AU624414B2 - A process and apparatus for the conversion of solid waste into glass - Google Patents
A process and apparatus for the conversion of solid waste into glass Download PDFInfo
- Publication number
- AU624414B2 AU624414B2 AU41060/89A AU4106089A AU624414B2 AU 624414 B2 AU624414 B2 AU 624414B2 AU 41060/89 A AU41060/89 A AU 41060/89A AU 4106089 A AU4106089 A AU 4106089A AU 624414 B2 AU624414 B2 AU 624414B2
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- Australia
- Prior art keywords
- batch
- exhaust gas
- glass
- melt
- gas
- Prior art date
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- Ceased
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- 239000011521 glass Substances 0.000 title claims description 61
- 238000000034 method Methods 0.000 title claims description 43
- 238000006243 chemical reaction Methods 0.000 title claims description 5
- 239000002910 solid waste Substances 0.000 title 1
- 239000000156 glass melt Substances 0.000 claims description 35
- 239000000126 substance Substances 0.000 claims description 32
- 239000007859 condensation product Substances 0.000 claims description 23
- 239000000654 additive Substances 0.000 claims description 14
- 238000001816 cooling Methods 0.000 claims description 14
- 239000002699 waste material Substances 0.000 claims description 14
- 239000000155 melt Substances 0.000 claims description 12
- 239000007787 solid Substances 0.000 claims description 12
- 239000003513 alkali Substances 0.000 claims description 9
- 150000003839 salts Chemical class 0.000 claims description 7
- 239000000428 dust Substances 0.000 claims description 6
- 238000010309 melting process Methods 0.000 claims description 6
- 238000002156 mixing Methods 0.000 claims description 6
- 150000001447 alkali salts Chemical class 0.000 claims description 4
- 230000000996 additive effect Effects 0.000 claims description 3
- 239000007789 gas Substances 0.000 description 156
- 238000002844 melting Methods 0.000 description 47
- 230000008018 melting Effects 0.000 description 47
- 238000000746 purification Methods 0.000 description 32
- YLQBMQCUIZJEEH-UHFFFAOYSA-N Furan Chemical compound C=1C=COC=1 YLQBMQCUIZJEEH-UHFFFAOYSA-N 0.000 description 22
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 description 11
- 229910001385 heavy metal Inorganic materials 0.000 description 11
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 9
- 239000002826 coolant Substances 0.000 description 9
- 150000001805 chlorine compounds Chemical class 0.000 description 8
- 239000000203 mixture Substances 0.000 description 8
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 7
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 7
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 7
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 6
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 6
- 239000000047 product Substances 0.000 description 6
- 238000003303 reheating Methods 0.000 description 6
- 230000008030 elimination Effects 0.000 description 5
- 238000003379 elimination reaction Methods 0.000 description 5
- 238000010438 heat treatment Methods 0.000 description 5
- 239000002002 slurry Substances 0.000 description 5
- 150000003467 sulfuric acid derivatives Chemical class 0.000 description 5
- 238000000926 separation method Methods 0.000 description 4
- 210000004127 vitreous body Anatomy 0.000 description 4
- 239000002351 wastewater Substances 0.000 description 4
- 241000196324 Embryophyta Species 0.000 description 3
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 229910052783 alkali metal Inorganic materials 0.000 description 3
- 230000009286 beneficial effect Effects 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 3
- 229910002092 carbon dioxide Inorganic materials 0.000 description 3
- 239000001569 carbon dioxide Substances 0.000 description 3
- 238000004140 cleaning Methods 0.000 description 3
- 239000006063 cullet Substances 0.000 description 3
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- 239000011780 sodium chloride Substances 0.000 description 3
- 229910052938 sodium sulfate Inorganic materials 0.000 description 3
- 235000011152 sodium sulphate Nutrition 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 2
- 229910004298 SiO 2 Inorganic materials 0.000 description 2
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 2
- 229910000831 Steel Inorganic materials 0.000 description 2
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 239000011575 calcium Substances 0.000 description 2
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 2
- 238000009833 condensation Methods 0.000 description 2
- 230000005494 condensation Effects 0.000 description 2
- 239000004035 construction material Substances 0.000 description 2
- 239000000706 filtrate Substances 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 238000009413 insulation Methods 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 229910052753 mercury Inorganic materials 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 239000006060 molten glass Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 239000004576 sand Substances 0.000 description 2
- 229920006395 saturated elastomer Polymers 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- 239000010959 steel Substances 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- 235000018734 Sambucus australis Nutrition 0.000 description 1
- 244000180577 Sambucus australis Species 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 239000005864 Sulphur Substances 0.000 description 1
- ATJFFYVFTNAWJD-UHFFFAOYSA-N Tin Chemical compound [Sn] ATJFFYVFTNAWJD-UHFFFAOYSA-N 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 238000005266 casting Methods 0.000 description 1
- 230000001413 cellular effect Effects 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 239000000567 combustion gas Substances 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 239000000498 cooling water Substances 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 230000008025 crystallization Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000005108 dry cleaning Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 230000007717 exclusion Effects 0.000 description 1
- 150000004820 halides Chemical class 0.000 description 1
- 231100001261 hazardous Toxicity 0.000 description 1
- 239000011133 lead Substances 0.000 description 1
- 230000013011 mating Effects 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 239000010813 municipal solid waste Substances 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 239000002901 radioactive waste Substances 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 230000000284 resting effect Effects 0.000 description 1
- 238000007711 solidification Methods 0.000 description 1
- 230000008023 solidification Effects 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 229910052718 tin Inorganic materials 0.000 description 1
- 239000011135 tin Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000010891 toxic waste Substances 0.000 description 1
