CS251513B1 - A method of multistage biological activation purification of wastewater in pulp and paper production - Google Patents
A method of multistage biological activation purification of wastewater in pulp and paper production Download PDFInfo
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- CS251513B1 CS251513B1 CS85868A CS86885A CS251513B1 CS 251513 B1 CS251513 B1 CS 251513B1 CS 85868 A CS85868 A CS 85868A CS 86885 A CS86885 A CS 86885A CS 251513 B1 CS251513 B1 CS 251513B1
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- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
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- Activated Sludge Processes (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Removal Of Specific Substances (AREA)
Abstract
Sposob viacstupňového čistenia odpadových vod -sípočíva v tom, že sa odpadová voda před prvým -stupňom upraví na pH 7,5 až 8,5, s výhodou n'a p-H 8 a v ďalšom -stupni na pH 5,5 až 6,5, s výhodou na pH 6, za iprida-nia biogénnych prvlk-ov dusíka a fosforu. Riesenie sa dá využívat na -čištenie odpadových; vod pri -výrobě -buničiny a papi-era.The method of multi-stage wastewater treatment consists in that the wastewater is adjusted to pH 7.5 to 8.5, preferably to pH 8, before the first stage, and to pH 5.5 to 6.5, preferably to pH 6, in the next stage, with the addition of biogenic elements of nitrogen and phosphorus. The solution can be used for wastewater treatment in the production of pulp and paper.
Description
251513251513
Vynález rieši spůsob biologického čiste-nia odpadových vod z výroby buničín aipapiera. V súčasnosti sa na čistenie odpa-dových vod z výroby buničiny a papiera po-užívajú jednostupňové a viacstupňové bio-logické aktivačně postupy. Vedia nespor-ných předností majú tieto postupy akonevýhodu vysolkú spotřebu elektrickej ener-gie potrebne] na aretáciu a vysoké nákla-dy spojené s dávkováním solí dusíka a fos-foru, ktoré atol biogénne prvky je nutnédávkovať obvykle v pomere BSKs : N : P == 100 : 4 : 0,8. (Hnětkovský a ikol. Papieren-ská příručka SNTL, Praha 1983.) jďalšou nevýhodou sú vysoké náklady nut-né na likvidáciu přebytečného aktivované-ho (kalu, ktorý u tohoto typu vod vzniká vmnožstvo až 0,5 kg na 1 kg odbúranéhoBSKs. (K. R. Dietrich: Die Abwassertechnik,Alfred Húthing Verlag, Zleidelberg 1973.)The present invention provides a method for the biological purification of wastewater from pulp and paper pulp production. Currently, single-stage and multi-stage biological activation procedures are used to purify wastewater from pulp and paper production. Knowing the undisputed advantages, these processes and the disadvantage of consuming electrical energy are necessary for arresting and high costs associated with the dispensing of nitrogen and phosphate salts, which atoll biogenic elements usually need to be dosed in a BSKs: N: P ratio == 100: 4: 0.8. Another disadvantage is the high costs involved in disposing of excess activated (sludge which, in this type of water, produces up to 0.5 kg per kg of degraded BSKs). KR Dietrich: Die Abwassertechnik, Alfred Húthing Verlag, Zleidelberg 1973.)
Tieto postupy pracujú tak, že sa k voděešte před vstupom do aktivácie přidá vyššieuvedené množstvo biogénnych prvkov N aP a hodnota pH upraví sa na 7 až 7,5.(Klandúch, Balhar: Správa zo> služobnejcesty do ZSSR 1977, VÚPC, Bratislava.) Popřidaní recirlkulovaného aktívneho kalusa voda podrobí jedno- alebo viaicstupňo-vej aktivácii.These procedures work by adding the abovementioned amount of biogenic N aP elements to the water lot before entering the activation and adjusting the pH to 7 to 7.5 (Klandúch, Balhar: Report on Business Travel to USSR 1977, VÚPC, Bratislava.) Addition of recirculated active potassium to water undergoes one- or multi-stage activation.
