LT3153B - Nonwaste method for anionite regenerating of chlorine ionite filter - Google Patents
Nonwaste method for anionite regenerating of chlorine ionite filter Download PDFInfo
- Publication number
- LT3153B LT3153B LTIP162A LTIP162A LT3153B LT 3153 B LT3153 B LT 3153B LT IP162 A LTIP162 A LT IP162A LT IP162 A LTIP162 A LT IP162A LT 3153 B LT3153 B LT 3153B
- Authority
- LT
- Lithuania
- Prior art keywords
- regeneration
- filter
- hydrochloric acid
- water
- consumption
- Prior art date
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- 238000000034 method Methods 0.000 title description 6
- 239000000460 chlorine Substances 0.000 title description 3
- 229910052801 chlorine Inorganic materials 0.000 title description 2
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 title 1
- 230000001172 regenerating effect Effects 0.000 title 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims abstract description 20
- 238000011069 regeneration method Methods 0.000 claims abstract description 20
- 238000005349 anion exchange Methods 0.000 claims description 8
- BVKZGUZCCUSVTD-UHFFFAOYSA-M Bicarbonate Chemical compound OC([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-M 0.000 claims 1
- 238000010521 absorption reaction Methods 0.000 claims 1
- 230000008929 regeneration Effects 0.000 abstract description 19
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 abstract description 15
- 239000003153 chemical reaction reagent Substances 0.000 abstract description 9
- 239000001569 carbon dioxide Substances 0.000 abstract description 7
- 229910002092 carbon dioxide Inorganic materials 0.000 abstract description 7
- 239000006227 byproduct Substances 0.000 abstract description 5
- IXCSERBJSXMMFS-UHFFFAOYSA-N hcl hcl Chemical compound Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 abstract description 2
- 239000000047 product Substances 0.000 abstract description 2
- 125000000129 anionic group Chemical group 0.000 abstract 1
- 230000003247 decreasing effect Effects 0.000 abstract 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 23
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 10
- 238000005342 ion exchange Methods 0.000 description 5
- 239000011780 sodium chloride Substances 0.000 description 5
- 239000002253 acid Substances 0.000 description 4
- 150000001450 anions Chemical class 0.000 description 3
- 238000010438 heat treatment Methods 0.000 description 3
- 238000011084 recovery Methods 0.000 description 3
- 230000002378 acidificating effect Effects 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- JYYOBHFYCIDXHH-UHFFFAOYSA-N carbonic acid;hydrate Chemical compound O.OC(O)=O JYYOBHFYCIDXHH-UHFFFAOYSA-N 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- 230000003213 activating effect Effects 0.000 description 1
- 230000004888 barrier function Effects 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- -1 chlorine ions Chemical class 0.000 description 1
- 238000005202 decontamination Methods 0.000 description 1
- 230000003588 decontaminative effect Effects 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- ZZUFCTLCJUWOSV-UHFFFAOYSA-N furosemide Chemical compound C1=C(Cl)C(S(=O)(=O)N)=CC(C(O)=O)=C1NCC1=CC=CO1 ZZUFCTLCJUWOSV-UHFFFAOYSA-N 0.000 description 1
- 238000009533 lab test Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Landscapes
- Treatment Of Water By Ion Exchange (AREA)
Abstract
Description
Išradimas priskiriamas šiluminės energetikos sričiai, tiksliau metodams, įgalinantiems išvengti nuosėdų (nuovirų) susidarymo šildytuvų, apšildymo paviršių šiluminių ir tiekimo ir apyvartinio ant šilumokaičių, vandens katilų šilumą perduodančių atominių ekektrinių šilumos vandens tiekimo sistemose, vandens valymo nuo nuovirų, vandens, skirto šilumos tiekimo sistemų maitinimui, karbonatinio kietumo vandens sumažinimo sistemoms, o tiksliau, jonų mainų medžiagų, kurių dėka atliekamas karbonatinio vandens kietumo sumažinimas, regeneracinei technologijai.The present invention relates to the field of thermal energy, more particularly to methods for preventing the formation of sedimentation in heaters, heating and supplying heating surfaces and circulating on heat exchangers, water boiler heat transfer nuclear power water supply systems, decontamination water, water for heat supply systems. power, carbonate water reduction systems, or more precisely, regeneration technology of ion-exchange materials that reduce carbonate water hardness.