- 238000009834 vaporization Methods 0.000 description 1
- 230000008016 vaporization Effects 0.000 description 1
- 238000004017 vitrification Methods 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C03—GLASS; MINERAL OR SLAG WOOL
- C03B—MANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
- C03B3/00—Charging the melting furnaces
- C03B3/02—Charging the melting furnaces combined with preheating, premelting or pretreating the glass-making ingredients, pellets or cullet
- C03B3/023—Preheating
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/20—Agglomeration, binding or encapsulation of solid waste
- B09B3/25—Agglomeration, binding or encapsulation of solid waste using mineral binders or matrix
- B09B3/29—Agglomeration, binding or encapsulation of solid waste using mineral binders or matrix involving a melting or softening step
-
- C—CHEMISTRY; METALLURGY
- C03—GLASS; MINERAL OR SLAG WOOL
- C03B—MANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
- C03B19/00—Other methods of shaping glass
- C03B19/10—Forming beads
- C03B19/109—Glass-melting furnaces specially adapted for making beads
-
- C—CHEMISTRY; METALLURGY
- C03—GLASS; MINERAL OR SLAG WOOL
- C03B—MANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
- C03B5/00—Melting in furnaces; Furnaces so far as specially adapted for glass manufacture
- C03B5/005—Melting in furnaces; Furnaces so far as specially adapted for glass manufacture of glass-forming waste materials
-
- C—CHEMISTRY; METALLURGY
- C03—GLASS; MINERAL OR SLAG WOOL
- C03B—MANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
- C03B5/00—Melting in furnaces; Furnaces so far as specially adapted for glass manufacture
- C03B5/02—Melting in furnaces; Furnaces so far as specially adapted for glass manufacture in electric furnaces, e.g. by dielectric heating
- C03B5/027—Melting in furnaces; Furnaces so far as specially adapted for glass manufacture in electric furnaces, e.g. by dielectric heating by passing an electric current between electrodes immersed in the glass bath, i.e. by direct resistance heating
- C03B5/03—Tank furnaces
-
- C—CHEMISTRY; METALLURGY
- C03—GLASS; MINERAL OR SLAG WOOL
- C03B—MANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
- C03B5/00—Melting in furnaces; Furnaces so far as specially adapted for glass manufacture
- C03B5/04—Melting in furnaces; Furnaces so far as specially adapted for glass manufacture in tank furnaces
-
- C—CHEMISTRY; METALLURGY
- C03—GLASS; MINERAL OR SLAG WOOL
- C03B—MANUFACTURE, SHAPING, OR SUPPLEMENTARY PROCESSES
- C03B5/00—Melting in furnaces; Furnaces so far as specially adapted for glass manufacture
- C03B5/16—Special features of the melting process; Auxiliary means specially adapted for glass-melting furnaces
- C03B5/235—Heating the glass
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N2550/00—Monitoring or diagnosing the deterioration of exhaust systems
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P40/00—Technologies relating to the processing of minerals
- Y02P40/50—Glass production, e.g. reusing waste heat during processing or shaping
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Materials Engineering (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Electrochemistry (AREA)
- Manufacturing & Machinery (AREA)
- Processing Of Solid Wastes (AREA)
- Glass Melting And Manufacturing (AREA)
Description
:Crr~ 41 4 COMPLETE SPECIFICATION FOR OFFICE USE Application Number: Lodged: Complete Specification Priority: Class Int. Class Lodged: Accepted: Published: Related Art: o po 9 p 0 *000 0 TO BE COMPLETED BY APPLICANT 1QL Name of Applicant: A SORG GmbH Co. KG. and METALLGESELLSCHAFT AG.
Address of Applicant: Im Aller 23, D-8770 Lohr/Main, Federal Republic of Germany and Reuterweg 14, D-6000 Frankfurt 1, Federal Republic of Germany respectively.
p 0 0 0 0 Actual Inventors: Address for Service: Helmut SORG, Helmut PIEPER, Hartmut ZSCHOCHER and Heinz MERLET SMITH SHELSTON BEADLE 207 Riversdale Road Box 410) Hawthorn, Victoria, Australia Complete Specification for the invention entitled: o*0 A PROCESS AND APPARATUS FOR WASTE INTO GLASS THE CONVERSION OF SOLID of this invention, including The following statement is a full description the best method of performing it known to us: Page 1 Our Ref: #4016 JC:WB 24sor 1 u i The invention relates to a process for the conversion of solid, mostly dehydrated waste substances into glass, wherein the waste substances are mixed with one or several additives to form a batch to be melted. A major portion of the batch is melted into a glass melt by supplying heat and a minor portion is exhausted from the melting batch as an exhaust gas. Solid vitreous bodies are formed from the «glass melt by means of casting and cooling. Furthermore, r r the invention relates to an apparatus for the working of *0 this process.
It has long been known, to convert toxic and radioactive waste substances in the form of slurries or suspensions into glass by means of melting after adding o 0. additives and mixing it into a batch. The formerly loose waste substances are now tightly incorporated in the glass.
o Glass possesses the advantages property that it is difficult to leach out, thus permitting the release of heavy metal and other substances contained in the glass only to such a small extent that the storage or the use of bodies made of such 0O glass does not cause any problems. One difficulty regarding the vitrification of waste substances is their generally high percentage of chlorides -2ll i i| t;S_ :~lj: r r
-I,
t "600 and calcium sulfate. Thc',cra integrated into the glass melt only to a very small extent during the melting process even if the chloride and sulphur capacity of the glass melt is completely saturated, which is due to the large amount of these substances present. Hence, large amounts of exhaust gas containing gases of chlorides and sulfate, especially Cl, HC1, SO 2 and SO, are a disadvantageous result.
Contrary to that, it is a matter of fact that a sufficient amount of heavy metal and additional alkali escaping from F the glass melt by means of vaporization. The most S aggravating disadvantage of the known process, especially 0 with regard to its environmental effects, is the formation or possible formation of dioxin and/or furan when the batch is heated during the melting process. This occurs when the 15 waste substances to be converted still contain organic components, from which these harmful substances are formed 0 under temperatures occurring during the melting of the batch.
.rJI 6 0 ao 046 0 0 o« 0 4l SUMMARY OF THE INVENTION Hence, it is the object of the invention to provide a process which is less harmful to the environment and excludes especially the emission of dioxin and/or furan even -3r I~ ii; i i ;d ii b
I~
-4if heterogeneous, organic components as well as heavy metal are employed. Furthermore, it is the object of the invention to provide an apparatus for the working of this process.
