DK175803B1 - Method for treating fly ash and device for use therein - Google Patents
Method for treating fly ash and device for use therein Download PDFInfo
- Publication number
- DK175803B1 DK175803B1 DK199401166A DK116694A DK175803B1 DK 175803 B1 DK175803 B1 DK 175803B1 DK 199401166 A DK199401166 A DK 199401166A DK 116694 A DK116694 A DK 116694A DK 175803 B1 DK175803 B1 DK 175803B1
- Authority
- DK
- Denmark
- Prior art keywords
- water
- fly ash
- mixture
- consistency
- ash
- Prior art date
Links
- 239000010881 fly ash Substances 0.000 title claims description 24
- 238000000034 method Methods 0.000 title claims description 17
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 30
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 28
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 claims description 23
- 239000002956 ash Substances 0.000 claims description 21
- 239000000292 calcium oxide Substances 0.000 claims description 18
- 239000000203 mixture Substances 0.000 claims description 16
- 238000002156 mixing Methods 0.000 claims description 12
- 230000008569 process Effects 0.000 claims description 10
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims description 6
- 235000012255 calcium oxide Nutrition 0.000 description 16
- 239000000446 fuel Substances 0.000 description 15
- 239000008187 granular material Substances 0.000 description 11
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 10
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 10
- 235000011941 Tilia x europaea Nutrition 0.000 description 10
- 239000004571 lime Substances 0.000 description 10
- 239000011593 sulfur Substances 0.000 description 10
- 238000006243 chemical reaction Methods 0.000 description 9
- 229910052717 sulfur Inorganic materials 0.000 description 9
- 235000019738 Limestone Nutrition 0.000 description 8
- 235000011132 calcium sulphate Nutrition 0.000 description 8
- 239000006028 limestone Substances 0.000 description 8
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 7
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 6
- 239000011575 calcium Substances 0.000 description 6
- 238000002485 combustion reaction Methods 0.000 description 6
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 5
- 230000015572 biosynthetic process Effects 0.000 description 5
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 4
- 229910052791 calcium Inorganic materials 0.000 description 4
- 229910052925 anhydrite Inorganic materials 0.000 description 3
- 239000001175 calcium sulphate Substances 0.000 description 3
- 239000003245 coal Substances 0.000 description 3
- 238000005469 granulation Methods 0.000 description 3
- 230000003179 granulation Effects 0.000 description 3
- 229910052602 gypsum Inorganic materials 0.000 description 3
- 239000010440 gypsum Substances 0.000 description 3
- 239000003415 peat Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 235000002918 Fraxinus excelsior Nutrition 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 238000001354 calcination Methods 0.000 description 2
- 235000010216 calcium carbonate Nutrition 0.000 description 2
- 229910000019 calcium carbonate Inorganic materials 0.000 description 2
- 239000004567 concrete Substances 0.000 description 2
- 238000006477 desulfuration reaction Methods 0.000 description 2
- 230000023556 desulfurization Effects 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 238000002386 leaching Methods 0.000 description 2
- 238000011068 loading method Methods 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
- 239000004449 solid propellant Substances 0.000 description 2
- 239000002023 wood Substances 0.000 description 2
- 241000196324 Embryophyta Species 0.000 description 1
- 241001122767 Theaceae Species 0.000 description 1
- 239000000853 adhesive Substances 0.000 description 1
- 230000001070 adhesive effect Effects 0.000 description 1
- 229910052783 alkali metal Inorganic materials 0.000 description 1
- 150000001340 alkali metals Chemical class 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 238000000151 deposition Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000010410 dusting Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 230000020169 heat generation Effects 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 238000003754 machining Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000004886 process control Methods 0.000 description 1
- 238000011946 reduction process Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 230000019635 sulfation Effects 0.000 description 1
