-UHFFFAOYSA-N 3,3',5,5'-tetrachlorobiphenyl Chemical compound ClC1=CC(Cl)=CC(C=2C=C(Cl)C=C(Cl)C=2)=C1 UTMWFJSRHLYRPY-UHFFFAOYSA-N 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 3
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 3
- WHXSMMKQMYFTQS-UHFFFAOYSA-N Lithium Chemical compound [Li] WHXSMMKQMYFTQS-UHFFFAOYSA-N 0.000 description 3
- 239000002202 Polyethylene glycol Substances 0.000 description 3
- 229910052784 alkaline earth metal Inorganic materials 0.000 description 3
- 238000004458 analytical method Methods 0.000 description 3
- 125000003118 aryl group Chemical group 0.000 description 3
- 125000004429 atom Chemical group 0.000 description 3
- 239000002585 base Substances 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 3
- 231100001261 hazardous Toxicity 0.000 description 3
- 239000001257 hydrogen Substances 0.000 description 3
- 229910052739 hydrogen Inorganic materials 0.000 description 3
- 229910052744 lithium Inorganic materials 0.000 description 3
- 229910000000 metal hydroxide Inorganic materials 0.000 description 3
- 150000004692 metal hydroxides Chemical class 0.000 description 3
- 229920001223 polyethylene glycol Polymers 0.000 description 3
- YLQBMQCUIZJEEH-UHFFFAOYSA-N tetrahydrofuran Natural products C=1C=COC=1 YLQBMQCUIZJEEH-UHFFFAOYSA-N 0.000 description 3
- XTHFKEDIFFGKHM-UHFFFAOYSA-N Dimethoxyethane Chemical compound COCCOC XTHFKEDIFFGKHM-UHFFFAOYSA-N 0.000 description 2
- AMQJEAYHLZJPGS-UHFFFAOYSA-N N-Pentanol Chemical compound CCCCCO AMQJEAYHLZJPGS-UHFFFAOYSA-N 0.000 description 2
- 125000002015 acyclic group Chemical group 0.000 description 2
- 230000001476 alcoholic effect Effects 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- 150000001342 alkaline earth metals Chemical class 0.000 description 2
- 150000001502 aryl halides Chemical class 0.000 description 2
- 239000012298 atmosphere Substances 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 229910052801 chlorine Inorganic materials 0.000 description 2
- 125000001309 chloro group Chemical group Cl* 0.000 description 2
- ZUOUZKKEUPVFJK-UHFFFAOYSA-N diphenyl Chemical group C1=CC=CC=C1C1=CC=CC=C1 ZUOUZKKEUPVFJK-UHFFFAOYSA-N 0.000 description 2
- 230000008034 disappearance Effects 0.000 description 2
- 125000004435 hydrogen atom Chemical group [H]* 0.000 description 2
- 150000002739 metals Chemical class 0.000 description 2
- 238000010534 nucleophilic substitution reaction Methods 0.000 description 2
- 230000027756 respiratory electron transport chain Effects 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- LAXBNTIAOJWAOP-UHFFFAOYSA-N 2-chlorobiphenyl Chemical group ClC1=CC=CC=C1C1=CC=CC=C1 LAXBNTIAOJWAOP-UHFFFAOYSA-N 0.000 description 1
- WCMSFBRREKZZFL-UHFFFAOYSA-N 3-cyclohexen-1-yl-Benzene Chemical compound C1CCCC(C=2C=CC=CC=2)=C1 WCMSFBRREKZZFL-UHFFFAOYSA-N 0.000 description 1
- 101150034533 ATIC gene Proteins 0.000 description 1
- 101100511466 Caenorhabditis elegans lon-1 gene Proteins 0.000 description 1
- 244000228957 Ferula foetida Species 0.000 description 1
- 238000005727 Friedel-Crafts reaction Methods 0.000 description 1
- IMNFDUFMRHMDMM-UHFFFAOYSA-N N-Heptane Chemical compound CCCCCCC IMNFDUFMRHMDMM-UHFFFAOYSA-N 0.000 description 1
- 244000018764 Nyssa sylvatica Species 0.000 description 1
- 235000003339 Nyssa sylvatica Nutrition 0.000 description 1
- CTQNGGLPUBDAKN-UHFFFAOYSA-N O-Xylene Chemical compound CC1=CC=CC=C1C CTQNGGLPUBDAKN-UHFFFAOYSA-N 0.000 description 1
- 241001163743 Perlodes Species 0.000 description 1
- 239000004698 Polyethylene Substances 0.000 description 1
- 150000001336 alkenes Chemical class 0.000 description 1
- 125000000217 alkyl group Chemical group 0.000 description 1
- 150000001350 alkyl halides Chemical class 0.000 description 1
- 150000001491 aromatic compounds Chemical class 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- FFBHFFJDDLITSX-UHFFFAOYSA-N benzyl N-[2-hydroxy-4-(3-oxomorpholin-4-yl)phenyl]carbamate Chemical compound OC1=C(NC(=O)OCC2=CC=CC=C2)C=CC(=C1)N1CCOCC1=O FFBHFFJDDLITSX-UHFFFAOYSA-N 0.000 description 1
- 235000010290 biphenyl Nutrition 0.000 description 1
- 239000004305 biphenyl Substances 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 150000001805 chlorine compounds Chemical class 0.000 description 1
- 229910000366 copper(II) sulfate Inorganic materials 0.000 description 1
- JZCCFEFSEZPSOG-UHFFFAOYSA-L copper(II) sulfate pentahydrate Chemical compound O.O.O.O.O.[Cu+2].[O-]S([O-])(=O)=O JZCCFEFSEZPSOG-UHFFFAOYSA-L 0.000 description 1
- 150000001907 coumarones Chemical class 0.000 description 1
- 125000004122 cyclic group Chemical group 0.000 description 1
- HHNHBFLGXIUXCM-GFCCVEGCSA-N cyclohexylbenzene Chemical compound [CH]1CCCC[C@@H]1C1=CC=CC=C1 HHNHBFLGXIUXCM-GFCCVEGCSA-N 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 238000006704 dehydrohalogenation reaction Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 150000002170 ethers Chemical class 0.000 description 1
- LYCAIKOWRPUZTN-UHFFFAOYSA-N ethylene glycol Substances OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 238000004817 gas chromatography Methods 0.000 description 1
- 238000002290 gas chromatography-mass spectrometry Methods 0.000 description 1
- 125000005843 halogen group Chemical group 0.000 description 1
- 238000004128 high performance liquid chromatography Methods 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 238000004255 ion exchange chromatography Methods 0.000 description 1
- 150000002576 ketones Chemical class 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 150000004965 peroxy acids Chemical class 0.000 description 1
- 239000002798 polar solvent Substances 0.000 description 1
- 229920000573 polyethylene Polymers 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 239000013259 porous coordination polymer Substances 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 150000005838 radical anions Chemical class 0.000 description 1
- 239000000376 reactant Substances 0.000 description 1
- 239000011541 reaction mixture Substances 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000011946 reduction process Methods 0.000 description 1
- 230000003252 repetitive effect Effects 0.000 description 1
- 159000000000 sodium salts Chemical class 0.000 description 1
- RBWSWDPRDBEWCR-RKJRWTFHSA-N sodium;(2r)-2-[(2r)-3,4-dihydroxy-5-oxo-2h-furan-2-yl]-2-hydroxyethanolate Chemical compound [Na+].[O-]C[C@@H](O)[C@H]1OC(=O)C(O)=C1O RBWSWDPRDBEWCR-RKJRWTFHSA-N 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 125000000999 tert-butyl group Chemical group [H]C([H])([H])C(*)(C([H])([H])[H])C([H])([H])[H] 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 125000000391 vinyl group Chemical group [H]C([*])=C([H])[H] 0.000 description 1
- 229920002554 vinyl polymer Polymers 0.000 description 1
- 239000008096 xylene Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C07—ORGANIC CHEMISTRY
- C07C—ACYCLIC OR CARBOCYCLIC COMPOUNDS
- C07C1/00—Preparation of hydrocarbons from one or more compounds, none of them being a hydrocarbon
- C07C1/26—Preparation of hydrocarbons from one or more compounds, none of them being a hydrocarbon starting from organic compounds containing only halogen atoms as hetero-atoms
-
- A—HUMAN NECESSITIES
- A62—LIFE-SAVING; FIRE-FIGHTING
- A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
- A62D3/00—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
- A62D3/30—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
- A62D3/34—Dehalogenation using reactive chemical agents able to degrade
-
- A—HUMAN NECESSITIES
- A62—LIFE-SAVING; FIRE-FIGHTING
- A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
- A62D2101/00—Harmful chemical substances made harmless, or less harmful, by effecting chemical change
- A62D2101/20—Organic substances
- A62D2101/22—Organic substances containing halogen
Abstract
A process for the reductive dehalogenation of halogenated aromatics. The process comprises reacting halogenated aromatics with sodium or calcium in the presence of a lower alcohol selected from the group comprising methanol, ethanol or isopropanol and mixtures thereof in order to convert the halogenated aromatics to hydrogenated aromatics. The halogenated aromatics are preferably reacted with sodium in the presence of methanol under reaction conditions whereby said sodium is in molten form. The preferred starting sodium/methanol/halogen molar ratio ranges from 30-40/15-20/1. The process is particularly useful for dechlorinating polychlorinated biphenyls found in electrical transformer oil.