Accordingly, the invention provides a process for converting solid, dehydrated waste substance into glass, comprising mixing the waste substances with at least one additive to form a mixed batch, generating a gall layer of alkali salt or alkaline earth salt on the surface of a glass melt heated solely by electrodes, and introducing the mixed batch onto said glass melt surface so that a major portion is melted into the melt and a minor portion produces an exhaust gas emerging O" from the melt, said gall layer serving as a melt 0 accelerator, introducing the exhaust gas into the batch to be melted, thereby cooling said gas and producing condensation products in the batch, and reintroducing said condensation products into the melt with the batch. I The first part of the object is achieved in a process where the waste substance is incineration ash, i and hot exhaust gas is withdrawn under exclusion of surrounding air and reintroduced into the batch to be melted where it is cooled down to 20 to 50 C.
Condensation products resulting from the cooling process bc/13/4016.res 92 3 17
'I
i f are melted with the batch, and the cold exhaust gas emerging from the batch to be melted is purified.
The new process permits the conversion of a so far very problematic waste substance, i.e. incineration ash, into glass in an ecologically beneficial way despite the fact that such ash products are heterogeneous and consist of high and unstable percentages especially of carbon, mercury, lead, tin, zinc, calcium, chlorides, and halides. A major portion of these harmful substances is directly integrated into the glass melt, hence, they are tightly incorporated. Harmful substances escaping as gases are mostly condensed by cooling within the batch to be molten and then reintroduced into the melting mass. The remaining, relatively small amount of cold exhaust gases are neutralized in a subsequent purification process.
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r: if A further development of the process provides a reheating of the hot exhaust gas which escapes from the batch to be molten to at least 1200 0 C for a residence time of at least 1.5 second. The gas is then pre-cooled under partial condensation to 200 to 300 0 C and subsequently reintroduced into the batch to be molten where it is cooled down to 20 to 50 0 C; the condensation products resulting from the pre-cooling are reintroduced into the batch to be l molten and/or exhausted. Reheating the exhaust gas to definitely eliminates a possible presence of dioxin and 0 furan. Hence, the average temperature and residence time must be selected to ensure the elimination desired. The subsequently exhausted gas basically contains only chlorides, sulfates, carbon dioxide, and alkali and heavy 15 metal vapor. Through a following pre-cooling to 200-300°C a0o o the hot exhaust gas is partially condensed, hence reduced in its quantity as well as in its number of components. The o return pipes provided for the reintroduction of the condensation products into the batch to be molten keep these 20 products in a closed circuit; they are gradually converted into glass. After an initial phase a balanced condition is reached causing the amount of condensation products to remain constant. Passing the pre-cooled exhaust gas through the batch to be molten causes vapors which condense only at i: q :i: ib l f:' i I i ~3 i
I
ie: low temperatuares, like heavy-metal vapor and especially mercury vapor, to be deposited on batch particles, thus being reintroduced to the melting process. Due to the strong cooling while passing through the batch, the chlorides and sulfates are practically completely condensed.
If more chlorides and sulfates are vaporized than can be dissolved in the glass melt after the reintroduction of the condensed products, these substances are enriched in the rc r batch. To avoid this, the surplus condensation product 0 resulting from the pre-cooling is advantageously removed.
0 These condensation products are for the most part solid.
S: The remaining cold exhaust gas then contains almost exclusively hydrogen chloride (HC1) and sulfur dioxide (SO 2 in high concentration. The volume of the remaining exhaust gas is relatively small, compared to the throughput of 8 incineration ash. Moreover, the relatively high concentration and the simple composition of the cold exhaust gas is advantageous to the subsequent final gas purification. The gas purification requires only a 2z0 relatively small capacity and provides comparatively pure i separation products, especially sodium chloride and sodium sulfate, which can be used, for example, for the manufacture of soda. The heat energy required for the melting process is electrically generated, thus avoiding the addition of i -6-
"I
I y combustion gas of a fossil-fuel-operated heating device to the exhaust gas resulting from the melting batch, a fact which would complicate the exhaust gas treatment.
The new process is ecologically very beneficial as well as economical. On the one hand, the exhaust gas emission is largely reduced and on the other hand the process provides raw material for other purposes; for example vitreous bodies which are employed as construction materials and the already mentioned sodium chloride and sodium sulfate. The new process excludes any emission of dioxin and/or furan.
o &o Furthermore, the new process permits a reheating of the hot exhaust gas in a separate after-burner. This variant of *4 the process is not as economical with regard to the energy consumption, however, it does not require a complicated oe: 15 melting device. Furthermore, it is advantageous that the o' entire glass bath can be covered by the batch, permitting a major portion of the alkali and heavy metal vapor to be i 0 4 condensed under the batch cover in the furnace. An alternative and particularly energy saving embodiment of the .o process suggests that a part of the glass melt surface be free of batch; the hot exhaust gas escaping from the melting batch be then passed over the batch-free part of the glass melt surface and thus reheated by heat absorption from the glass melt.
-L i i. ii 4" J Another alternative suggests that the cold exhaust gas emerging from the batch to be molten be reheated up to a temperature of at least 1200°C for a period of at least 1.6 seconds and then be subject to purification. The exhaust gas reheating eliminates dioxin and/or furan, thus ensuring that there is no escape of these harmful substances.
As a last alternative regarding the reheating of the exhaust gas, the process suggests that the exhaust gas emerging from the purification process be reheated to a temperature of at least 1200 0 C for a period of at least seconds. This also ensures an elimination of dioxin and/or furan. The selection of an appropriate variant is up to the o g.o expert and depends on the requirements and conditions of the individual case.
0 :'i6 With regard to the additives, the process suggests the use of substances containing SiO 2 especially sand and/or phonolite. These additives are easy to handle and inexpensive. Alternatively and/or supplementary, cullet can o0 be employed as an additive containing SiO 2 The process oc 0 00 0 o a4 also suggests that the gas escaping from the melting batch as well as the hot exhaust gas be exhausted under subatmospheric pressure and pre-cooled and that the pre-cooled exhaust gas be then put under super atmospheric pressure. The exhaust gas can then be passed through the -8-
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1 j i iB: i~f
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i81_ batch to be molten in a counterflow and the pressure of the cold exhaust gas escaping from the batch to be molten can be controlled so that it be basically identical with the pressure of the surrounding air. On the one hand this ensures that no exhaust gas resulting from the melting batch escapes into the environment; on the other hand there is a sufficient throughput of pre-cooled exhaust gas through the batch to be molten. Finally, it is also achieved that there is no major escape of exhaust gas into the environment during the formation of the batch and that no additional air infiltrates the exhaust gas.
o Apparatus for practicing the process includes a batch o mixer and a closed glass melting furnace. The batch mixer has an inlet for incineration ash and additives, and an outlet for the mixed batch, as well as gas inlet and a gas 0 outlet for passing exhaust gas from the furnace through the batch. A batch outlet provides charge to one end of the furnace, which has a molten glass outlet at the opposite end.
o 0 one 00~u" p..s 0 pose 0.4i 0 0 0'4 00 0 o o 0 This apparatus permits a safe, continuous, and ecologically beneficial working of the above described process.