- 238000005670 sulfation reaction Methods 0.000 description 1
- 229910052815 sulfur oxide Inorganic materials 0.000 description 1
- 239000008400 supply water Substances 0.000 description 1
- 229920002994 synthetic fiber Polymers 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 230000032258 transport Effects 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 238000009736 wetting Methods 0.000 description 1
- 239000010803 wood ash Substances 0.000 description 1
Classifications
-
- 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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
- B01D53/50—Sulfur oxides
-
- 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
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2/00—Lime, magnesia or dolomite
- C04B2/02—Lime
- C04B2/04—Slaking
-
- 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
- A62D2101/08—Toxic combustion residues, e.g. toxic substances contained in fly ash from waste incineration
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- Ceramic Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Materials Engineering (AREA)
- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- Organic Chemistry (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Structural Engineering (AREA)
- General Health & Medical Sciences (AREA)
- Toxicology (AREA)
- Business, Economics & Management (AREA)
- Emergency Management (AREA)
- Processing Of Solid Wastes (AREA)
Description
DK 175803 B1 iDK 175803 B1 i
Den foreliggende opfindelse angår en fremgangsmåde til granulering af flyveaske indeholdende calciumoxid og eventuelt calciumsulfat ved blanding med vand, hvorved asken granuleres til en på enkel måde håndterbar og deponerbar form under læskning af calciumoxidet. Ifølge opfindelsen sker blandingen ved fritfaldsblanding ' 5 under tilsætning af vand i forhold til askemængden. Opfindelsen angår tillige en indretning til anvendelse ved gennemførelse af fremgangsmåden, hvilken indretning omfatter organer til afføling af blandingens konsistens og organer til at styre vandtilførslen i afhængighed deraf.The present invention relates to a process for granulating fly ash containing calcium oxide and optionally calcium sulfate by admixing with water, whereby the ash is granulated to an easily manageable and disposable form while grinding the calcium oxide. According to the invention, the mixture is effected by free-fall mixture 5 with the addition of water relative to the amount of ash. The invention also relates to a device for use in carrying out the method, which comprises means for sensing the consistency of the mixture and means for controlling the water supply in dependence thereof.
10 Varmekedler af FB-typen, dvs. sådanne, der gør brug af et fluidiserende leje, anvendes i bl.a. kraftvarmeværker. Forbrændingen sker i disse med brændselspartiklerne i et leje af fint sand, som holdes svævende ved, at luft indblæses med høj hastighed. Lejet får derved væskelignende egenskaber.10 FB type boilers, ie. those which use a fluidizing bed are used in e.g. CHP. The combustion takes place in these with the fuel particles in a bed of fine sand, which is kept floating by the air being blown at high speed. The bearing thereby has liquid-like properties.
15 En af de store fordele ved forbrænding i et fluidiserende leje er, at man kan fyre med brændsler med forskellige egenskaber i samme kedel. I FB-kedler fyrer man således med bl.a. kul, træ, tørv og andre faste brændsler såsom affald enten hver for sig eller i forskellige kombinationer.15 One of the great advantages of combustion in a fluidizing bed is that you can fire with fuels with different properties in the same boiler. In FB boilers, one thus fires with e.g. coal, wood, peat and other solid fuels such as waste either individually or in different combinations.
20 En anden stor fordel ved forbrænding i et fluidiserende leje er, at udslippet af svovl- og nitrogenoxider kan begrænses på en enklere måde end i andre typer forbrændingsanlæg. Specielt kul og tørv indeholder svovl, hvorved man kan binde svovlen ved at tilsætte formalet kalksten til lejet. Kalkstenen reagerer med den dannede svovldioxid for at danne calciumsulfat.Another great advantage of combustion in a fluidising bed is that the emission of sulfur and nitrogen oxides can be reduced in a simpler way than in other types of combustion plants. Particularly coal and peat contain sulfur, whereby the sulfur can be bonded by adding ground limestone to the bed. The limestone reacts with the sulfur dioxide formed to form calcium sulfate.