Description
2~26~0~
,., ~
TITLE OF THE INVENTION
Process for the reductlve dehalogenatlon of polyhaloaromatlcs.
FIELD OF THE INVENTION
The present invention relates to a process for the dehalogenatlon of halogenated aromatlcs. Thls process lnvolves reactlng halogenated aromatlcs wlth sodlum or calclum ln the presence of a low molecular welght alcohol, preferably methanol.
lo BACKGROUND OF THE INVENTION
The dlsposal of halogenated aromatlc compounds such as polychlorinated biphe~yls ~PCBs) has, ln recent years, become a problem of growlng concern, especially because of the potentlal envlronmental hazard resultlng from the accumulatlon of large amounts of such types of compounds .
The use of sodlum as a dechlorinatlng agent for varlous types of allphatlc and aromatic chlorlde~ 1B well establlshed and sodlum stlll appears to be the metal of cholce ln current and future research in the area of PCB
treatment. The ultlmate purpose of the research done ln PCB treatment 18 obvlously to provlde effectlve dechlorination processes that can be carrled out ~afely and efficiently at costs that are as minlmal as posslble.
At the pre~ent time, one of the most reliable processes used to dechlorinate PCBs 1B a process by whlch the -2- 2Q~5~
~, compounds are heated until decomposltion occurs. The process lnvolves the use of extremely hlgh temperatures.
Among the ma~or drawback~ of this type of proce~s, one may mention the formatlon of highly toxic benzofuran compounds which appear to be even more hazardous than the PCBs them6elves.
The usefulness of the proces6 uslng llthlum or 60dium in the presence of alcohol3 and THF to dechlorlnate non-aromatic organic compounds ha6 been recognlzed in the prior art for many year~. Hence, aliphatlc halide~, which are normally qulte reactlve compounds, especlally when nucleophilic substitution or elimination of the hallde lon is de~lred, have been dehalogenated using sodium or llthium in the presence of an alcohol and thls type of reaction is well documented ln text books as well as ln other types of prlor art publications.
Flrstly, a number of ba61c organlc chemistry textbooks describe dechlorination reactlons lnvolving lithium or 60dlum in the presence of alcohol and THF. Tn the third edition of "Advanced Organic Chemlstry", Harch, at page 390, mentions that a good reduclng agent for the removal of halogen atom~ ln a non-aromatlc polyhalo compound ~including vinyl, allyllc, geminal, and even bridgehead haloqens) is llthlum or sodiu~ and t-BuOH in tetrahydrofuran. Solomons, ln the third edltion of ~Organic Chemi~try~, teaches the dehydrohalogenatlon of
,., ~
TITLE OF THE INVENTION
Process for the reductlve dehalogenatlon of polyhaloaromatlcs.
FIELD OF THE INVENTION
The present invention relates to a process for the dehalogenatlon of halogenated aromatlcs. Thls process lnvolves reactlng halogenated aromatlcs wlth sodlum or calclum ln the presence of a low molecular welght alcohol, preferably methanol.
lo BACKGROUND OF THE INVENTION
The dlsposal of halogenated aromatlc compounds such as polychlorinated biphe~yls ~PCBs) has, ln recent years, become a problem of growlng concern, especially because of the potentlal envlronmental hazard resultlng from the accumulatlon of large amounts of such types of compounds .
The use of sodlum as a dechlorinatlng agent for varlous types of allphatlc and aromatic chlorlde~ 1B well establlshed and sodlum stlll appears to be the metal of cholce ln current and future research in the area of PCB
treatment. The ultlmate purpose of the research done ln PCB treatment 18 obvlously to provlde effectlve dechlorination processes that can be carrled out ~afely and efficiently at costs that are as minlmal as posslble.
At the pre~ent time, one of the most reliable processes used to dechlorinate PCBs 1B a process by whlch the -2- 2Q~5~
~, compounds are heated until decomposltion occurs. The process lnvolves the use of extremely hlgh temperatures.
Among the ma~or drawback~ of this type of proce~s, one may mention the formatlon of highly toxic benzofuran compounds which appear to be even more hazardous than the PCBs them6elves.
The usefulness of the proces6 uslng llthlum or 60dium in the presence of alcohol3 and THF to dechlorlnate non-aromatic organic compounds ha6 been recognlzed in the prior art for many year~. Hence, aliphatlc halide~, which are normally qulte reactlve compounds, especlally when nucleophilic substitution or elimination of the hallde lon is de~lred, have been dehalogenated using sodium or llthium in the presence of an alcohol and thls type of reaction is well documented ln text books as well as ln other types of prlor art publications.
Flrstly, a number of ba61c organlc chemistry textbooks describe dechlorination reactlons lnvolving lithium or 60dlum in the presence of alcohol and THF. Tn the third edition of "Advanced Organic Chemlstry", Harch, at page 390, mentions that a good reduclng agent for the removal of halogen atom~ ln a non-aromatlc polyhalo compound ~including vinyl, allyllc, geminal, and even bridgehead haloqens) is llthlum or sodiu~ and t-BuOH in tetrahydrofuran. Solomons, ln the third edltion of ~Organic Chemi~try~, teaches the dehydrohalogenatlon of
-3- 2~J~'3 jjl~
alkyl halides using a variety of strong bases such a~ the sodium salts o~ various alcohols.
In a slmilar fashlon, Horrison and Boyd, in the fifth edltion of "Organic Chemlstry", descrlbe a reactlon for the dehalogenation of al~yl halides using potassium hydroxide and ethanol (pp. 265-266), as well as reactions for the dehydrohalogenation of vicinal dlhalldes also uslng potassium hydroxide wlth an alcohol (pp. ~20-421).
Horrlson and Boyd also mention that typically, aryl halides undergo nucleophilic substitution only with extreme difficulty. The authors state that lt 18 not posslble to use aryl halides as alkyl halldes are used, for example, in the Friedel-Craft~ reaction Ipage 1034-1035).
It therefore appears from the textbooks referred to above that nucleophlllc substitutlon of halide~ ha~
been mainly performed on allphatic halides, the same reactlon being difflcult to operate on aromatlc halides.
This findlng is also exemplified in the following publications referring to dechlorination of varlous type~
of non-aromatic compounds.
Xornel et al., ln ~PCB destruction. a novel dehalogenation reagent", Journal of Hazardous Materlal~, 12 ~1985), 161-176, descrlbe the use of polyethylene glycol and sodium hydroxlde in the dechlorlnatlon of PCBs at a temperature ranglng from 60 to 100~C. According to _4_ 2~2~ o~
the author3, alkali polyethylene glycolate complexes are malnly used because of thelr relatlve stablllty wlth regard to water and atmospherlc oxygen. The proce~s described by Kornel et al. lnvolves the prevlous S preparatlon of a dehalogenating agent which consists ln mlxlng polyethylene glycol wlth pota~slum hydroxlde and heatlng the solutlon untll potasslum hydroxlde has fully dl~olved. The reagent 18 then reacted wlth the PCB
contalning solution. Hence, the wor~ of Kornel et al.
mainly lnvolves the u~e of alcohollc sodlum hydroxlde or polyethylene ~lycol/metal hydroxide ln the dechlorinatlon of PCBs.
In U.S.P. 4,377,471, Brown et al. dlsclose a process for dechlorlnatlng PC~s that requires the use of sodlum metal and an aprotlc ion-complexlng solvent amongst whlch a certaln number of ethers such a~ ethylene glycol dimethyl ether may be selected. This process, whlch appears to be carrled out at room temperature, does not appear to refer to or suggest the use of any alcohol solvent to perform the dechlorinatlon of the PCB
contamlnated solutlon.
In U.S.P. 2,717,851 lssued to Lldov and in U.S.P. 2,676,132 to Bluestone, the authors descrlbe a proce~s through which a chlorlnated compound, such as heptachloroblcycloheptene, is treated wlth an ethanollc potasslum hydroxlde so~ution with the vlew to partlally -5- 2~2~ Os ;. ,_ dechlorinate the given compound. Thu~, the proces~
de~crlbed by Lldov leads to the removal of one chlorlne atom on the heptachloroblcycloheptene molecule.
Grlffin et al., ln "Perchloro cage compounds. I.
Structural Studles", Journal of Organlc Chemlstry, Vol.