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ii -9- 1 BRIEF DESCRIPTION OF THE DRAWINGS Figure 1 Figures 2 Figure 5 Figure 6 Figure 7 is a diagrammatical cross section view of the first embodiment, to 4 show the apparatus in its respective second, third, and fourth embodiments, is a schematic of a first embodiment of gas purification device, is a schematic of a second embodiment of gas purification device, is a flow diagram of a system of removing dust and filtrate slurry from the exhaust gas.
a at 0 DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS a .Figure 1 shows supply vessels 2, batch mixer 3, a glass S melting furnace 4, a glass working machine, an exhaust gas o cooler 6, and a gas purification device 7.
The supply vessels 2 serve to hold and store incineration ash 80 and additives 81. The bottom end of each supply vessel 2 is provided with a dosing sluice S* for example a cellular wheel sluice. These dosing sluices Slod" end in a common conveyor device 21, in this case a screw conveyor, which leads to the top of the batch mixer 3. The batch mixer 3 consists of a funnel-like housing 30 and a mixing screw 31 disposed in housing 30. The mixing screw 31 i iI i; runs parallel to the inner side of the lateral wall of housing 30; it can be rotated around its own axis as well as around an axis running vertically through the center of the housing 30 of the batch mixer. The upper part of housing 30 is provided with a solid substance inlet which is connected with the above mentioned conveyor device 21. The bottom end of housing 30 of the batch mixer 3 is provided with a solid substance outlet leading to a batch conveyor 46. The batch conveyor 46 is already part of the glass tO melting furnace 4. The glass melting furnace 4 includes a tank 41 of fire-proof material covered by a superstructure 42, also made of fire-proof material. The tank 41 and the o 0 superstructure 42 rest on a support configured as steel girders. The external surface of the superstructure 42 of oro o 5 the glass melting furnace 4 has a gastight cover 42' o o S consisting of sheet steel. The cover 42' reaches up to the top rim of tank 41 to which it is joined in a sealed connection. From the top downward, heating electrodes 43 0o0e o pass through the superstructure 42 and the cover 42' into O ,o the interior of the glass melting furnace 4. The interior of the glass melting furnace is subdivided into two o0 different areas: a melting area, which is represented on the right side of Figure i. A suspended and straight arch 0 4esus 44 subdivides the glass melting furnace into said areas.
-11- L1L It j A I This arch 44 protrudes downwardly and is configured as a part of the superstructure 42 from which it is suspended.
During operation of the glass melting furnace 4 this arch 44 is close to the surface 84' of a glass melt 84 contained in the furnace 4, and serves as a perpendicular dividing wall to form the gas area of furnace 4. Furthermore, under arch 44 there is a coolant tube 45 which runs parallel to this arch across the glass melting furnace 4. The coolant tube passes exactly at the same level with the surface 84' of the glass melt 84 and causes the glass melt 84 to solidify in the area surrounding the tube 45. The right end of the glass melting furnace is provided with a glass melt outlet ooc ~o 0 09 48 where a diagrammatically represented glass working eoso 9o°" machine 5 is added. Finally, the right end of the glass oooo C5 melting furnace 4 is also provided with an upward exhaust 0:o gas outlet 47 passing through the superstructure 42.
A heat insulated gas pipe 60 from the exhaust gas outlet 47 of the glass melting furnace 4 to the gas inlet 61 *oMVr oo of the exhaust gas cooler. In addition to the gas inlet 61, oY the exhaust gas cooler 6 is also provided with a gas outlet 62 and an outlet 63 for condensation products. Both outlets ec are disposed on the bottom end of exhaust gas cooler 6.
o Furthermore, the exhaust gas cooler 6 is furnished with a o 00device 65 for the feeding as well as the supply and the06 device 65 for the feeding as well as the supply and the -12- 1' 2' 4 f *0 discharge of a coolant, cooling water or cooling air.
On top of the exhaust cooler 6, a mechanical cleaning device 66 is indicated by means of which the gas containing parts of the exhaust gas cooler 6 are continuously or periodically Scleansed of the condensation products which result from exhaust gas cooling. The condensation product outlet 63 of the exhaust gas cooler 6 is connected to the feeding side of the batch mixer 3, i.e. to the upper part of its interior, via another conveyor device 64, in this case also a screw conveyor. For this purpose, the upper part of the housing of the batch mixer 3 is provided with a condensation product inlet 36. If required, the condensation products can be discharged either partially or completely via a switch 69 which is disposed on the upper end of the conveyor device 64.
A first suction fan 67, whose end is joined to a connecting pipe 68, is disposed downstream of the gas outlet 62 of the exhaust gas cooler 6. The connecting pipe 68 leads to a gas inlet 34 of the batch mixer 3. The gas inlet :7C 34 in disposed in the bottom part of the housing 30, and is configured to permit the gas to enter the interior of the houiing 30, but to prevent any batch discharge from the interior of housing 30 into pipe 38.
-13- 5I .0 1, e I i i;
I
4 i ;j iiii
;-I
?t:f ii! ii :3 1- 4 4
I
A gas outlet J3, followed by a second downstream suction fan 70, is disposed on the opposite end of gas inlet 34, i.e. on the upper end of batch mixer 3. The power of the first suction fan 67 and of the second suction fan can be controlled, preferably by a common control device. A gas pipe 71 leads from the outlet of the second suction fan to a gas purification device 7 whose components are generally known and are therefore not listed in detail.
t Finally, a chimney 79 is disposed downstream of the outlet t t0 of the gas purification device 7.