Vienas būdų, įgalinančių išvengti nuosėdų susidarymo ant šilumos perdavimo paviršių, yra vandens, skirto šilumos tiekimo sistemų maitinimui, valymas chlorjonitiniais filtrais (Uį.B. AntJ)innų CnpaBOMHMK no ΒΟΑΟΠΟΑΓΟΤΟΒκε KOTeAHbix ycTaHOBOK.-M ., 1976, 26 - 28 pusi.) Chlorjonitiniuose filtruose pakrauta jonų mainų medžiaga - anijonitas, kuris vandens valymo procese absorbuoja hidrokarbonatinius jonus, o vietoj jų išskiria chloro jonus. Filtro mainų talpai pasibaigus, atliekama anijonito regeneracija - anijonito jonų mainų savybių hidrokarbonatinių jonų atžvilgiu atstatymas. Paprastai chlorjonitinio filtro anijonito regeneracija vykdoma, praleidžiant natrio chlorido (NaCl) tirpalą per filtrą iš viršaus į apačią. Šiuo atveju jonų mainų reakcija užrašoma šia lygtimi:One way to prevent the formation of sediment on heat transfer surfaces is to clean the water used to power the heat supply systems by means of chlorine ion filters (UJ.B. AntJ) inn CnpaBOMHMK no ΒΟΑΟΠΟΑΓΟΤΟΒκε KOTeAHbix ycTaHOBOK.-M. Chlorionite filters are loaded with ion-exchange material, anion, which absorbs hydrocarbonate ions in the water purification process and releases chlorine ions instead. At the end of the filter exchange capacity, anion exchange regeneration is performed - restoration of the ion exchange properties of the anion exchange with respect to hydrocarbonate ions. Usually, the anion exchange regeneration of the chlorionated filter is accomplished by passing the sodium chloride (NaCl) solution through the filter from top to bottom. In this case, the ion-exchange reaction is given by the following equation:
An HCO3 + NaCl = An C1 + NaHCO3 An HCO 3 + NaCl = An C1 + NaHCO 3
Šis regeneracijos metodas turi šiuos trūkumus.This method of regeneration has these disadvantages.
Dėl to, kad regeneracijos masto priklausomybė nuo reagento suvartojimo yra nelinijinio charakterio, netgi norint pasiekti 60 - 70 % masto regeneraciją (anijono jonų mainų savybių atstatymą) natrio chlorido suvartojimas turi viršyti teoriškai reikalingą kiekį kelis kartus. Reagento (NaCl) perteklius ir regeneracijos šalutinis produktas - sodos (NaHCO3) tirpalas nuleidžiami i drenažą ir toliau į atvirus vandens telkinius.Because of the non-linear nature of the reagent consumption dependence on the recovery rate, even in order to achieve a 60-70% recovery (anion exchange), the consumption of sodium chloride must be several times the theoretical amount required. Excess reagent (NaCl) and by-product of regeneration - soda (NaHCO 3 ) solution - are discharged into drainage and further into open water bodies.
Siūlomo būdo tikslas yra reagento suvartojimo regeneracijai sumažinimas ir galimybė išvengti regeneracijos produktų išmetimo į aplinką.The purpose of the proposed process is to reduce reagent consumption for regeneration and to prevent the release of regeneration products into the environment.
Nurodytas tikslas pasiekiamas tuo, kad siūloma chlorjonitinio filtro regeneraciją vykdyti druskos rūgšties (HC1) tirpalą perleidžiant per filtrą iš apačios i viršų.The stated aim is achieved by proposing that the regeneration of the chlorionated filter be effected by passing a solution of hydrochloric acid (HCl) from the bottom upwards.
Jonų mainų reakcija šiuo atveju užrašoma lygtimi:The ion-exchange reaction in this case is given by the equation:
An HCO3 + HC1 = An Cl H2CO3 An HCO 3 + HC1 = An Cl H 2 CO 3
Anglies rūgštis (H2CO3 akimirksniu skyla i vandeni (H2O) ir anglies dioksidą (CO2):Carbonic acid (H 2 CO 3 instantly decomposes into water (H 2 O) and carbon dioxide (CO 2 )):
H2CO3 = H2O + CO2, kuris pereina per anijonitą, jį sumaišydamas, pasišalina iš filtro ir susikaupia atskiroje talpoje. Tai, kad regeneracijos šalutinis produktas (CO2) pašalinamas iš reakcijos zonos, regeneracijos masto priklausomybė nuo reagento (HC1) suvartojimo turi linijini charakterį, t. y. vienas reagentas visiškai sunaudojamas. Todėl netgi 100 % anijonito atstatymui reikia teoriškai paskaičiuoto (stechiometrinio) reagento suvartojimo.H 2 CO 3 = H 2 O + CO 2 , which passes through the anion by mixing, is removed from the filter and collected in a separate container. The removal of regeneration by-product (CO 2 ) from the reaction zone has a linear character in the extent of regeneration relative to reagent (HC1) consumption, ie one reagent is completely consumed. Therefore, even a 100% anion exchange recovery requires a theoretically calculated (stoichiometric) reagent consumption.