29, 196q, pages 3192-3196, teach a proce~s for dechlorlnatlng chlorinated organlcs. The proce~ lnvolves reactlng small piece~ of metallic sodlum wlth a ~olution comprlslng the compound to be dechlorinated along wlth t-butyl alcohol in tetrahydrofuran. The reactlon appears to be performed at relatlvely low temperatures. The process de~cribed by Grlffln is aimed at removing chlorlne atoms from non-aromatic organic compounds.
Wllcox et al., in ~The Synthesis of 1,4-dlchloroblcyclo[2.2.1]heptanen, Journal of Organlc Chemlstry, Augu~t 1964, pages 2209-2211, descrlbe a proces~ by whlch a chlorinated compound 1- partly dechlorinated using lithlum and t-butyl alcohol in tetrahydrofuran.
Soloway et al., in "Reactions of Isodrln and Endrln", Journal of American Chemical Soclety 82, ~1960), pages 5377-5385, de~crlbe a method for dechlorinatlng non-aromatlc compounds ln n-amyl alcohol and xylene using ~odlum. Slmllarly, Stedman et al., ln ~The blrd-cage ketone, hexacyclo[5.4.1Ø0Ø0]dodecan-~-one, and some of its derlvatives", Journal of Canadlan Chemlstry 32, 2J2~0~
~1967), pages 35-38, teach the dechlorlnatlon of non-aro~atic chlorinated compounds using t-butyl alcohol and llthlum wlre cut lnto small piece~.
Von Doering et al., in "The addltlon of dlchlorocarbene to olefins", Journal of American Chemlcal Soclety, (1954), pages 6162-6165, descrlbe a dehalogenation process ln which metallic sodlum is used along with methanol. Methanol is added dropwise wlth rapld stlrring after sodium has been added to the solution contalning the halogenated compound to be reduced, the coDpound to be dechlorinated being a non-aromatlc compound. The methanol u~ed in this proco~s 18 wet methanol.
In the Gassman et al. reference entltled "The chemistry of 7-substltuted norborneses. The reaction of blcyclo[2.2.1]hept-2-en-7-one wlth peracid~, Journal of Canadian Chemistry, ~1964), Vol. 29, pages 160-163, the authors describe a dehalogenatlon process uslng t-butyl ln tetrahydrofurane wlth flnely chopped lithlum wlre. The process 1~ applled to non-aroDatic compounds.
Hence, the prior art processes descrlbed above mostly refer to the use of sodlum or lithlum along with various alcohols to partially dehalogenate certain types of mainly halogenated compounds. In fact, most of the reactions carried out ln these references are directed at selectlvely removlng chlorlne from certain posltlons ln _7_ ~a~
"~
cycllc and acyclic aliphatlc chlorides for the preparation of certaln novel chemlcals or for baslc research. One obvlous common factor among the~e references i8 that all the chlorinated compounds that have 80 far been treated are allphatic, cyclic or acyclic. Aliphatlc halides, as mentioned earller in the Horrlson and Boyd reference, are normally much more reactlve than aromatlc halldes, partlcularly when nucleophillc substitutlon or ellmlnatlon of the hallde lon 1~ concerned. In fact, ~ome basic organlc chemlstry textbooks seem to suggest that reactlons lnvolvlng nucleophillc substltutlon of aryl halldes are not deslrable slnce they have to be conducted under harsh experlmental condltions and since they are overall lnefficient.
Therefore, the development of sultable alternatlves to presently exlstlng processes for dehalogenatlng haloaromatics, partlcularly for decontamlnatlng methanollc extracts of PCB contamlnated 8011, methanol washlngs of PCB and Askarel containers, hlgh concentratlon levels of PCB and Askarel ln transformer 0118 and for treatlng neat PCBs and Askarel, would be hlghly de~lrable.
SUHHARY OF THE INVENTION
In accordance with the present lnvention, there 18 provided a process for the reductlve dehalogenation of halogenated aromatics. The process compri~es reactlng -8- ~ Q ~
halogenated aromatics wlth sodlum or calclum in the presence of a lower alcohol such as methanol, ethanol or isopropanol, preferably methanol, to convert the halogenated aromatlcs to hydroqenated aromatlcs.
Preferably, the process of the present lnvention 18 performed under condltions whereby sodlum 18 ln melted form. The use of a lower alcohol such as methanol ln the dehalogenation process avoids extenslve polymerlzatlon from PCBs and polyhalogenated aromatlcs and also helps to prevent decomposltlon of the oil ln whlch the substance~
to be dehalogenated may be found.
Thus, when lt 18 deslred to prevent oll decomposltlon, the use of methanol ln quantltles not exceedlng half the molar amount of sodlum was found to be deslrable. By doing 80, the oil 18 kept lntact and even lts color, a faint yellow, 1B not altered by the reactlon.
Furthermore, the ma~or products formed under these condltlons are those resultlng from the dechlorlnatlon of PCPs such as blphenyl. On the other hand, the absence of methanol ln a reactlon mlxture contalnlng oll affords a vlscous dark black gum resultlng from the extenslve decomposltlon of the oll and polymerlzatlon of the aromatlc halides. In these lnstances, ldentlflcatlon of the dechlorlnated products 18 difflcult.
When calclum 1B used as the dechlorlnatlng agent, lt 18 used ln a commerclally avallable form, that CA 02026~06 1998-12-24 is in granular form or as turnings, in a lower alcohol, preferably methanol, at room temperature. However, there are, in this case, no specific molar ratio limitations between the metal and methanol. Hence, the reaction using calcium and methanol is suitable to dechlorinate PCBs or Askarel in methanol. It may be a one step process if it is desired to reduce the PCB concentration in a given PCB solution or as a repetitive two step process if it is desired to eliminate PCBs.
Ethanol and isopropanol can be used as suitable alcohols but for economical and performance considerations, methanol is the preferred alcohol. Also preferred is the use of a nitrogen atmosphere when performing the reaction with sodium.
The process of the present invention can therefore be employed to dehalogenate various types of PCBs or other polyhalogenated aromatics at various concentrations such as those found in transformer oils.
Some prior art literature refers to the use of alcoholic metal hydroxides such as MaOH/ROH in dehalogenation reactions. The present invention refers to the use of alkali or alkaline earth metal in alcohols (e.g. Na-ROH). Hence, the process of the present invention is to be distinguished from other processes that require the use of alcoholic sodium hydroxi~e or polyethylene glycol/metal hydroxide. Basically, each ~3~ 0~
reactlon proceeds with different chemlstry ln terms of mechanlsms and products.
The pre~ent invention will be more readily lllustrated by referring to the following de~crlption.
DETAILED DESCRIPTION OF THB INVENTION
The present lnventlon relates to a process useful to dehalogenate polyhaloaromatic compounds and partlcularly to dechlorlnate polychlorlnated blphenyls present ln transformer oll. It lnvolves reacting halogenated aromatlcs in a lower alcohol such as methanol, ethanol or isopropanol with elther sodlum or calclum, preferably but not necessarlly under a nitrogen atmosphere.
COHPOUNDS TO BE DEHALOGENATED
The process of the present lnventlon may be used to dehalogenate a wide variety of halogenated aromatlcs at various concentratlons. The proce~s is to be employed mainly ln the dechlorlnatlon of polychlorinated blphenyls IPC~s) although lt 18 to be understood that lt could be used ln the reductlve dehalogenatlon of other types of aromatlc compounds.
HETALS
Two types of metal are malnly contemplated for use ln the proces~ of the present invention. One metal, sodlum, i~ an alkall metal and one metal, calclum, is an o ~
alkaline earth metal. The form in which the metals are used may vary dependlng on the nature of the metal ltself.
In the case of sodlum, if dehalogenatlon 18 conducted above the melting polnt of this metal, that 18 above 97~C, the form of the metal is not crltlcal since sodlum will be ln a llquid, active form. At room temperature however, sodlum must first be brought to lts reactlve sand form. It is to be noted that dehalogenatlon at room temperature normally requlres longer reactlon tlmes and is lesg efflclent than dehalogenatlon performed at temperatures above the melting point of sodlum.
Tn the case of calcium, the temperature at which the reaction 18 performed and the form of the metal are not crucial factors ln the reaction. In fact, calclum may be used ln granular form o~ as turnings wlth methanol as the solvent.
ALCOHOLS
The alcohols that may be used ln the context of the present invention are malnly lower alcohols such as methanol, ethanol and lsopropanol. Hethanol has been found to be the most suitable alcohol which could be used both ln terms of cost and efficiency. However, ethanol and isopropanol are to be vlewed as possible alternatives.
It i8 mostly preferred to use sodlum and methanol as reactants in the dehalogenatlon process of the present lnventlon. The starting sodlum/methanol~halogen .,.,,_ ~ ~ 2 ~ ~ 0 ~
molar ratio may be in the following range- 30-40-15-20-1.
Further development has shown that a 2~ ratlo is the most practical ratlo slnce lt requires less sodlum and affords evenly effectlve reaction condltlons.