The embodiment represented in Figure !2 has a slightly :S different configuration than the embodiment as described in Figure 1. The arch 44 of Figure 1 is omitted in the glass melting furnace 4 of Figure 2; the superstructure 42 of the glass melting furnace 4 is configured as one single o o0 continuous component with the furnace interior forming one single area. Furthermore, the coolant tube 45 of the glass o* melting furnace according to Figure 1 is moved towards the li i discharge end of the glass melting furnace 4, i.e. to the right side. This permits the batch 83, which floats on the glass melt 84, to cover almost the entire surface 84' of the glass melt 84. This causes a major part of the gases and vapor escaping from the glass melt 84 to condense on the batch resting thereon. Thus, the amount of exhaust gas is -14- 7 k-a reduced. At the same timc, the temperature of the gas i emerging from the glass melting furnace 4 through outlet 47 is reduced. At this point, the temperature is between 300 and 500 0 C. In order to ensure a complete elimination of dioxin and/or furan in the exhaust gas, a separate gas heater 91 is employed in the gas pipe 60 disposed downstream of the gas exhaust outlet 47. This gas heater 91 is only diagrammatically indicated and can be of conventional design. The incoming gas is heated to a temperature of at least 1200 0 C for a period of at least 1.5 seconds.
Itt do Other details of the apparatus of Figure 2 correspond to the apparatus of Figure 1, with same parts of the apparatus being characterized by the same numbers.
In a third embodiment of the apparatus, shown in Figure 3, the exhaust gas cooler 6 inclusive of the mating gas pipe 60 is omitted. The glass melting furnace 4 corresponds in its essential parts to the glass melting furnace as a represented in Figure 2. It differs from the latter inasmuch that the gas exhaust outlet 47' is disposed at the furnace 4. This exhaust gas outlet 47' is connected to the intake of the first suction fan 67 via a short gas pipe From this point, an already described connection pipe 68 leads to the batch mixer 3.
L- 71:. Ii. i. iIi Since there are no condensatic.oducts fed to the exhaust gas cooler, the batch is, in its upper part, configured without the charging inlet 36 as described in the embodiments of Figures 1 and 2.
The heat necessary for the definite elimination of dioxin and/or furan is generated by a separate gas heater 91. In the apparatus according to Figure 3 this gas heater 91 is connected to the exhaust gas pipe 71 leading from the second suction fan 70 to the gas purification device 7.
The embodiment of Figure 4 corresponds mostly to the embodiment of Figure 3. It differs from the latter in that the separate gas heater 91 for the heating of the gas and the elimination of possible dioxin and/or furan is disposed downstream of the gas purification device 7 and is incorporated in the gas pipe leading to chimney 79. This embodiment offers the particular advantage that the amount of gas to be heated after passing the gas purification S( t4t device amounts only to about 50% of the original amount of gas which means saving heating energy.
The following is a description of how the process works, based on the apparatus described in Figure i.
Incineration ash 80 from a refuse incinerator or a garbage disposal plant is fed to the first supply vessel 2.
The remaining supply vessels 2 are charged with the S-16ii Condensation products resulting from the cooling process 'wJ 92 3 17 S Sbc/13/4016.res 9 3 17 if required, cullet, By means of the dosing sluices r i! necessary additives 81, especially sand and ,..onolite and, if required, cullet, By means of the dosing sluices premeasured amounts of incineration ash 80 and additives 81 are taken from the supply vessels 2 and fed via conveyor device 21 to vessel 30 of batch mixer 3, where the individual components are mixed by a mixer screw 31 in order to form a homogenous batch 82 which can be molten. The 00 prepared batch 82 is fed through the solid substance outlet 0000 ooo 33 of the batch mixer to the interior of the glass melting 000e furnace 4 by means of the batch charging device 46. During 8000 operation, the glass melting furnace 4 is filled with glass melt 84 up to a certain level. The surface 84' of the glass melt 84 is exactly at the same level with the coolant tube and just below the arch 44.
000 00oo6 The batch which is supplied by the batch charging 0 3 "00 device floats as a melting batch 83 on the glass melt 84 and is distributed on the surface 84' of the latter in the melting area (left part) of the glass melting furnace 4. A solidification of the glass melt 84 in the area surrounding *000 2O the coolant tube caused by a coolant passing through the latter prevents the melting batch 83 from passing beyond the arch 44 and the coolant tube 45. The heat energy required for the melting of the batch 83 is generated as joulean heat by heating electrodes 43, whose bottom ends protrude into -17- I l 1 the glass melt 84 which, in turn, assumes the function of an Fi ohmic resistor.
During the melting process, gases escape from the batch 83 with an exhaust gas temperature between 100°C and 1000 0
C.
Basically, this exhaust gas can contain SO 2 HC1, chloride, sulfates, carbon dioxide, alkali and heavy metal vapor, and dioxin and/or furan.
This exhaust gas 85 enters the right side of the interior of the glass melting furnace 4 through a crack between the bottom of arch 44 and the coolant tube 45. The surface 84' of the glass melt 84 in this part of the glass melting furnace 4 is free of batch. The glass melt 84 contained in this part of the glass melting furnace 4 has a temperature of approximately 1400 0 C. Hence, the temperature 1:5 in the upper part of the glass melting furnace 4 above the melt 84 amounts to at least 1300-1350 0 C. To achieve the S< highest possible temperature it is advantageous to provide the superstructure 42 of the glass melting furnace 4 with a Litt best possible insulation. The gas entering this area of the o glass melting furnace 4 is reheated by absorbing heat from the glass melt. An appropriate adjusting of the flow rate I and a corresponding selection of the dimensions of glass melting furnace causes the temperature of the hot exhaust gas to amount to at least 1200°C for a period of at least 1 -ie-.
i l 1
II.
i 1i i, I i 1 7i2% seconds. Thus, the dioxin and/or furan which is possibly contained in the exhaust gas is definitely eliminated; consequently the hot exhaust gas contains only the chlorides, sulfates, carbon dioxide and the alkali and heavy metal vapors.
This hot exhaust gas is exhausted through the heat insulated pipe 60. Basically, the insulation serves to prevent a cooling and thus a subsequent condensation of the 4 of hot exhaust gas 86 within the pipe 60. The hot exhaust 0a0 10O gas is fed through gas inlet 61 to exhaust gas cooler 6, where it is cooled down to a temperature between 300 and 500 0 C, a process whereby a part of the exhaust gas is condensed and deposited within the c-haust gas cooler 6.