2525
Oxidationen af luftens nitrogen til nitrogenoxid er temperaturafhængig. Den forholdsvis lave forbrændingstemperatur i FB-kedler, 800° - 900°C, medfører, at udslippet af nitrogenoxid kan holdes på et lavt niveau. Den normale forbrændingstemperatur i andre typer kedler er over 1000°C.The oxidation of the nitrogen of the air to nitric oxide is temperature dependent. The relatively low combustion temperature in FB boilers, 800 ° - 900 ° C, means that the emission of nitric oxide can be kept at a low level. The normal combustion temperature in other types of boilers is above 1000 ° C.
30 '30 '
Ved store kedler opnås der imidlertid store mængder flyveaske, som der skal tages vare på, hvilket medfører såvel praktiske problemer som arbejdsmiljøproblemer.However, with large boilers, large quantities of fly ash are obtained, which must be taken care of, which leads to practical problems as well as working environment problems.
Ved fyring med svovlholdige brændsler kommer flyveasken således til at indeholde 35 calciumsulfat, et overskud af tilsat kalk i form af CaC03 og i fyrstedet brændt kalk,Thus, when fired with sulfur-containing fuels, the fly ash will contain 35 calcium sulfate, an excess of added lime in the form of CaCO 3 and lime burnt in the fireplace,
I DK 175803 B1 II DK 175803 B1 I
CaO. Kalkstenen tilføres som nævnt for at minimere svovlemissionerne. Kalkstens- ICaO. As mentioned, the limestone is added to minimize sulfur emissions. Limestone I
mængden bestemmes af brændslets svovlindhold og forholdet Ca/S, som normalt Ithe amount is determined by the sulfur content of the fuel and the ratio of Ca / S, which usually I
er 1,5 - 3. Hvis brændslet eller brændselsblandingen i sig selv indeholder en stor Iis 1.5 - 3. If the fuel or fuel mixture itself contains a large I
andel kalk, kan indfødningen af tilsætningsskalk reduceres. Der kræves ligeledes Iproportion of lime, the addition of lime can be reduced. Also required
5 mindre eller ingen kalktilsætning ved brændsler med et lavt svovlindhold. Den til- I5 Minor or no lime addition for low sulfur fuels. It adds
satte kalk udgøres af CaC03. Nar CaC03 opvarmes til temperaturer over 800°C, Iset lime is constituted by CaCO3. When CaCO 3 is heated to temperatures above 800 ° C, I
gennemgår den en kalcineringsproces. Reaktionen forløber i henhold til: - Iit undergoes a calcination process. The reaction proceeds according to: -
CaC03(s).......> CaO(s) + C02(g). ICaCO3 (s) .......> CaO (s) + CO2 (g). IN
Det ved kalcineringen dannede calciumoxid kan ved tilstedeværelse af oxygen rea- IThe calcium oxide formed during the calcination can be reacted in the presence of oxygen
gere med svovldioxid til dannelse af calciumsulfat: Isulfur dioxide forming calcium sulphate: I
CaO(s) + S02(g) + y202 ......> CaS04(s). ICaO (s) + SO2 (g) + y2 O2 ......> CaSO4 (s). IN
Denne reaktion benævnes sulfatering. IThis reaction is called sulfation. IN
Mange parametre indgår i afsvovlingsprocessen. Dette medfører, at den tilførte IMany parameters are part of the desulphurisation process. This results in the supply of I
kalksten ikke kan udnyttes 100%, men sædvanligvis kun 20-60%. En af de vig- 20 tigste styreparametre er temperaturen i fyrstedet, hvilken kan varieres mellem 800Limestone cannot be utilized 100%, but usually only 20-60%. One of the most important control parameters is the temperature of the fireplace, which can be varied between 800
og 900°C. Iand 900 ° C. IN
Afsvovlingsgraden kan betragtes som en kappestrid mellem to konkurrerende pro- IThe degree of desulfurization can be regarded as a clash between two competing pro- I
cesser, nemlig den ovenfor angivne Icesses, namely the above I