PROCESS
Reactlon mechanl~m It i8 belleved that the dehalogenatlon of the present lnventlon can proceed through two posslble mechanlsms. Thu~, the reactlon could pos~lbly proceed through elther an electron transfer/hydrogen abstractlon mechanlsm that invoIves the formatlon of radical anlons and radical~ or through an abstractlon/ellmlnation mechanlsm that lnvolves the formatlon of benzynes as reactlve lntermediates.
In the process of the present inventlon, slmllarly to other proces~es that require the use of metals such as ~odlum to dehalogenate polyhalogenated aromatlcs such as PC~s, the prlnclpal PCB dechlorlnatlon step involves an electron transfer process. As shown in Scheme 1 below, the metal tran~fers an electron to the aromatic halide, ArCl, to form a radlcal anlon (I) whlch then loo~es a chloride lon to yield radical (II).
Subsequently, radical (IIJ abstracts hydrogen to yield the de~lred dechlorlnated product.
~ ~ a V S
~ M e ~ A~ _ a Ar ~ Ar a~ (2) A~ ~ MdOH ~ A~ - H
Sch~me 1 In addition to the general mechanism shown above that describe~ the involvement of radicals and radical anions in the dehalogenation process, it appears that other lntermediates, such as benzyne, may also be involved.
As shown in Scheme II below, the strongly basic methoxlde anion, MeO , generated ln BitU from the reactlon of methanol with the metal, may abstract hydrogen from one of the biphenyl rings in a PCB molecule (III) to produce anion (IV). Dechlorlnatlon of ~IV) would then proceed by e11minatlng the chloride anion resulting ln the formatlon of benzyne lntermedlate ~V). The formation of such lntermedlate 1B made po~slble by the pre~ence of several ~_ 2 Q 2 ~
negative chlorine atom~ on the aromatlc rlngs of PCB8.
These atoms, through their negative lnductlve effects, render the aromatic hydrogens ~llghtly acldlc thus favorlng reaction wlth the strongly baslc methoxlde lon.
gubsequent ellmination of the chlorlde lon from (IV) glves the benzyne lntermedlate (V). Repetltlon of thls abstraction/elimlnatlon process would thus lead to another effectlve route for PC~ dechlorlnation.
2 MdDH ~ 2 M ~ 2MbO M + H2 a a .
abso~cd~n a~) ~ + McOH
III IV
Cl - a , Cl~Cl ~ ~ dechlorinated din~ination products Scheme 2: i -..
It ls to be noted that thls second mechanlsm 18 not fully understood and that lts validity wlth regard to the present system iB uncertain. A ve~y strong base 8uch -15- ~ ~ 2 ~ ~ O ~
as an amlde anion (NH2) 18 normally requlred to generate benzyne from aromatlc halldes. However, the presence of several chlorine atoms ~as election wlth drawing groups) or PCBs may render some hydrogens on the ring acldic enough to react wlth the weaker base methoxlde anlon to glve (IV).
a) When uslnq sodium If sodium ls to be employed as the prlnclpal actlve component in the process, a sultable vehicle ~uch as transformer oll is first used to melt the sodlum at a temperature of about 100~C ln order to transfer it into one of lts most reactlve forms; As mentioned earlier, the sodium particle size is not crltical.
Once sodium has been brought to its melted form ln the transformer oil, the dechlorlnatlon process 18 carried out at approxlmately the same temperature as the melting polnt of ~odium, thus allowlng sodium to stay in lts reactive form. One of the alcohols referred to above 18 used to stop polymerization from taking place and to stop the decompositlon of the oll whlch can be recycled and used again. The alcohol that is preferred 18 methanol. The use of an lnert gas is lmportant, for safety consideratlons. However, the reactlon proceeds ln the absence of lnert atmosphere.
In the absence of alcohol, particularly methanol, but under otherwise identlcal conditions, ~ ~ ~ 2 ~
dehalogenatlon takes place wlth a smaller amount of sodlum, that ls approximately half the amount requlred when an alcohol is present. However, under these condltion~, dehalogenatlon i8 often accompanled wlth oll destructlon and exten~lve polymerlzatlon, partlcularly from the blphenyls present ln the solutlon.
It 1~ lmportant to note that sodlum 18 the preferred metal to be used. When slmllar dehalogenatlon 18 attempted wlth llthlum metal in~tead of sodlum under otherwlse identlcal condltlons, the halogenated aromatlcs remaln almost lntact wlth very llttle dehalogenatlon taklng place. If THF ls added to a PCB mlxture contalned in oll and sub~tantial heat 18 applled to the proces~, that 1~ a temperature over 170~C for a perlod exceedlng 17 hours, more than 25% of the original concentratlon of the halogenated aromatlcs remaln lntact.
In fact, lt ls the presence of oll that apparently reduces the reactlvlty of llthlum. If no oll 18 present ln the PCB mlxture, Ll can be used to dechlorlnate PCBs ln a sultable organlc solvent such as THF. However, the use of THF ls not recoDmended for commercial use because of the followlng factorsl it iB
corroslve, hazardous, expenslve and unde~lrable because of ..
the ~lgnificant side reactlon that takes place between lithium and THF. In fact, ln some lnstances, lithlum -17- 2Q2~
placed ln contact with a solutlon containing PCBs, THF and oll will react wlth THF but not with the PCBs.
Thus, numerous advantages result from the use of a lower alcohol ~uch as methanol in a dehalogenation process. Hence, methanol apparently particlpates in the reduction process. It also appears to prevent oil decomposition and leads to a clean formation of blphenyl products while reducing the possibility of polymer formatlon. Also, the low cost of methanol renders the process readlly feaslble commercially.
The reaction descrlbed above can proceed uslng various conditions. Firstly, different temperatures may be used. The reaction has been found to proceed at room temperature but the speed of the reaction is increased lf the temperature is above the meltlng polnt of sodium.
Also, the reaction time may range between 1 and 24 hours.
Furthermore, different concentrations of halogenated aromatics can be treated under the conditions set forth above. For example, concentrations of over 100,000 ppm of PC~s can be easily treated using the method of the present invention. It is to be understood, however, that concentratlons below the 100,000 ppm mark can also be treated.
The process is partlcularly useful to treat methanollc extracts of PCB contamlnated soil, methanol _ 2~26~
wa~hings of PCB and A~karel containers, PCB and As~arel in transformer oll a~ well as neat Askarel.
b) When u~lnq calclum When it i~ desired to use calcium in the dehalogenation proce~ of the pre~ent inventlon, calcium is to be added to a mixture containlng the halogenated aromatics in a lower alcohol ~uch as methanol at a temperature close to room temperature. Other types of alcohols such as ethanol and lsopropanol could also be used to perform the dehalogenatlon uslng calclum, provlded that methanol i~ present.
The following examples are provided to illu~trate rather than llmlt the scope of the present invention.
Rxaaple 1 Reductlve dechlorlnatlon of Askarel uslng sodium ln methanol.
2.01 g of sodium were heated in 50 ml of transformer mineral oil at a temperature of 105~C. After having melted sodium, the mixture wa~ rapldly stlrred to transfer sodium into a very reactlve ~and form. The oil was then carefully cooled down 80 that sodlum could stay in lts reactlve sand form. 1.040 g of Askarel lArochlor 1260 (40%) in trlchlorobenzenes~ ln 1.410 g of methanol was added to the above mlxture under nltrogen and the -19- 2~2~06 reactlon mixture was heated ~ust above the meltlng polnt of sodlum for 30 minutes. Under these conditlons, sodlum stayed as a flne powder ln a very reactlve for~. The mlxture was then cooled down to room temperature 80 that the reactlon vessel could be agltated to get the chlorinated aromatlcs from the wall of the flask into the reacting area. The mlxture, plnk ln color, was heated for another 30 minutes and a yellow color was obtalned. At thls stage, a sample was withdrawn from the reactlon mlxture and analyzed by GC/ECD. After quenchlng wlth water, clean up wlth acld and extraction with hexane, the GC/ECD showed complete dlsappearance of the 20,800 ppm Askarel that was originally present in the oil. An external standard of 1 ppm Arochlor 1260 was used to monitor the dechlorination proce~s. GC/ECD analysis showed no pre~ence of Askarel after treatment.
Furthermore, chloride analysis by HPLC ion chromatography showed complete recovery of the organo-chlorine ln Askarel as sodium chlorlde.
Example 2 When sodlum was replaced by llthlum, under condltions otherwise simllar to those of Example 1, no reactlon was observed. It 18 only when the reaction mlxture was heated above 150~C that only about 70~ of the PCBs ln Askarel were degraded. The presence of the -20- 2 ~ 2 ~ 6 ,.~
transformer oll seems to deactlvate lithium whlch otherwlse 18 known to dehalogenate aromatlc halldes ln polar solvent~.