The resulting condensation products 88 are removed
D
S
A
0re continuously or periodically by means of a cleaning device 66 and fed to condensation product outlet 63 which is below '0 the exhaust gas cooler 6. The condensation products 88 are fed via conveyor device 64 through condensation product inlet 36 to the interior of the batch mixer 3 and thus reintroduced into the batch to be molten. If necessary, the condensation products cna be removed completely or partially via outlet 69.
I;
*1.
LI)
-19- 1 i The pre-cooled exhaust gas 87 exits the exhaust gas cooler via gas outlet 62 and reaches the first suction fan 67, which generates at its intake, within the exhaust gas cooler 6, in the pipe 60 and in the glass melting furnace 4, a pressure less than the pressure of the surrounding air. On the side facing towards the conveyor, the pre-cooled exhaust gas passes through the connecting pipe 68 towards the batch mixer 3 at a pressure higher than the pressure of the surrounding air. This pre-cooled 'tCIO exhaust gas 87, being under a superatmospheric pressure, is ft t t fed into the batch 82 contained in the interior of the batch mixer 3 via gas inlet 34. While the exhaust gas 87 is passing through, it condenses and thereby is cooled down to approximately 20-50 0 C. It emerges from the surface of the t ti15 batch 82 as a cold exhaust gas. In addition to the mixing of the individual batch components, the mixer screw 31 keeps the batch loose and permeable to gas. Due to the intense t cooling, even low condensing vapor e.g. heavy metal vapor condenses within the batch 82 to be molten. The cold S o10 exhaust gas 89 escaping through gas outlet 35 of the batch mixer 3 contains basically only HCl and SO 2 Interacting with a corresponding control unit and a pressure sensor, it is the purpose of the second suction fan I which is disposed downstream of the gas outlet 35, to -7maintain the pressure of the cold exhaust gas 89 in the upper part of the batch mixer at approximately the same level with the pressure of the surrounding air. This prevents the intrusion of exhaust gas and additional air 6 into the system.
The cold exhaust gas 89 which is basically a concentrated gas consisting of chlorides, SO 2 and SO 3 is fed to the gas purification device 7 via pipe 71 where it is subject to purification. The remaining exhaust gases 0especially N 2
CO
2 and small amounts of oxygen, which escape from the gas purification device are finally exhausted into the environment through chimney 79. The relatively harmless components of the remaining exhaust gas 90 are not hazardous or pollutant to the environment.
level wAccording to the ssupr of esentative embodiments, the apparatus 1 provides, in addition to the remaining exhaust Thegas, a vitreous body 9 which can be reused as a raw material for further industrial purposes. These vitreous bodies 9it is are manufactured continuously from the discharged glass Sespec84''iall by means of a glass working machine 5. These vitreouscape frbodies can be used, for example, as ballast or concreted into additivesording to the representative embodiments, the -21- V *i 1 -8-
I
The size of the glass melting furnace 4 and hence the volume of the glass melt 84 contained therein are advantageously selected to be large enough so that deviations in the composition of the incineration ash, which might occur, do not suddenly change the entire chemistry of the molten glass. Changes of the glass melt composition 84 can be determined very quickly, e.g. by changes in the electrical resistance of the glass melt 84 between the electrodes. These measured values can be used to control 01 10 the mixture of the incineration ash 80 and the individual o 00 additives, especially additives with a certain alkali 01-g percentage, e.g. phonolite.
Another possibility for monitoring the composition of 006 the glass melt 84 is to examine the crystallization of the final glass product. Glass compositions within certain e4 e 0 limits form certain crystals which can be easily recognized in the final glass. They indicate if and how the °0 o composition of the glass has been modified. The amount of the incineration ash 80 and the additives to be added can P o0 then be correspondingly adapted. Figures 5 and 6 show two embodiments of the gas purification device 7. Figure 5 represents a wet cleaning device 7, and Figure 6 a dry or semi-dry cleaning device 7.
-22- V idiivs eseilyadtvswihacranak k -9- According to Figure 5, the cold exhaust gas 89 is fed through pipe 71 to a first purification stage 72. This first purification stage serves to wash out especially HC1 gas from the exhaust gas. In a second purification stage 72' SO 2 is washed out. A subsequent drop separator 73 separates the water drops which were dragged along. In a gas reheating stage 74, the gas is reheated to an appropriate temperature between 30 and 90 0 C and subsequently fed through an activated carbon filter stage 78. After i0 passing this stage the remaining exhaust gas 90 consists C C basically of N 2 C0 2 and small amounts of oxygen which are rt exhausted into the environment via chimney 79.
For the HC1 separation in the first purification state 72, an acid, preferably of pH less than 1, has to be selected. For the separation of SO 2 in the second purification stage 72', however, a pH of 6-7.5 is preferred.
4 it Preferably, both purification stages 72 and 72' operate on reversed current, however, direct current is also possible.
Mercury which is possibly present in the exhaust gas 89 is 1* O separated in the activated charcoal filtering stage. The amount of waste water and slurry resulting from the purification stages 72 and 72' and from the drop separator are fed advantageously to a waste-water purifying plant.
-23i The seco.d embodiment of the gas purification device 7, shown in Figure 7 has as a first component a saturator 75 to which the cold exhaust gas 89 is fed, also via pipe 71.
Once the exhaust gas is saturated with water in the saturator 75, it is introduced to a fluidized bed or a spray adsorber 76. Preferably, NaOH or Ca(OH) in watery solution are admitted to the spray adsorber. In a gas temperature regulating stage 77 the escaping gas is brought to an optimum temperature for the subsequent activated charcoal filtering stage 78. The finally remaining exhaust gas which escaped is exhausted into the environment through chimney o 79.
:The waste waters and the solid substances resulting 0 from this process are subject to further purification, e.g.
in a waste-water purification plant or are dumped or reused.
Due to the relatively simple, defined composition of 0 00 a the exhaust gas 89, the gas purification devices serve to recover sodium chloride and sodium sulfate in a relatively °p pure form. These raw substances, in turn, can be used for o0 the manufacture of soda.
1-i -24-i i S iti i.
L
.1:
J;
Apart from glass, products resulting from the inventive process are glass gall, dust, and/or slurry which have to be deposited or further processed if they are not used as a construction material like the glass.