Podl'a předmětného vynálezu sa viacstup-ňové aktivačně čistenie odpadných vod zvýroby ibuničiny a papieru vyznačuje tým,že sa odpadová voda před prvým stupňomupraví na alkaliokú hodnotu pH 7,5 až 8,5,s výhodou na piH 8 bez pridania zlúčeníndusíka a fosforu a před dalším stupňom sapH hOdnota změní na kyslú hodnotu pH 5,5až 6,5, s výhodou na ρΗ 6, za pridania zlú-čenín dusíka a fosforu. Zo zlúčenín dusíkasa najěaistejšie používá amoniak alebo mo-čovina a zo zlúčenín fosforu fosforečnanyalebo kyselina fosforečná.According to the present invention, the multistage activation purification of waste water by the production of ibunicum and paper is characterized in that the waste water is treated before the first stage to an alkali pH of 7.5 to 8.5, preferably to piH 8 without the addition of nitrogen and phosphorus compounds and before the next step sapH, the pH changes to an acidic pH of 5.5 to 6.5, preferably to 6, with the addition of nitrogen and phosphorus compounds. Of the nitrogen compounds, ammonia or urea and phosphorous or phosphoric acid are most commonly used.
Vynález vycháldza z námi zistených po-znatkov, že celulózopapierenské vody zhladiska biologického odbúrania obsahujúdve skupiny látek, z kterých prvá sa rých-lejšie rozkládá pri pH 8 a Ik rozkladu nepo-třebuje biogénne prvky a druhá pri pH 6a za přítomnosti biogénnych prvkov dusíkaa fosforu. Příklad 1The present invention is based on the findings of ourselves that cellulosic paper waters contain a group of substances, the first of which decomposes more rapidly at pH 8 and decomposition does not require biogenic elements and the other at pH 6a in the presence of biogenic nitrogen and phosphorus elements. Example 1
Alkalická odpadová voda z výroby sulfá-tovej buničiny o koncentrácii 300 mg/1 BSKs,sa upraví přidáním H2SO4 na pH 7,5 a bezďalšieho přídavku biogénnych prvkov savedie kontinuálně do prvého stupňa viac-stupňovej aktivačnej biologickej čističky.Tu sa k nej přidává opracovaný vrátný ak-tivovaný kal v množstve 3 g/1. Zmes sa pre-vzdušňuje priebežne pomocou aerátora.Alkaline effluent from the production of sulphate pulp with a concentration of 300 mg / l BSKs is adjusted by adding H 2 SO 4 to pH 7.5 and the addition of biogenic elements is added to the first stage of the multi-stage activation biological purifier continuously. activated sludge at 3 g / l. The mixture is aerated continuously by means of an aerator.