Thus, when mlxing llthium (1.128 g, 0.16 mole) and A~karel 11.6718 g) in tran~former mineral oll (50 ml) contalnlng methanol (2.58 g~ at room temperature, no reaction was observed. When the mixture was heated for 2 hours at 105~C, no reactlon was observed. The mlxture was then heated between 150 and 17S~C for 2 hours. It is after this drastlc heatlng that only about 70S of the Arochlor 1260 in Askarel dlsappeared. Thls example demonstrate~ the necesslty to use sodlum as an alkall metal in the process of the pre8ent lnventlon.
ExaDple 3 Dechlorlnatlon of Arochlor 1248 uslng calcium in methanol.
To 0.23 g of Arochlor 1248 in 100 ml of methanol, 2.0 g of calcium were added under a nltrogen atmosphere at room temperature. The mixture was then stirred and an immedlate reactlon took place. After the disappearance of calcium, that is approxlmately 40 mlnutes, a 200 ul sample was taken out, neutralized with 0.5 ml of water and then extracted with 1 ml of hexane.
GC analysis indicated dlsappearance of about 50% of the PCBs. The reaction mlxture was then sub~ected to a second treatment outllned as follows.
-21- 2 ~ ~ ~ S db Unreacted PCBs and thelr organic produats were extracted into 2 X 100 ml of hexane and hexane was subsequently evaporated on a water pump at room temperature to avoid 108~ of PCBs. The re~idual untreated PCBs were dis~olved in 100 ml of methanol and treated wlth 2.01 g of calcium for 1 hour at room temperature. The reaction mixture wa~ worked up as described above. GC and GC/MS analysls showed dl~appearance of more than 95% of the PCBs wherea~ blphenyl ~m/e 154), mono-chlorobiphenyl 10(m/e 188) and dl-chlorobiphenyl (m~e 122) formed in almost equal amounts.
Exa-ple 4 Dechlorination of Askarel.
15The condltlons clted ln ~xample 3 for the dechlorlnation of Arochlor 1248 were repeated for the dechlorinatlon of Askarel. To a mlxture of Askarel (1.5990 gl in methanol (100 ml), 2.04 g of calcium were added and the mixture was stirred at room temperature untll calcium metal disappeared. Hexane extractlon was then performed to prepare unreacted Askarel for the second treatment. The second treatment also lnvolved the use of 2.04 g of calcium and 100 ml of methanol. After the disappearance of calclum GC/Mass analysis lndlcated that close to 99% of Askarel had dlsappeared. The products formed were mainly blphenyl and partially hydrogenated CA 02026~06 1998-12-24 Mono- and di-chlorobiphenyls, traces of cyclohexylbenzene and cyclohexenylbenzene are also formed.
Example 5 When the experimental conditions of Examples 3 and 4 were used replacing methanol with iso-propanol and terbutanol or THF, no appreciable dechlorination was observed.
alkyl halides using a variety of strong bases such a~ the sodium salts o~ various alcohols.
In a slmilar fashlon, Horrison and Boyd, in the fifth edltion of "Organic Chemlstry", descrlbe a reactlon for the dehalogenation of al~yl halides using potassium hydroxide and ethanol (pp. 265-266), as well as reactions for the dehydrohalogenation of vicinal dlhalldes also uslng potassium hydroxide wlth an alcohol (pp. ~20-421).
Horrlson and Boyd also mention that typically, aryl halides undergo nucleophilic substitution only with extreme difficulty. The authors state that lt 18 not posslble to use aryl halides as alkyl halldes are used, for example, in the Friedel-Craft~ reaction Ipage 1034-1035).
It therefore appears from the textbooks referred to above that nucleophlllc substitutlon of halide~ ha~
been mainly performed on allphatic halides, the same reactlon being difflcult to operate on aromatlc halides.
This findlng is also exemplified in the following publications referring to dechlorination of varlous type~
of non-aromatic compounds.
Xornel et al., ln ~PCB destruction. a novel dehalogenation reagent", Journal of Hazardous Materlal~, 12 ~1985), 161-176, descrlbe the use of polyethylene glycol and sodium hydroxlde in the dechlorlnatlon of PCBs at a temperature ranglng from 60 to 100~C. According to _4_ 2~2~ o~
the author3, alkali polyethylene glycolate complexes are malnly used because of thelr relatlve stablllty wlth regard to water and atmospherlc oxygen. The proce~s described by Kornel et al. lnvolves the prevlous S preparatlon of a dehalogenating agent which consists ln mlxlng polyethylene glycol wlth pota~slum hydroxlde and heatlng the solutlon untll potasslum hydroxlde has fully dl~olved. The reagent 18 then reacted wlth the PCB
contalning solution. Hence, the wor~ of Kornel et al.
mainly lnvolves the u~e of alcohollc sodlum hydroxlde or polyethylene ~lycol/metal hydroxide ln the dechlorinatlon of PCBs.
In U.S.P. 4,377,471, Brown et al. dlsclose a process for dechlorlnatlng PC~s that requires the use of sodlum metal and an aprotlc ion-complexlng solvent amongst whlch a certaln number of ethers such a~ ethylene glycol dimethyl ether may be selected. This process, whlch appears to be carrled out at room temperature, does not appear to refer to or suggest the use of any alcohol solvent to perform the dechlorinatlon of the PCB
contamlnated solutlon.
In U.S.P. 2,717,851 lssued to Lldov and in U.S.P. 2,676,132 to Bluestone, the authors descrlbe a proce~s through which a chlorlnated compound, such as heptachloroblcycloheptene, is treated wlth an ethanollc potasslum hydroxlde so~ution with the vlew to partlally -5- 2~2~ Os ;. ,_ dechlorinate the given compound. Thu~, the proces~
de~crlbed by Lldov leads to the removal of one chlorlne atom on the heptachloroblcycloheptene molecule.
Grlffin et al., ln "Perchloro cage compounds. I.
Structural Studles", Journal of Organlc Chemlstry, Vol.
29, 196q, pages 3192-3196, teach a proce~s for dechlorlnatlng chlorinated organlcs. The proce~ lnvolves reactlng small piece~ of metallic sodlum wlth a ~olution comprlslng the compound to be dechlorinated along wlth t-butyl alcohol in tetrahydrofuran. The reactlon appears to be performed at relatlvely low temperatures. The process de~cribed by Grlffln is aimed at removing chlorlne atoms from non-aromatic organic compounds.
Wllcox et al., in ~The Synthesis of 1,4-dlchloroblcyclo[2.2.1]heptanen, Journal of Organlc Chemlstry, Augu~t 1964, pages 2209-2211, descrlbe a proces~ by whlch a chlorinated compound 1- partly dechlorinated using lithlum and t-butyl alcohol in tetrahydrofuran.
Soloway et al., in "Reactions of Isodrln and Endrln", Journal of American Chemical Soclety 82, ~1960), pages 5377-5385, de~crlbe a method for dechlorinatlng non-aromatlc compounds ln n-amyl alcohol and xylene using ~odlum. Slmllarly, Stedman et al., ln ~The blrd-cage ketone, hexacyclo[5.4.1Ø0Ø0]dodecan-~-one, and some of its derlvatives", Journal of Canadlan Chemlstry 32, 2J2~0~
~1967), pages 35-38, teach the dechlorlnatlon of non-aro~atic chlorinated compounds using t-butyl alcohol and llthlum wlre cut lnto small piece~.
Von Doering et al., in "The addltlon of dlchlorocarbene to olefins", Journal of American Chemlcal Soclety, (1954), pages 6162-6165, descrlbe a dehalogenation process ln which metallic sodlum is used along with methanol. Methanol is added dropwise wlth rapld stlrring after sodium has been added to the solution contalning the halogenated compound to be reduced, the coDpound to be dechlorinated being a non-aromatlc compound. The methanol u~ed in this proco~s 18 wet methanol.
In the Gassman et al. reference entltled "The chemistry of 7-substltuted norborneses. The reaction of blcyclo[2.2.1]hept-2-en-7-one wlth peracid~, Journal of Canadian Chemistry, ~1964), Vol. 29, pages 160-163, the authors describe a dehalogenatlon process uslng t-butyl ln tetrahydrofurane wlth flnely chopped lithlum wlre. The process 1~ applled to non-aroDatic compounds.
Hence, the prior art processes descrlbed above mostly refer to the use of sodlum or lithlum along with various alcohols to partially dehalogenate certain types of mainly halogenated compounds. In fact, most of the reactions carried out ln these references are directed at selectlvely removlng chlorlne from certain posltlons ln _7_ ~a~
"~
cycllc and acyclic aliphatlc chlorides for the preparation of certaln novel chemlcals or for baslc research. One obvlous common factor among the~e references i8 that all the chlorinated compounds that have 80 far been treated are allphatic, cyclic or acyclic. Aliphatlc halides, as mentioned earller in the Horrlson and Boyd reference, are normally much more reactlve than aromatlc halldes, partlcularly when nucleophillc substitutlon or ellmlnatlon of the hallde lon 1~ concerned. In fact, ~ome basic organlc chemlstry textbooks seem to suggest that reactlons lnvolvlng nucleophillc substltutlon of aryl halldes are not deslrable slnce they have to be conducted under harsh experlmental condltions and since they are overall lnefficient.