oxygenreduktionsproces, som giver calciumsulfat, og følgende reaktion, som er i Ioxygen reduction process which gives calcium sulfate and the following reaction which is in I
ligevægt med den: Iequilibrium with it: I
2 CaS04(s) + CO/H2{g) ......> 2 CaO(s) + 2 S02 + C02/H20(g). I2 CaSO4 (s) + CO / H2 (g) ......> 2 CaO (s) + 2SO2 + CO2 / H2O (g). IN
Begge processerne kan studeres i et stabilitetsdiagram. IBoth processes can be studied in a stability diagram. IN
Såfremt udnyttelsesgraden af den tilførte kalksten er ringe, udskilles en stor IIf the utilization rate of the applied limestone is low, a large I is excreted
mængde brændt kalk fra røggasserne i kedlens elektrofilter og genfindes således i Iamount of burnt lime from the flue gases in the boiler's electric filter and thus recovered in I
35 flyveasken. Denne kan tillige indeholde CaO hidrørende fra i brændslet naturligt I35 fly ash. This may also contain CaO derived from the fuel naturally I
DK 175803 B1 3 forekommende calcium. Den brændte kalk bliver senere læsket ved udtagningen ved befugtning af asken. Den kemiske reaktion ved læskning af brændt kalk er:DK 175803 B1 3 occurring calcium. The burnt lime is later crushed by the removal of the ash by wetting the ash. The chemical reaction of crushed lime is:
CaO + H20.......> Ca(OH)2.CaO + H2O .......> Ca (OH) 2.
55
Denne reaktion finder sted under stærk varmeudvikling, som medfører såvel håndterings- som arbejdsmiljøproblemer.This reaction takes place during strong heat development, which causes both handling and working environment problems.
Mængden af CaO i flyveasken bør således begrænses. På den anden side tilstræber 10 man en vidtgående afsvovling, hvilket indebærer, at man normalt overdoserer tilsætningen af kalksten, hvilket ligeledes giver et overskud af CaO.Thus, the amount of CaO in the fly ash should be limited. On the other hand, 10 extends desulphurisation, which means that one usually overdoses the addition of limestone, which also gives an excess of CaO.
I dag transporteres sædvanligvis den i elektrofilteret udskilte flyveaske, som udgør ca. 85% af den totale askemængde, via et pneumatisk transportsystem til en eller 15 flere siloer: Derfra lastes de ofte via en celleføder og en befugtningsindretning på lastbiler. Befugteren kan bestå af et langstrakt trug med et padleværk, som blander asken med fra dyser indsprøjtet vand og transporterer blandingen til en slisk, hvorfra den lastes på et lastbillad i form af en klæbrig masse.Today, the fly ash separated in the electro filter is usually transported, which constitutes approx. 85% of the total ash volume, via a pneumatic conveyor system to one or 15 more silos: From there they are often loaded via a cell feeder and a humidifier on trucks. The humidifier may consist of an elongated trough with a paddle, which mixes the ashes with water injected with nozzles and transports the mixture to a sludge, from which it is loaded onto a load sheet in the form of a sticky mass.
20 Kravet til det udlastede produkt er, at det af arbejdsmiljøgrunde ikke skal støve og heller ikke skal være for "blødt", da man derved får store problemer som følge af vedhæftning på ladets overflader eller som følge af, at med aske blandet vand lækker fra lastefladen. Aske fra forskellige brændsler har helt forskellig evne til at binde vand, hvilket medfører vanskeligheder med at opnå masser med den "rigtige" 25 konsistens.20 The requirement for the unloaded product is that it must not be dusty or too "soft" for work environment reasons, as this will cause major problems as a result of adhesion to the surface of the drawer or as a result of ash mixed water leaking from loading area. Ashes from different fuels have completely different ability to bind water, causing difficulties in obtaining masses with the "right" consistency.