It is thus a further object of the invention, to solve the problem of substances resulting from the melting of incineration ash in glass, which substances have not been deposited at all, or only to a small extent. The process should operate inexpensively, by means of conventional industrial apparatus, and should be safe So and troublefree.
r o This further object is achieved, by adding dust resulting from D gas purification into the batch, which dust may be a filtrate o slurry.
In order to have an absolutely harmless pure gas, the exhaust 1 5 gas is fed through an activated charcoal filter after purification.
In order to concentrate the exhaust gas, it is advantageous to cool it before and after purification.
o The total amount of harmful substances discharged from the process is reduced by those substances resulting from the gas purification and the heavy metals contained in the melt. Since the solubility for the heavy metals contained in the glass melt, and in a broader sense for all metals contained therein, is no exceeded during the process, all heavy metals are incorporated in i the glass, where they cannot be leached out, by reintroduction into the glass melt.
It is further surprising that the glass gall residue is relatively clean. This is due to the fact that a larger amount of gall, as compared to the process, permits a more exact separation and the gall thus reaches also a higher degreee of purity. It is possible to use this glass gall as a raw material for chemical pruposes. The glass gall percentage amounts to approximately of the incineration ash employed.
The claims form part of the disclosure of this specification.
00oo00 0 0 0000 0000 o a 0 J 0 0000 0000 o0 00 o*oo 0000 00 o 0 0 0 0 G0o 000 00 0 000 26
Claims (9)
1. Process for converting solid, dehydrated waste substance into glass, comprising mixing the waste substances with at least one additive to form a mixed batch, generating a gall layer of alkali salt or alkaline earth salt on the surface of a glass melt heated solely by electrodes, and introducing the mixed batch onto said glass melt surface so that a major portion is melted into the melt and a minor portion produces an exhaust gas emerging from the melt, said gall layer serving as a melt accelerator, introducing the exhaust gas into the batch to be melted, thereby cooling said gas and producing condensation products in the batch, and reintroducing said condensation products into the melt with the batch.
2. Process as in claim 1 wherein part of said gall layer is periodically removed to maintain a thickness between 2 and 5 cm.
3. Process as in claim 1 wherein said exhaust gas and the resulting condensation products contain alkali therein, said gall layer comprising one or more alkali salts from the group consisting of Na 2 SO,, K 2 SO 4 Li,SO,, and LiCI, said gall layer being generated during the melting process by adding one or more alkaline earth f 7* salts from the group consisting of CaSO,, CaCl,, MgSO,, 4 bc/13/4016.re 92 3 17 4 I 4 28 and Mgcl,, said alkaline earth salts reacting with said alkali to produce said alkali salts.
4. Process as in claim 3 wherein said alkaline earth salts are added to the melt with the batch.
Process as in claim 3 wherein said alkaline earth salts are added to the melt separately from the batch.
6. Process as in claim 1 wherein said gall layer comprises one or more alkaline earth salts from the group consisting of CaSO, and MgSO,.
7. Process as in claim 6 wherein said exhaust gas and the resulting condensation products contain little or no alkali.
8. Process as in claim 1 wherein said solid, dehydrated waste substance in incineration ash.
9. Process as in claim 1 further comprising purifying the exhaust gas emerging from the batch to be melted, said purifying comprising removing dust from said exhaust gas and reintroducing said dust into the batch to be melted. A process for the conversion of solid, dehydrated waste substances into g.ass substantially as hereinbefore described with reference to the accompanying drawings. DATED this 17 March 1992 CARTER SMITH BEADLE Fellows Institute of Patent Attorneys of Australia Patent Attorneys for the Applicant: BETREILIGUNGEN SORG GMBH CO. KG and METALLGESELLSCHAFT A.G. 6 btc/13/016.res 92 3 17 it I 1 i
Applications Claiming Priority (6)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE3830899 | 1988-09-10 | ||
DE3830899 | 1988-09-10 | ||
DE3841889A DE3841889A1 (en) | 1988-09-10 | 1988-12-13 | Process for converting solid, substantially anhydrous waste materials into the glass form (vitrification) and apparatus for carrying out the process |
DE3841889 | 1988-12-13 | ||
DE3904613 | 1989-02-16 | ||
DE19893904613 DE3904613A1 (en) | 1989-02-16 | 1989-02-16 | Environmentally friendly process for converting solid waste materials into glass form (vitrification) |
Publications (2)
Publication Number | Publication Date |
---|---|
AU4106089A AU4106089A (en) | 1990-03-15 |
AU624414B2 true AU624414B2 (en) | 1992-06-11 |
Family
ID=27198209
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
AU41060/89A Ceased AU624414B2 (en) | 1988-09-10 | 1989-09-04 | A process and apparatus for the conversion of solid waste into glass |
Country Status (6)
Country | Link |
---|---|
EP (1) | EP0359003B1 (en) |
JP (1) | JPH07102977B2 (en) |
AU (1) | AU624414B2 (en) |
DE (1) | DE58906363D1 (en) |
DK (1) | DK169057B1 (en) |
ES (1) | ES2047074T3 (en) |
Families Citing this family (24)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4977837A (en) * | 1990-02-27 | 1990-12-18 | National Recovery Technologies, Inc. | Process and apparatus for reducing heavy metal toxicity in fly ash from solid waste incineration |
CH680198A5 (en) * | 1990-07-06 | 1992-07-15 | Sulzer Ag | |