Therefore, the development of sultable alternatlves to presently exlstlng processes for dehalogenatlng haloaromatics, partlcularly for decontamlnatlng methanollc extracts of PCB contamlnated 8011, methanol washlngs of PCB and Askarel containers, hlgh concentratlon levels of PCB and Askarel ln transformer 0118 and for treatlng neat PCBs and Askarel, would be hlghly de~lrable.
SUHHARY OF THE INVENTION
In accordance with the present lnvention, there 18 provided a process for the reductlve dehalogenation of halogenated aromatics. The process compri~es reactlng -8- ~ Q ~
halogenated aromatics wlth sodlum or calclum in the presence of a lower alcohol such as methanol, ethanol or isopropanol, preferably methanol, to convert the halogenated aromatlcs to hydroqenated aromatlcs.
Preferably, the process of the present lnvention 18 performed under condltions whereby sodlum 18 ln melted form. The use of a lower alcohol such as methanol ln the dehalogenation process avoids extenslve polymerlzatlon from PCBs and polyhalogenated aromatlcs and also helps to prevent decomposltlon of the oil ln whlch the substance~
to be dehalogenated may be found.
Thus, when lt 18 deslred to prevent oll decomposltlon, the use of methanol ln quantltles not exceedlng half the molar amount of sodlum was found to be deslrable. By doing 80, the oil 18 kept lntact and even lts color, a faint yellow, 1B not altered by the reactlon.
Furthermore, the ma~or products formed under these condltlons are those resultlng from the dechlorlnatlon of PCPs such as blphenyl. On the other hand, the absence of methanol ln a reactlon mlxture contalnlng oll affords a vlscous dark black gum resultlng from the extenslve decomposltlon of the oll and polymerlzatlon of the aromatlc halides. In these lnstances, ldentlflcatlon of the dechlorlnated products 18 difflcult.
When calclum 1B used as the dechlorlnatlng agent, lt 18 used ln a commerclally avallable form, that CA 02026~06 1998-12-24 is in granular form or as turnings, in a lower alcohol, preferably methanol, at room temperature. However, there are, in this case, no specific molar ratio limitations between the metal and methanol. Hence, the reaction using calcium and methanol is suitable to dechlorinate PCBs or Askarel in methanol. It may be a one step process if it is desired to reduce the PCB concentration in a given PCB solution or as a repetitive two step process if it is desired to eliminate PCBs.
Ethanol and isopropanol can be used as suitable alcohols but for economical and performance considerations, methanol is the preferred alcohol. Also preferred is the use of a nitrogen atmosphere when performing the reaction with sodium.
The process of the present invention can therefore be employed to dehalogenate various types of PCBs or other polyhalogenated aromatics at various concentrations such as those found in transformer oils.
Some prior art literature refers to the use of alcoholic metal hydroxides such as MaOH/ROH in dehalogenation reactions. The present invention refers to the use of alkali or alkaline earth metal in alcohols (e.g. Na-ROH). Hence, the process of the present invention is to be distinguished from other processes that require the use of alcoholic sodium hydroxi~e or polyethylene glycol/metal hydroxide. Basically, each ~3~ 0~
reactlon proceeds with different chemlstry ln terms of mechanlsms and products.
The pre~ent invention will be more readily lllustrated by referring to the following de~crlption.
DETAILED DESCRIPTION OF THB INVENTION
The present lnventlon relates to a process useful to dehalogenate polyhaloaromatic compounds and partlcularly to dechlorlnate polychlorlnated blphenyls present ln transformer oll. It lnvolves reacting halogenated aromatlcs in a lower alcohol such as methanol, ethanol or isopropanol with elther sodlum or calclum, preferably but not necessarlly under a nitrogen atmosphere.
COHPOUNDS TO BE DEHALOGENATED
The process of the present lnventlon may be used to dehalogenate a wide variety of halogenated aromatlcs at various concentratlons. The proce~s is to be employed mainly ln the dechlorlnatlon of polychlorinated blphenyls IPC~s) although lt 18 to be understood that lt could be used ln the reductlve dehalogenatlon of other types of aromatlc compounds.
HETALS
Two types of metal are malnly contemplated for use ln the proces~ of the present invention. One metal, sodlum, i~ an alkall metal and one metal, calclum, is an o ~
alkaline earth metal. The form in which the metals are used may vary dependlng on the nature of the metal ltself.
In the case of sodlum, if dehalogenatlon 18 conducted above the melting polnt of this metal, that 18 above 97~C, the form of the metal is not crltlcal since sodlum will be ln a llquid, active form. At room temperature however, sodlum must first be brought to lts reactlve sand form. It is to be noted that dehalogenatlon at room temperature normally requlres longer reactlon tlmes and is lesg efflclent than dehalogenatlon performed at temperatures above the melting point of sodlum.
Tn the case of calcium, the temperature at which the reaction 18 performed and the form of the metal are not crucial factors ln the reaction. In fact, calclum may be used ln granular form o~ as turnings wlth methanol as the solvent.
ALCOHOLS
The alcohols that may be used ln the context of the present invention are malnly lower alcohols such as methanol, ethanol and lsopropanol. Hethanol has been found to be the most suitable alcohol which could be used both ln terms of cost and efficiency. However, ethanol and isopropanol are to be vlewed as possible alternatives.
It i8 mostly preferred to use sodlum and methanol as reactants in the dehalogenatlon process of the present lnventlon. The starting sodlum/methanol~halogen .,.,,_ ~ ~ 2 ~ ~ 0 ~
molar ratio may be in the following range- 30-40-15-20-1.
Further development has shown that a 2~ ratlo is the most practical ratlo slnce lt requires less sodlum and affords evenly effectlve reaction condltlons.
PROCESS
Reactlon mechanl~m It i8 belleved that the dehalogenatlon of the present lnventlon can proceed through two posslble mechanlsms. Thu~, the reactlon could pos~lbly proceed through elther an electron transfer/hydrogen abstractlon mechanlsm that invoIves the formatlon of radical anlons and radical~ or through an abstractlon/ellmlnation mechanlsm that lnvolves the formatlon of benzynes as reactlve lntermediates.
In the process of the present inventlon, slmllarly to other proces~es that require the use of metals such as ~odlum to dehalogenate polyhalogenated aromatlcs such as PC~s, the prlnclpal PCB dechlorlnatlon step involves an electron transfer process. As shown in Scheme 1 below, the metal tran~fers an electron to the aromatic halide, ArCl, to form a radlcal anlon (I) whlch then loo~es a chloride lon to yield radical (II).
Subsequently, radical (IIJ abstracts hydrogen to yield the de~lred dechlorlnated product.
~ ~ a V S
~ M e ~ A~ _ a Ar ~ Ar a~ (2) A~ ~ MdOH ~ A~ - H
Sch~me 1 In addition to the general mechanism shown above that describe~ the involvement of radicals and radical anions in the dehalogenation process, it appears that other lntermediates, such as benzyne, may also be involved.
As shown in Scheme II below, the strongly basic methoxlde anion, MeO , generated ln BitU from the reactlon of methanol with the metal, may abstract hydrogen from one of the biphenyl rings in a PCB molecule (III) to produce anion (IV). Dechlorlnatlon of ~IV) would then proceed by e11minatlng the chloride anion resulting ln the formatlon of benzyne lntermedlate ~V). The formation of such lntermedlate 1B made po~slble by the pre~ence of several ~_ 2 Q 2 ~
negative chlorine atom~ on the aromatlc rlngs of PCB8.
These atoms, through their negative lnductlve effects, render the aromatic hydrogens ~llghtly acldlc thus favorlng reaction wlth the strongly baslc methoxlde lon.
gubsequent ellmination of the chlorlde lon from (IV) glves the benzyne lntermedlate (V). Repetltlon of thls abstraction/elimlnatlon process would thus lead to another effectlve route for PC~ dechlorlnation.
2 MdDH ~ 2 M ~ 2MbO M + H2 a a .
abso~cd~n a~) ~ + McOH
III IV
Cl - a , Cl~Cl ~ ~ dechlorinated din~ination products Scheme 2: i -..
It ls to be noted that thls second mechanlsm 18 not fully understood and that lts validity wlth regard to the present system iB uncertain. A ve~y strong base 8uch -15- ~ ~ 2 ~ ~ O ~
as an amlde anion (NH2) 18 normally requlred to generate benzyne from aromatlc halldes. However, the presence of several chlorine atoms ~as election wlth drawing groups) or PCBs may render some hydrogens on the ring acldic enough to react wlth the weaker base methoxlde anlon to glve (IV).
a) When uslnq sodium If sodium ls to be employed as the prlnclpal actlve component in the process, a sultable vehicle ~uch as transformer oll is first used to melt the sodlum at a temperature of about 100~C ln order to transfer it into one of lts most reactlve forms; As mentioned earlier, the sodium particle size is not crltical.