Som følge af den til mindskning af støvdannelsen nødvendige vandindblanding forårsager flyveaskens indhold af brændt kalk og calciumsulfat kemiske reaktioner såsom læskning af den brændte kalk med kraftig varmeudvikling og dannelse af gips, 30 hvorved det her tilstræbes, at vandmolekyler bindes krystallinsk til CaSCVmoleky-lerne.Due to the water mixing required to reduce the dust formation, the fly ash content of burnt lime and calcium sulfate causes chemical reactions such as leaching of the burnt lime with vigorous heat generation and gypsum formation, thereby seeking to bind water molecules crystalline to the CaSCV molecules.
Kalklæskningen og gipsdannelsen medfører, at massen brænder sammen og hæfter fast på ladet, hvilket medfører store problemer ved tipningen, samt aflejres på 35 blandetruget og det deri indførte padleværk. Dette medfører behov for stor manuel _ _The limescale and gypsum formation causes the pulp to collapse and adhere to the ladle, causing major problems with the tipping, as well as depositing on the mixing trough and the padding introduced therein. This leads to the need for a large manual _ _
I DK 175803 B1 II DK 175803 B1 I
IIN
I arbejdsindsats under vanskelige arbejdsmiljøforhold, da tungt værktøj skal hånd- IIn work effort in difficult working environment conditions, as heavy tools must be hand- I
I teres for at fjerne det vedhæftende materiale samtidigt med, at der opstår kraftig IIteres to remove the adhesive while causing strong I
I støvdannelse under arbejdet.In dusting during work.
I 5 Den under læskningsprocessen opstående varmeudvikling, som når sit maksimum II 5 The heat generated during the curing process, which reaches its maximum I
I 5-8 minutter efter vandtilsætningen, medfører i visse tilfælde ved de i dag anvend- IFor 5-8 minutes after the addition of water, in some cases at the current use I
I te metoder, at der i den bløde masse på ladet dannes dampbobler, som stiger opad IIn tea methods, in the soft mass of the charge, steam bubbles are formed which rise upwards
I og afstedkommer udbrud, hvorved store dele af lasten slynges ud fra lastbilladet. IOutbreaks occur and cause large parts of the cargo to be thrown out from the cargo image. IN
I Dette medfører alvorlig fare for ulykker og tillige miljøproblemer. II This poses a serious risk of accidents and also environmental problems. IN
I 10 II 10 I
I Hovedformålet med den foreliggende opfindelse er at tilvejebringe en teknik til be- IThe main object of the present invention is to provide a technique for use
I handling af flyveaske af den aktuelle type på en sådan måde, at de uønskede kon- IIn the act of fly ash of the current type in such a way that the undesirable con- I
I sekvenser af de kemiske reaktioner elimineres, og at disse i stedet på en fordelag- IIn sequences of the chemical reactions are eliminated and that instead of on an advantageous day
I tig mide benyttes til at forvandle asken til en på enkel måde håndterbar og depo- IThis method is used to transform the ash into a simple, manageable and landfill
I 15 nerbar form, som bl.a. fjerner de ovenfor nævnte miljørisici. IIn removable form, such as removes the environmental risks mentioned above. IN
I Til grund for opfindelsen ligger den indsigt, at dette mål kan opnås ved at bearbej- IIn accordance with the invention lies the insight that this object can be achieved by machining
I de flyveasken, inden den transporteres videre, så den danner et tørt granulat, som IIn the fly ash before it is transported further to form a dry granulate such as you
I ikke klæber på de overflader, som det kommer i kontakt med, og ved hvilket var- IYou do not stick to the surfaces with which it comes in contact, and on which you were