Fig. I pateikti laboratorinių tyrimų rezultatai, kurie patvirtina išsiskiriančio anglies dioksido kiekio (VCO2) tiesinę priklausomybę nuo druskos rūgšties (HC1) suvartojimo, t. y. patvirtina regeneracijos masto priklausomybės nuo rūgšties suvartojimo charakterį (Fig. I skaičiais pažymėta:FIG. The results of the laboratory tests, which confirm the linear dependence of the carbon dioxide emission (VCO 2 ) on the consumption of hydrochloric acid (HCl), ie the character of the dependence on the acid consumption of the regeneration scale are presented in Fig. I:
- druskos rūgšties koncentracija 0,92 mg-ekv/1;- hydrochloric acid concentration of 0.92 mg-eq / l;
-druskos rūgšties koncentracija 2,60 mg-ekv/1;hydrochloric acid concentration of 2.60 mg-eq / l;
- druskos rūgšties koncentracija 12,00 mg-ekv/1.- hydrochloric acid concentration of 12.00 mg-eq / l.
Fig. 2 pavaizduota principinė anijonito regeneracijos technologinė schema, užtikrinanti anglies dioksido surinkimą ir utilizaciją.FIG. Figure 2 depicts the principal technological scheme of anion exchange regeneration for carbon capture and utilization.
Schemoje parodytas siurblys I sujungtas su filtru 2, pastarasis per drenažinę sistemą 3 sujungtas su ežektoriumi 4. Prie viršutinės filtro 2 dalies prijungta šalutinių reakcijos produktų talpa 5. Druskos rūgšties talpa 6 sujungta su filtru 2 per ežektorių 4 ir siurblį I. Talpa 5 sujungta su vandens talpa 7. Rūgštingumas nustatomas pH-metru 8. Dekarbonizatorius 9 sujungtas su ežektoriumi 10 ir vandens talpa II. Siurbliu 12 užpildoma ši vandens talpa II. Šalutinių reakcijos produktų talpa 5 sujngta su kompresoriumi 13 ir dujų balionu 14.The pump I shown in the diagram is connected to a filter 2, the latter connected to a ejector 4 via a drainage system 3. The reaction vessel 5 is connected to the upper part 2 of the filter 5. The hydrochloric acid reservoir 6 is connected to the filter 2 via water capacity 7. Acidity is determined by pH meter 8. Decarbonator 9 is connected to ejector 10 and water capacity II. Pump 12 fills this water capacity II. The by-product reaction vessel 5 is connected to a compressor 13 and a gas cylinder 14.
Schema dirba tokiu būdu.The scheme works this way.
Įjungiamas siurblys I ir sukuriama vandens cirkuliacija filtre 2 iš apačios į viršų per vidurinę drenažinę sistemą 3 ir ežektorių 4. Vandens naudojama tiek, kad užtikrintų anijonito sluoksnio išsiplėtimą 20-30 %. Iš taplos 6 paduodama druskos rūgštis į filtrą 2 ežektoriumi 4. Susidaręs anglies dvideginis pereina per anijonito sluoksnį ir juda iš filtro 2 į talpą 5. Talpa 7 yra kaip hidroužtvara slėgio padidėjimui talpoje 5 ir kaip buferis nuplovimo vandens priėmimui. Pakylus vandens lygiui filtre 2 iki b lygio, rūgšties padavimas į filtrą 2 nutraukiamas, sumažinamas vandens kiekis filtre 2 iki lygio a, išleidžiant vandenį į talpą 5, po to vėl į filtrą 2 paduodama rūgštis. Baigiant leisti paskaičiuotą rūgšties kiekį, jos padavimas nutraukiamas. Po 10-15 min. (laikas patikslinamas derinimo darbų metu) išjungiamas siurblys I, filtras 2 užpildomas pradiniu vandens kiekiu, išstumiant anglies dioksidą į talpą 5. Filtras 2 praplaunamas pradiniu vandens kiekiu, vanduo išpilamas į talpą 5. Padidėjus pH > 7 (kontrolė atliekama pHmetru 8), regeneracija laikoma baigta, plovimas nutraukiamas. Toliau filtras 2 gali būti naudojamas darbe arba rezervuojamas.Pump I is turned on and circulation of water in the filter 2 from the bottom up through the central drainage system 3 and the ejector 4 is achieved. The water is used to provide an anion exchange expansion of 20-30%. From the tap 6, the hydrochloric acid is fed to the filter 2 by means of an ejector 4. The carbon dioxide formed passes through the anion exchanger layer and moves from the filter 2 to the container 5. The container 7 acts as a hydro barrier for increasing pressure When the water level in the filter 2 rises to level b, the acid supply to the filter 2 is stopped, the amount of water in the filter 2 is reduced to the level a by discharging the water into the tank 5, then the acid 2 is again supplied to the filter 2. When the calculated amount of acid is stopped, the feed is stopped. After 10-15 min. (time to be adjusted during tuning) pump I is switched off, filter 2 is filled with the initial water volume, displacing carbon dioxide into the tank 5. filter 2 is washed with the initial water volume, the water is poured into the tank 5. pH increase> 7 (control by pHmeter 8) considered completed, the washing shall be interrupted. Next, filter 2 can be used at work or reserved.