Once sodium has been brought to its melted form ln the transformer oil, the dechlorlnatlon process 18 carried out at approxlmately the same temperature as the melting polnt of ~odium, thus allowlng sodium to stay in lts reactive form. One of the alcohols referred to above 18 used to stop polymerization from taking place and to stop the decompositlon of the oll whlch can be recycled and used again. The alcohol that is preferred 18 methanol. The use of an lnert gas is lmportant, for safety consideratlons. However, the reactlon proceeds ln the absence of lnert atmosphere.
In the absence of alcohol, particularly methanol, but under otherwise identlcal conditions, ~ ~ ~ 2 ~
dehalogenatlon takes place wlth a smaller amount of sodlum, that ls approximately half the amount requlred when an alcohol is present. However, under these condltion~, dehalogenatlon i8 often accompanled wlth oll destructlon and exten~lve polymerlzatlon, partlcularly from the blphenyls present ln the solutlon.
It 1~ lmportant to note that sodlum 18 the preferred metal to be used. When slmllar dehalogenatlon 18 attempted wlth llthlum metal in~tead of sodlum under otherwlse identlcal condltlons, the halogenated aromatlcs remaln almost lntact wlth very llttle dehalogenatlon taklng place. If THF ls added to a PCB mlxture contalned in oll and sub~tantial heat 18 applled to the proces~, that 1~ a temperature over 170~C for a perlod exceedlng 17 hours, more than 25% of the original concentratlon of the halogenated aromatlcs remaln lntact.
In fact, lt ls the presence of oll that apparently reduces the reactlvlty of llthlum. If no oll 18 present ln the PCB mlxture, Ll can be used to dechlorlnate PCBs ln a sultable organlc solvent such as THF. However, the use of THF ls not recoDmended for commercial use because of the followlng factorsl it iB
corroslve, hazardous, expenslve and unde~lrable because of ..
the ~lgnificant side reactlon that takes place between lithium and THF. In fact, ln some lnstances, lithlum -17- 2Q2~
placed ln contact with a solutlon containing PCBs, THF and oll will react wlth THF but not with the PCBs.
Thus, numerous advantages result from the use of a lower alcohol ~uch as methanol in a dehalogenation process. Hence, methanol apparently particlpates in the reduction process. It also appears to prevent oil decomposition and leads to a clean formation of blphenyl products while reducing the possibility of polymer formatlon. Also, the low cost of methanol renders the process readlly feaslble commercially.
The reaction descrlbed above can proceed uslng various conditions. Firstly, different temperatures may be used. The reaction has been found to proceed at room temperature but the speed of the reaction is increased lf the temperature is above the meltlng polnt of sodium.
Also, the reaction time may range between 1 and 24 hours.
Furthermore, different concentrations of halogenated aromatics can be treated under the conditions set forth above. For example, concentrations of over 100,000 ppm of PC~s can be easily treated using the method of the present invention. It is to be understood, however, that concentratlons below the 100,000 ppm mark can also be treated.
The process is partlcularly useful to treat methanollc extracts of PCB contamlnated soil, methanol _ 2~26~
wa~hings of PCB and A~karel containers, PCB and As~arel in transformer oll a~ well as neat Askarel.
b) When u~lnq calclum When it i~ desired to use calcium in the dehalogenation proce~ of the pre~ent inventlon, calcium is to be added to a mixture containlng the halogenated aromatics in a lower alcohol ~uch as methanol at a temperature close to room temperature. Other types of alcohols such as ethanol and lsopropanol could also be used to perform the dehalogenatlon uslng calclum, provlded that methanol i~ present.
The following examples are provided to illu~trate rather than llmlt the scope of the present invention.
Rxaaple 1 Reductlve dechlorlnatlon of Askarel uslng sodium ln methanol.
2.01 g of sodium were heated in 50 ml of transformer mineral oil at a temperature of 105~C. After having melted sodium, the mixture wa~ rapldly stlrred to transfer sodium into a very reactlve ~and form. The oil was then carefully cooled down 80 that sodlum could stay in lts reactlve sand form. 1.040 g of Askarel lArochlor 1260 (40%) in trlchlorobenzenes~ ln 1.410 g of methanol was added to the above mlxture under nltrogen and the -19- 2~2~06 reactlon mixture was heated ~ust above the meltlng polnt of sodlum for 30 minutes. Under these conditlons, sodlum stayed as a flne powder ln a very reactlve for~. The mlxture was then cooled down to room temperature 80 that the reactlon vessel could be agltated to get the chlorinated aromatlcs from the wall of the flask into the reacting area. The mlxture, plnk ln color, was heated for another 30 minutes and a yellow color was obtalned. At thls stage, a sample was withdrawn from the reactlon mlxture and analyzed by GC/ECD. After quenchlng wlth water, clean up wlth acld and extraction with hexane, the GC/ECD showed complete dlsappearance of the 20,800 ppm Askarel that was originally present in the oil. An external standard of 1 ppm Arochlor 1260 was used to monitor the dechlorination proce~s. GC/ECD analysis showed no pre~ence of Askarel after treatment.
Furthermore, chloride analysis by HPLC ion chromatography showed complete recovery of the organo-chlorine ln Askarel as sodium chlorlde.
Example 2 When sodlum was replaced by llthlum, under condltions otherwise simllar to those of Example 1, no reactlon was observed. It 18 only when the reaction mlxture was heated above 150~C that only about 70~ of the PCBs ln Askarel were degraded. The presence of the -20- 2 ~ 2 ~ 6 ,.~
transformer oll seems to deactlvate lithium whlch otherwlse 18 known to dehalogenate aromatlc halldes ln polar solvent~.
Thus, when mlxing llthium (1.128 g, 0.16 mole) and A~karel 11.6718 g) in tran~former mineral oll (50 ml) contalnlng methanol (2.58 g~ at room temperature, no reaction was observed. When the mixture was heated for 2 hours at 105~C, no reactlon was observed. The mlxture was then heated between 150 and 17S~C for 2 hours. It is after this drastlc heatlng that only about 70S of the Arochlor 1260 in Askarel dlsappeared. Thls example demonstrate~ the necesslty to use sodlum as an alkall metal in the process of the pre8ent lnventlon.
ExaDple 3 Dechlorlnatlon of Arochlor 1248 uslng calcium in methanol.
To 0.23 g of Arochlor 1248 in 100 ml of methanol, 2.0 g of calcium were added under a nltrogen atmosphere at room temperature. The mixture was then stirred and an immedlate reactlon took place. After the disappearance of calcium, that is approxlmately 40 mlnutes, a 200 ul sample was taken out, neutralized with 0.5 ml of water and then extracted with 1 ml of hexane.
GC analysis indicated dlsappearance of about 50% of the PCBs. The reaction mlxture was then sub~ected to a second treatment outllned as follows.
-21- 2 ~ ~ ~ S db Unreacted PCBs and thelr organic produats were extracted into 2 X 100 ml of hexane and hexane was subsequently evaporated on a water pump at room temperature to avoid 108~ of PCBs. The re~idual untreated PCBs were dis~olved in 100 ml of methanol and treated wlth 2.01 g of calcium for 1 hour at room temperature. The reaction mixture wa~ worked up as described above. GC and GC/MS analysls showed dl~appearance of more than 95% of the PCBs wherea~ blphenyl ~m/e 154), mono-chlorobiphenyl 10(m/e 188) and dl-chlorobiphenyl (m~e 122) formed in almost equal amounts.
Exa-ple 4 Dechlorination of Askarel.
15The condltlons clted ln ~xample 3 for the dechlorlnation of Arochlor 1248 were repeated for the dechlorinatlon of Askarel. To a mlxture of Askarel (1.5990 gl in methanol (100 ml), 2.04 g of calcium were added and the mixture was stirred at room temperature untll calcium metal disappeared. Hexane extractlon was then performed to prepare unreacted Askarel for the second treatment. The second treatment also lnvolved the use of 2.04 g of calcium and 100 ml of methanol. After the disappearance of calclum GC/Mass analysis lndlcated that close to 99% of Askarel had dlsappeared. The products formed were mainly blphenyl and partially hydrogenated CA 02026~06 1998-12-24 Mono- and di-chlorobiphenyls, traces of cyclohexylbenzene and cyclohexenylbenzene are also formed.
Example 5 When the experimental conditions of Examples 3 and 4 were used replacing methanol with iso-propanol and terbutanol or THF, no appreciable dechlorination was observed.