I 20 meudviklingen ikke kan bevirke indesluttede bobler, som risikerer at briste. I ste- IIn the 20 meevelopment can not cause entrapped bubbles, which may burst. I stand- I
I det kommer varme dampstrømme til at kunne passere gennem granulatet udenIn it, hot vapor streams will be able to pass through the granules without
I problemer. Granulatets større berøringsflade med den omgivende luft medfører IIn problems. The larger contact surface of the granulate with the surrounding air results in I
endvidere en mere effektiv afkøling af granulatet, hvilket yderligere reducerer pro- Imore efficient cooling of the granulate, further reducing the pro- I
I blemerne. IIn the blisters. IN
I II I
I Til dannelse af granulatet kan man benytte reaktionen i forbindelse med læskning- IFor the formation of the granulate, the reaction may be used in conjunction with leaching
I en af kalken ved blanding af flyveasken med vand og den gipsdannende virkning, IIn one of the lime by mixing the fly ash with water and the gypsum-forming effect, I
I som opnås derved, når asken indeholder calciumsulfat. IYou are thereby obtained when the ash contains calcium sulphate. IN
I 30 Man kan ikke opnå nogen granulering ved den tidligere anvendte blanding af flyve- II No granulation can be obtained from the previously used mixture of aircraft I
I aske og vand i en trugform eller lignende. Hertil kræves der ifølge den foreliggende IIn ash and water in a trough form or similar. According to the present invention, this is required
I opfindelse, at flyveasken udsættes for en såkaldt fritfaldsblanding under tilsætning IIn the invention, the fly ash is subjected to a so-called free fall mixture during addition I
I af vand i forhold til askemængden, så det indeholdte calciumoxid læskes, og der IOf water in proportion to the amount of ash so that the contained calcium oxide is quenched and there
sker en dannelse af gips ved forekomst af calciumsulfat, hvilke reaktioner som føl- Igypsum formation occurs upon the occurrence of calcium sulphate, which reactions as follows
I 35 ge af fritfaldsblandingen giver anledning til granulering af asken. IIn 35 g of the free-fall mixture gives rise to granulation of the ash. IN
5 DK 175803 B15 DK 175803 B1
Ved hjælp af en nøjagtig regulering af vandmængden kan man således ved hjælp af fremgangsmåden afstedkomme en granulering af asken, hvilket granulat siden på enkel måde kan transporteres og deponeres. Afhængigt af askens kemiske sam-’ 5 mensætning i øvrigt kan granulatet eventuelt føres tilbage til naturen eller udnyttes i fx bygningsmaterialer.Thus, by means of an accurate regulation of the amount of water, a granulation of the ash can be effected by means of the method, which granules can then be easily transported and deposited. Depending on the chemical composition of the ash in general, the granulate may possibly be returned to nature or used in, for example, building materials.
Blandingen af flyveaske og vand kan ske portionsvis, hvorved der passende kan ske en afføling af blandingens konsistens, og vandtilførslen styres afhængigt heraf.The mixing of fly ash and water can be done in portions, whereby a consistency of the consistency of the mixture can be sensed and the water supply is controlled accordingly.
1010
Det særligt kendetegnende ved en indretning til anvendelse ved gennemførelse af fremgangsmåden fremgår af de efterfølgende patentkrav.The particular characteristic of a device for use in carrying out the method is apparent from the following claims.
Opfindelsen vil blive nærmere beskrevet nedenfor under henvisning til den som ek-15 sempel på vedlagte tegning viste udførelsesform for en indretning til behandling af flyveaske.The invention will be described in more detail below with reference to the exemplary embodiment of a fly ash processing device shown in the accompanying drawing.