Vandens kiekiui talpose 5 ir 7 padidėjus iki nustatyto lygio, jis utilizuojamas tokiu būdu:When the water content in tanks 5 and 7 rises to the set level, it is disposed of as follows:
- įjungiamas dekarbonizatoriaus 9 ventiliatorius:- Decarboniser 9 fan is activated:
- įjungiamas ežektorius 10, nustatomas rūgštaus (iš talpų 5 ir 7) ir išvalyto (po filtro 2) vandens sunaudojimas tokiu būdu, kad būtų visiškai neutralizuotas rūgštus vanduo.- activating the ejector 10, adjusting the consumption of acidic (from tanks 5 and 7) and purified (after filter 2) water in such a way as to completely neutralize the acidic water.
Užpildant talpą 11, įjungiamas siurblys 12. Iš talpos 5 anglies dioksidas pumpuojamas į balionus 14.When filling the tank 11, the pump 12 is started. From the tank 5, carbon dioxide is pumped into cylinders 14.
Fig. 2 pavaizduota technologinė schema numato įprastų, manometriniams slėgiams nepaskaičiuotų talpų panaudojimą vandens paruošimo šiluminių tinklų maitinimui įrenginiuose.FIG. The technological diagram depicted in Fig. 2 provides for the use of conventional tanks not calculated for manometric pressures in water treatment plants for the supply of heating networks.
Lyginant su žinomais būdais, siūlomo regenaracijos būdo panaudojimas užtikrina šiuos privalumus:Compared to known techniques, the use of the proposed regeneration technique offers the following advantages:
1) atliekų išmetimo į aplinką nebuvimą;(1) the absence of waste discharges into the environment;
2) šalutinio regeneracijos produkto (anglies dioksidas) surinkimą ą atskirą talpą, sutalpinimą balionuose ir panaudojimą įvairiose, pramonės pvz. maisto, šakose.(2) the collection of the by-product regeneration (carbon dioxide) into a separate container, its storage in cylinders and its utilization in a variety of industrial applications; food, in the branches.
3) reagento, druskos rūgšties, sunaudojimą griežtai pagal stechiometrinę priklausomybę 100 %.3) 100% strict stoichiometric dependence of reagent, hydrochloric acid reagent.
IŠRADIMO APIBRĖŽTISDEFINITION OF INVENTION
Claims (1)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| LTIP162A LT3153B (en) | 1992-10-27 | 1992-10-27 | Nonwaste method for anionite regenerating of chlorine ionite filter |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| LTIP162A LT3153B (en) | 1992-10-27 | 1992-10-27 | Nonwaste method for anionite regenerating of chlorine ionite filter |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| LTIP162A LTIP162A (en) | 1994-05-15 |
| LT3153B true LT3153B (en) | 1995-01-31 |
Family
ID=19721069
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| LTIP162A LT3153B (en) | 1992-10-27 | 1992-10-27 | Nonwaste method for anionite regenerating of chlorine ionite filter |
Country Status (1)
| Country | Link |
|---|---|
| LT (1) | LT3153B (en) |
-
1992
- 1992-10-27 LT LTIP162A patent/LT3153B/en not_active IP Right Cessation
Non-Patent Citations (1)
| Title |
|---|
| SH.V. LIFSHIC: "Spravochnik po vodopodgotovke kotelnyx ustanovok", pages: 26 - 26 |
Also Published As
| Publication number | Publication date |
|---|---|
| LTIP162A (en) | 1994-05-15 |
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| MM9A | Lapsed patents |
Effective date: 19971027 |