Claims (26)
1. A process for the reductive dehalogenation of halogenated aromatics with sodium or calcium and a lower alcohol selected from the group consisting of methanol, ethanol, isopropanol and mixtures thereof, said process comprising:
a) when calcium is used:
- preparing a mixture comprising halogenated aromatics and calcium in said lower alcohol as a solvent;;
- allowing calcium to react with said halogenated aromatics; and - recovering products resulting from the reductive dehalogenation of said halogenated aromatics;
b) when sodium is used:
- preparing a mixture comprising halogenated aromatics in mineral oil, sodium in reactive form and said lower alcohol, said lower alcohol being present in an amount sufficient to prevent oil decomposition and polymerization of said halogenated aromatics when the reductive dehalogenation takes place;
- heating said mixture to a temperature above the melting point of sodium to cause said sodium to react with said halogenated aromatics; and - recovering products resulting from the reductive dehalogenation of said halogenated aromatics.
a) when calcium is used:
- preparing a mixture comprising halogenated aromatics and calcium in said lower alcohol as a solvent;;
- allowing calcium to react with said halogenated aromatics; and - recovering products resulting from the reductive dehalogenation of said halogenated aromatics;
b) when sodium is used:
- preparing a mixture comprising halogenated aromatics in mineral oil, sodium in reactive form and said lower alcohol, said lower alcohol being present in an amount sufficient to prevent oil decomposition and polymerization of said halogenated aromatics when the reductive dehalogenation takes place;
- heating said mixture to a temperature above the melting point of sodium to cause said sodium to react with said halogenated aromatics; and - recovering products resulting from the reductive dehalogenation of said halogenated aromatics.
2. A process according to claim 1, wherein said lower alcohol is methanol.
3. A process according to claim 1, wherein said calcium is used in granular form or as turnings.
4. A process according to claim 1, wherein said dehalogenation reaction is carried out at room temperature when calcium is used.
5. A process according to claim 1, wherein said lower alcohol acts as a solvent when calcium is used.
6. A process according to claim 1, wherein said halogenated aromatics are polychlorinated biphenyls.
7. A process according to claim 2, wherein the starting sodium/methanol/halogen molar ratio ranges from 2-40/1-20/1.
8. A process according to claim 7, wherein the starting sodium/methanol/halogen molar ratio is 2/1/1.
9. A process according to claim 1, wherein the dehalogenation reaction is carried out under nitrogen atmosphere when sodium is used.
10. A process according to claim 1, wherein said halogenated aromatics are contained in a mineral oil or in soil.
11. A process for the reductive dehalogenation of halogenated aromatics in mineral oil, said process comprising:
- preparing a mixture comprising halogenated aromatics, sodium in reactive form and a lower alcohol selected from the group consisting of methanol, ethanol and isopropanol and mixtures thereof, said lower alcohol being present in an amount sufficient to prevent oil decomposition and polymerization of halogenated aromatics when the reductive dehalogenation takes place;
- heating said mixture to a temperature above the melting point of sodium to cause said sodium to dehalogenate said halogenated aromatics; and - recovering said products resulting from the reductive dehalogenation of said halogenated aromatics.
- preparing a mixture comprising halogenated aromatics, sodium in reactive form and a lower alcohol selected from the group consisting of methanol, ethanol and isopropanol and mixtures thereof, said lower alcohol being present in an amount sufficient to prevent oil decomposition and polymerization of halogenated aromatics when the reductive dehalogenation takes place;
- heating said mixture to a temperature above the melting point of sodium to cause said sodium to dehalogenate said halogenated aromatics; and - recovering said products resulting from the reductive dehalogenation of said halogenated aromatics.
12. A process according to claim 11, wherein said halogenated aromatics are contained in transformer oil.
13. A process according to claim 11, wherein said lower alcohol is methanol.
14. A process according to claim 11, wherein said halogenated aromatics are polychlorinated biphenyls.
15. A process according to claim 11, wherein the starting sodium/methanol/halogen molar ratios ranges from 2-40/1-20/1.
16. A process according to claim 15, wherein the starting sodium/methanol/halogen molar ratio is 2/1/1.
17. A process for the reductive dehalogenation of halogenated aromatics, said process comprising reacting halogenated aromatics with calcium in a solvent selected from the group consisting of methanol, ethanol and isopropanol and mixtures thereof and recovering the products resulting from the reduction of said halogenated aromatics.
18. A process according to claim 17, wherein said solvent is methanol.
19. A process according to claim 17, wherein said calcium is used in granular form or as turnings.
20. A process according to claim 17, wherein said dehalogenation reaction is carried out at room temperature.
21. A process according to claim 17, wherein said halogenated aromatics are polychlorinated biphenyls.
22. A process according to claim 17, wherein said halogenated aromatics are contained in soil.
23. A process for the treatment of soil contaminated with halogenated aromatics to dehalogenate said halogenated aromatics, said process comprising:
- preparing a methanolic extract of said soil;
- reacting said extract with calcium; and - recovering the products resulting from the dehalogenation of said halogenated aromatics.
- preparing a methanolic extract of said soil;
- reacting said extract with calcium; and - recovering the products resulting from the dehalogenation of said halogenated aromatics.
24. A process according to claim 23, wherein said calcium in in granula form or as turnings.
25. A process according to claim 23, wherein said reaction is carried out at room temperature.
26. A process according to claim 23, wherein said halogenated aromatics are polychlorinated biphenyls.
Applications Claiming Priority (4)
Application Number | Priority Date | Filing Date | Title |
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US07/413,942 | 1989-09-28 | ||
US07/413,942 US4950833A (en) | 1989-09-28 | 1989-09-28 | Process for the reductive dehalogenation of polyhaloaromatics |
US07/538,233 | 1990-06-14 | ||
US07/538,233 US5185488A (en) | 1989-09-28 | 1990-06-14 | Process for the reductive dehalogenation of polyhaloaromatics with sodium or calcium in a lower alcohol |
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US5994604A (en) * | 1993-03-17 | 1999-11-30 | Lockheed Martin Idaho Technologies Company | Method and apparatus for low temperature destruction of halogenated hydrocarbons |
US5951852A (en) * | 1993-12-23 | 1999-09-14 | Commonwealth Scientific And Industrial Research Organisation Et Al. | Destruction of halide containing organics and solvent purification |
US5672266A (en) * | 1995-10-13 | 1997-09-30 | The Lubrizol Corporation | Treatment of organic compounds to reduce chlorine level |
US5489390A (en) * | 1995-03-14 | 1996-02-06 | The Lubrizol Corporation | Treatment of organic compounds to reduce chlorine level |
US5534124A (en) * | 1995-09-19 | 1996-07-09 | Chem-Pro | On-site electrochemical dehalogenation process and system |
US5674819A (en) * | 1995-11-09 | 1997-10-07 | The Lubrizol Corporation | Carboxylic compositions, derivatives,lubricants, fuels and concentrates |
DE19903987A1 (en) * | 1999-02-02 | 2000-08-10 | Friedrich Boelsing | Rapid reductive dehalogenation of halohydrocarbons, e.g. for removing toxic chloroaromatic compounds from waste oil or soil, by contacting finely divided solid starting material with reducing metal |
US6414212B1 (en) | 2000-08-18 | 2002-07-02 | Kinectrics, Inc. | Method for decontamination of low level polyhalogenated aromatic contaminated fluid and simultaneous destruction of high level polyhalogenated aromatics |
US20030120127A1 (en) * | 2001-11-07 | 2003-06-26 | Wylie Ian Gordon Norman | Process for destruction of halogenated organic compounds in solids |
US6984768B2 (en) | 2002-05-21 | 2006-01-10 | Battelle Energy Alliance, Llc | Method for destroying halocarbon compositions using a critical solvent |
US20050056598A1 (en) * | 2003-06-06 | 2005-03-17 | Chowdhury Ajit K. | Method for treating recalcitrant organic compounds |
CN101230304B (en) * | 2007-01-25 | 2010-05-19 | 钟奇 | Environment-friendly type transformer oil and preparation method thereof |
DE102008056086A1 (en) * | 2008-11-06 | 2010-05-12 | Gp Solar Gmbh | An additive for alkaline etching solutions, in particular for texture etching solutions and process for its preparation |
CN112142543B (en) * | 2019-06-26 | 2023-03-28 | 北京工商大学 | Dehalogenation method of covalent organic framework material photocatalytic halogenated aromatic compound |
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US4351978A (en) * | 1980-07-21 | 1982-09-28 | Osaka Prefectural Government | Method for the disposal of polychlorinated biphenyls |
US4447667A (en) * | 1982-09-22 | 1984-05-08 | The Goodyear Tire & Rubber Company | Process for the dehalogenation of organic compounds |
IT1206508B (en) * | 1983-07-22 | 1989-04-27 | Sea Marconi Decontamin Srl | CONTINUOUS PROCESS FOR THE DECOMPOSITION AND DECONTAMINATION OF ORGANIC COMPOUNDS AND HALOGENATED TOXIC AGENTS. |
CH668709A5 (en) * | 1985-12-06 | 1989-01-31 | Ciba Geigy Ag | METHOD FOR ENTHALOGENATING POLYHALOGENATED ALIPHATIC AND AROMATIC COMPOUNDS. |
DE3621175A1 (en) * | 1986-06-25 | 1988-01-07 | Huels Chemische Werke Ag | METHOD FOR ENTHALOGENATING HYDROCARBON OILS |
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