Med tallene 1 og 2 betegnes to siloer til modtagelse af flyveasken fra en stor, ikke vist, med fast brændsel fyret kedel, som fx kan være af CFB-typen, dvs. arbejden-20 de med et cirkulerende, fluidiserende leje. Flyveasken har i tør tilstand en finheds-grad, som omtrent modsvarer cement med en overfladevægt på 400m2/kilo. ud over de i brændslerne indgående mineraler indeholder asken tillige sand fra det fluidiserende leje samt Cao og CaS04 ved tilsætning af kalk til afsvovling. Askens sammensætning kommer til at variere betydeligt afhængigt af, hvilket brændsel 25 eller hvilke brændselskombinationer benyttes. Ved benyttelse af træbrændsel, som indeholder små mængder svovl, behøves der kun en lille eller ingen tilsætning af kalk. Brændslet indeholder imidlertid relativt store mængder alkalimetaller, hvorfor også aske fra træbrændsel vil indeholde calcium.Numbers 1 and 2 denote two silos for receiving the fly ash from a large solid fuel fired boiler, which may not be CFB-type, e.g. working with a circulating fluidizing bed. The fly ash has a degree of fineness which roughly corresponds to cement with a surface weight of 400 m2 / kg. in addition to the minerals contained in the fuels, the ash also contains sand from the fluidizing bed as well as Cao and CaSO4 when adding lime to desulphurisation. The composition of the ash will vary considerably depending on which fuel or combinations of fuel are used. When using wood fuel containing small amounts of sulfur, little or no addition of lime is needed. However, the fuel contains relatively large amounts of alkali metals, which is why wood ash will also contain calcium.
30 Ved fyring med torv, som har et højt svovlindhold, tilsættes der meget kalksten, hvorfor calciummængden i asken bliver stor, da også brændslet i sig selv indeholder calcium. Asken vil som afsvovlingsprodukt tillige komme til at indeholde CaS04. Dette gælder også kul, som har et højt svovlindhold, hvilket kræver en stor mængde kalksten. \ 3530 When burning with peat, which has a high sulfur content, a lot of limestone is added, which is why the amount of calcium in the ash becomes large, since the fuel itself contains calcium. The ash will also contain CaSO 4 as a desulfurization product. This also applies to coal which has a high sulfur content, which requires a large amount of limestone. \ 35
I DK 175803 B1 II DK 175803 B1 I
I 6 II 6 I
Flyveasken føres fra siloerne via en tilhørende transportør 3, 4 til en vægt 5, som IThe fly ash is passed from the silos via an associated conveyor 3, 4 to a weight 5 which I
I udvejer en pi forhånd bestemt portion af flyveaske. Denne føres via yderligere en IYou weigh a predetermined portion of fly ash. This is conducted via an additional I
transportør 6 til en blandemaskine 7, som er koblet til en vandtilførselsledning 8. Iconveyor 6 to a mixing machine 7 connected to a water supply line 8. I
5 Blandemaskinen 7 kan i princippet være udført som en til betonfremstilling anvendt I5 The mixing machine 7 can in principle be designed as one used for concrete production
I fritfaldsblandemaskine, dvs. omfatte en roterende tromle med skovle, som løfter IIn free-fall mixing machine, ie. include a rotating drum with vanes which lift I
I massen op og leder den falde frit ned. En kendt betonblandemaskine kan modifi-In the mass up and down it falls freely down. A known concrete mixer can be modified
I ceres til anvendelse til dette formål ved at fjerne diagonalskovlene og belægge ITo be used for this purpose, remove the diagonal blades and coat I
I tromlen indvendigt med et syntetisk materiale. Skovlene er derved udført således, IInside the drum with a synthetic material. The vanes are thus designed as follows: I
I 10 at massen blandes ved rotation i den ene retning, medens de ved rotation i den IIn that the mass is mixed by rotation in one direction, while in rotation in that I
I anden retning føder massen til ved en udløbsåbning beliggende tømmeskovle. IIn the other direction, the pulp feeds at a discharge bucket located at an outlet opening. IN
I Til forvandling af den i blandemaskinen med vand fugtede masse til granulatform II For the transformation of the pulp wetted mass into granular form I into the water mixer