DE4035777A1 (en) * | 1990-11-08 | 1992-05-14 | Noell Gmbh | METHOD FOR THE DISPOSAL OF DUST CONTAINING TOXIC HEAVY METALS, TOXIC ORGANIC MATERIALS AND SIMILAR COMPOUNDS |
DE4111385A1 (en) * | 1991-04-09 | 1992-10-15 | Leybold Ag | Filter dust smelting with reduced electrode erosion - in which electrodes are inserted into glass from above into mixt. of dust and additives |
DE4112162C1 (en) * | 1991-04-13 | 1992-07-30 | Beteiligungen Sorg Gmbh & Co Kg, 8770 Lohr, De | |
WO1993001141A1 (en) * | 1991-07-11 | 1993-01-21 | Schoenhausen Horst | Process and device for the safe disposal of toxic residues |
SK291691A3 (en) * | 1991-09-23 | 1995-07-11 | Inglas S R O | Vitrification method of powdered waste, mainly light ash from refuse destructing plants |
FR2684573B1 (en) * | 1991-12-05 | 1994-10-07 | Mediterranee Const Ind | PROCESS FOR THE TREATMENT OF SOLID RESIDUES FROM THE PURIFICATION OF FUMES FROM AN INCINERATION FURNACE TO PERFORM FOR THEM, FOR VITRIFICATION OR MELTING, AND ITS INSTALLATION. |
DE4301353C1 (en) * | 1993-01-20 | 1994-05-26 | Sorg Gmbh & Co Kg | Method of vitrifying waste material contg. high proportion of carbon - with heat generated by burning gases used to heat up material fed to appts. |
FR2719793A1 (en) * | 1993-07-30 | 1995-11-17 | Cnim | Vitrification of solid residues for incineration |
FR2708490B1 (en) * | 1993-07-30 | 1995-11-10 | Cnim | Vitrification process for solid residues from the incineration of household and / or industrial waste, device for the implementation of this process and product from this process. |
FR2711077B1 (en) * | 1993-10-11 | 1996-01-05 | Delot Int Fours | Waste vitrification process, and vitrification furnace. |
DE4424950C2 (en) * | 1994-07-14 | 1997-02-13 | Flachglas Ag | Device for withdrawing gaseous products and for draining the glass melt and their use |
FR2726492B1 (en) * | 1994-11-09 | 1997-01-17 | Electricite De France | ADJUVANT AND PROCESS FOR THE STABILIZATION OF WASTE CONTAINING METAL ELEMENTS |
KR0158083B1 (en) * | 1995-06-07 | 1998-12-15 | 신재인 | Vitrification method of high radioactive waste material using flyash |
FR2746037B1 (en) * | 1996-03-13 | 1998-05-15 | PROCESS FOR THE VITRIFICATION TREATMENT OF ASBESTOSED WASTE, PARTICULARLY FROM THE BUILDING, AND INSTALLATION FOR CARRYING OUT SAID METHOD | |
JPH11201439A (en) * | 1998-01-12 | 1999-07-30 | Ishikawajima Harima Heavy Ind Co Ltd | Ash-melting furnace |
EP1048899A4 (en) * | 1998-09-11 | 2004-09-22 | Jfeengineering Corp | Method and device for melt-treating incineration residue containing salts |
FR2816529B1 (en) * | 2000-11-13 | 2003-09-05 | Rech S De Traitement Des Deche | PROCESS FOR TREATING INCINERATION RESIDUES AND INSTALLATION FOR CARRYING OUT SUCH A PROCESS |
EP1390308B1 (en) * | 2001-05-16 | 2005-08-03 | Owens Corning | Exhaust positioned at the downstream end of a glass melting furnace |
FR2870758B1 (en) * | 2004-05-26 | 2006-08-04 | Commissariat Energie Atomique | METHOD FOR COMBUSTION AND COMPLETE OXIDATION OF THE MINERAL FRACTION OF A TREATED WASTE IN A DIRECT COMBUSTION-VITRIFICATION APPARATUS |
CN107089795B (en) * | 2017-03-29 | 2021-09-14 | 天津壹鸣环境科技股份有限公司 | Method for melting treatment and resource utilization of household garbage incineration fly ash electrode |
DE102018108418A1 (en) * | 2018-04-10 | 2019-10-10 | Schott Ag | Process for the preparation of glass products and apparatus suitable for this purpose |
CN113289441A (en) * | 2021-06-04 | 2021-08-24 | 中国矿业大学 | Device and method for purifying domestic garbage cracking gasification tail gas |
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US4632690A (en) * | 1985-06-04 | 1986-12-30 | Colwell Jr Robert E | Hazardous waste removal method and apparatus |
US4666490A (en) * | 1986-02-12 | 1987-05-19 | Drake Ronald N | Aqueous waste vitrification process and apparatus |
US4678493A (en) * | 1983-11-21 | 1987-07-07 | King Taudevin & Gregson (Holdings) Limited | Vitrification of asbestos waste |
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DE2631220C2 (en) * | 1976-07-12 | 1986-03-06 | Sorg-GmbH & Co KG, 8770 Lohr | Melting furnace for melting radioactive substances in glass |
US4652289A (en) * | 1984-11-26 | 1987-03-24 | Hydro-Quebec | Purification of effluent gases |
DE3631729A1 (en) * | 1986-09-18 | 1988-03-24 | Gea Luftkuehler Happel Gmbh | Process for the catalytic conversion of nitrogen oxides in the flue gases arising in glass manufacture |
-
1989
- 1989-08-25 EP EP89115675A patent/EP0359003B1/en not_active Expired - Lifetime
- 1989-08-25 DE DE89115675T patent/DE58906363D1/en not_active Expired - Fee Related
- 1989-08-25 ES ES89115675T patent/ES2047074T3/en not_active Expired - Lifetime
- 1989-09-04 AU AU41060/89A patent/AU624414B2/en not_active Ceased
- 1989-09-07 DK DK441489A patent/DK169057B1/en not_active IP Right Cessation
- 1989-09-11 JP JP1235478A patent/JPH07102977B2/en not_active Expired - Lifetime
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4678493A (en) * | 1983-11-21 | 1987-07-07 | King Taudevin & Gregson (Holdings) Limited | Vitrification of asbestos waste |
US4632690A (en) * | 1985-06-04 | 1986-12-30 | Colwell Jr Robert E | Hazardous waste removal method and apparatus |
US4666490A (en) * | 1986-02-12 | 1987-05-19 | Drake Ronald N | Aqueous waste vitrification process and apparatus |
Also Published As
Publication number | Publication date |
---|---|
DK441489A (en) | 1990-03-11 |
AU4106089A (en) | 1990-03-15 |
JPH07102977B2 (en) | 1995-11-08 |
JPH02175620A (en) | 1990-07-06 |
DE58906363D1 (en) | 1994-01-20 |
EP0359003A3 (en) | 1991-01-16 |
ES2047074T3 (en) | 1994-02-16 |
DK441489D0 (en) | 1989-09-07 |
EP0359003A2 (en) | 1990-03-21 |
EP0359003B1 (en) | 1993-12-08 |
DK169057B1 (en) | 1994-08-08 |
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