I kræves, at vandtilførslen reguleres nøjagtigt i afhængighed af den aktuelle flyve- IYou are required to regulate the water supply precisely depending on the actual flight I
I 15 askes egenskaber. IIn 15 ash properties. IN
I Hertil kan man starte blandemaskinen efter tilsætning af en bestemt mængde IIn addition, the mixing machine can be started after adding a certain amount of I
flyveaske, som gennemfugtes med en første vandtilsætning. Derefter tilføres der I vand meget langsomt under iagttagelse af massens konsistensforandring. Dettefly ash, which is moistened with an initial water addition. Then, water is added very slowly, observing the change in mass of the pulp. This
I 20 kan med fordel ske under registrering af det aktuelle drivmoment, som tilføres II 20 can advantageously be made during recording of the current torque applied to I
I blandemaskinen, hvilket udgør et mål for massens aktuelle konsistens. Når massen IIn the mixer, which is a measure of the actual consistency of the pulp. When the mass I
I begynder at granuleres for gradvist helt at gå over i et tørt granulat, noteres den IYou begin to granulate to gradually completely turn into a dry granule, note it
I totalt tilførte vandmængde. IIn total water supply. IN
I 25 Efter et sådant forløb, kan de kommende portioner behandles automatisk ved sty-After such a course, the future portions can be processed automatically by
I ring fra en mikrodatamat, som er blevet programmeret med de ved det første for- , IIn the ring from a microcomputer which has been programmed with those of the first device, I
I løb opnåede værdier. Det fra blandemaskinen udledte materiale består således af IObtained values in race. The material derived from the mixer thus consists of I
I tørt flyveaskegranulat, som kan tippes direkte ned på et lastbillad og efter trans- IIn dry fly ash granules, which can be tipped directly onto a truck and after trans-
I port til den ønskede deponering på enkel måde kan tippes af ladet. Ved lastningen .. IIn port for the desired deposit can easily be tipped off the charge. When loading .. I
I 30 kan chaufføren indlæse den ønskede lastvægt i den til styring af processen an- IAt 30, the driver can load the desired load weight into the process control unit
I vendte mikrodatamat, hvorefter denne udvejer en passende portion flyveaske og II turned the microcomputer, after which it weighed an appropriate portion of fly ash and I
I tilfører vand afhængigt af massens konsistens, dvs. det på sædvanlig måde aflæste IYou supply water depending on the consistency of the mass, ie. I read it in the usual way
I drivmoment. Når portionen er forvandlet til et tørt granulat, tippes dette automa- IIn torque. When the portion is turned into a dry granule, this is automatically tipped
I tisk ned på ladet, hvorefter næste lastbil kan køre frem og indprogrammere en ny IYou tic down the drawer, after which the next truck can drive forward and program a new one
I 35 lastmængde. IIn 35 cargo load. IN
Claims (5)
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
SE9303297 | 1993-10-08 | ||
SE9303297A SE511188C2 (en) | 1993-10-08 | 1993-10-08 | Appts. for treating fly ash contg. calcium oxide obtd. during the heating of sulphur rich fuels |
Publications (2)
Publication Number | Publication Date |
---|---|
DK116694A DK116694A (en) | 1995-04-09 |
DK175803B1 true DK175803B1 (en) | 2005-02-28 |
Family
ID=20391354
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
DK199401166A DK175803B1 (en) | 1993-10-08 | 1994-10-07 | Method for treating fly ash and device for use therein |
Country Status (3)
Country | Link |
---|---|
DK (1) | DK175803B1 (en) |
FI (1) | FI112444B (en) |
SE (1) | SE511188C2 (en) |
-
1993
- 1993-10-08 SE SE9303297A patent/SE511188C2/en not_active IP Right Cessation
-
1994
- 1994-10-07 DK DK199401166A patent/DK175803B1/en not_active IP Right Cessation
- 1994-10-07 FI FI944694A patent/FI112444B/en not_active IP Right Cessation
Also Published As
Publication number | Publication date |
---|---|
FI112444B (en) | 2003-12-15 |
SE9303297D0 (en) | 1993-10-08 |
FI944694A (en) | 1995-04-09 |
SE9303297L (en) | 1995-04-09 |
SE511188C2 (en) | 1999-08-23 |
DK116694A (en) | 1995-04-09 |
FI944694A0 (en) | 1994-10-07 |
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