Voda z prvého stupňa kontinuálně pretelkácez sedimentačnú nádrž, kde sa oddělí kala vyčištěná voda sa neutralizuje prídavkomH2SO4 kontinuálně na pH 5,5 a vstupuje dodruhého stupňa aktivácie. Tu sa přidávábiogénny dusík 6 mg/1 spracovanej vody voformě amoniaku a fosfor 1,2 mg/1 spracova-nej vody vo formě kyseliny fosforečnej. V druhom aktivačnom stupni sa vodaspracuje vratným aktivovaným kálom avzduchom rovnako, ako bolo popísané vprvom stupni. Voda z druhej aktivačnej ná-drže vstupuje do druhého stupňa sedimen-tácie. Odsedimentovaná vyčištěná voda máBSKs 15 mg/1, množstvo přebytečného akti-vovaného kalu je 50 mg na 1 ,1 vyčistenejvody. Účinnost' je 95 %. Příklad 2The water from the first stage continuously passes through the sedimentation tank, where the sludge-purified water is separated, is neutralized by the addition of H2SO4 continuously to pH 5.5 and enters the second stage of activation. Here, a biogenic nitrogen of 6 mg / l of treated water is added in the form of ammonia and phosphorus of 1.2 mg / l of treated water as phosphoric acid. In the second activation step, the water is treated with a reversible activated sludge and air as described in the first step. Water from the second activation reservoir enters the second stage of sedimentation. The settled purified water has a BSKs of 15 mg / L, the amount of excess activated sludge is 50 mg per 1.1 purified water. The efficiency is 95%. Example 2
Postupuje sa talk, ako v (příklade 1 s týmrozdielom, že sa použije kyslá odpadovávoda z výroby sulfitovej buničiny o kon-centrácii 350 mg BSKs/l a táto sa upravípřidáním vápenného mlieika na pH 8,5 a da-lej s tým rozdielom, že před druhým stup-ňom sa úprava pH na 5,5 dosiahne zmieša-ním s kyslou odpadovou vodou z výrobysulfitovej buničiny.One proceeds as in (Example 1, with the difference that acid wastewater from sulphite pulp production is used with a concentration of 350 mg BODs / l and this is adjusted to pH 8.5 by the addition of lime milk, with the difference that before by the second step, adjusting the pH to 5.5 is achieved by mixing with the acid waste water from the sulfite pulp.
Vyčištěná voda má BSKs 14 mg/1, množ-stvo přebytečného aktivovaného kalu je 60miligramov na 1 1 vyčistenej vody. Účinnost je 96 %. Příklad 3The purified water has a BOD of 14 mg / l, the amount of excess activated sludge is 60 milligrams per liter of purified water. The efficiency is 96%. Example 3
Dokumentuje ddterajší stav. Postupuje satak, alko v příklade 1 s tým rozdielom, ževoda sa upraví na pH 7, a dusík sa přidá vmnožstve 12 mg/1, fosfor v množstve 2,4 mgna liter ešte před prvý stupeň aktivácie. Ďalší iprídavoik biogénnych prvkov anizměna pH před druhým stupňom sa už ne-vykoná.It documents the current status. The procedure of satak, alcohol in Example 1 is followed except that the pH is adjusted to 7, and nitrogen is added in an amount of 12 mg / l, phosphorus at 2.4 mg / l before the first activation step. Further addition of biogenic elements and pH change before the second stage is no longer performed.
Vyčištěná voda BSKs 29 mg/1, množstvopřebytečného aktivovaného kalu je 125 mgna 1 1 vyčistenej vody. Účinnost je 90,3 %.Purified BOD water of 29 mg / l, the amount of activated activated sludge is 125 mg / l of purified water. The efficiency is 90.3%.
Modifilkáciou dvojstupňového alebo viac-stupňového čistenia podl'a předmětného vy-nálezu sa dosiahne zásadné zníženie množ-stva nadbytečného' aktivovaného kalu napolovinu oproti Idoteraz používaným postu-pem a tým úspora náikladov na jeho likvi-dáciu. Ďalej sa dosiahne zníženie spotřeby zte-čením dusíka a fosforu na 50 % až 30 %oproti doteraz používanému množstvu atým zníženie prevádzkových nákladov, akoi zvýšenie účinnosti biologického čisteniaodpadových vod.By modifying the two-stage or multi-stage purification according to the present invention, a substantial reduction in the amount of excess activated sludge is achieved in half compared to the Idoteraz process used, thereby saving the disposal costs. Furthermore, a reduction in the consumption of nitrogen and phosphorus by 50% to 30% compared to the amount used up to now is achieved, as well as reducing operating costs, as well as increasing the efficiency of the biological treatment of wastewater.
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CS85868A CS251513B1 (en) | 1985-02-08 | 1985-02-08 | A method of multistage biological activation purification of wastewater in pulp and paper production |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CS85868A CS251513B1 (en) | 1985-02-08 | 1985-02-08 | A method of multistage biological activation purification of wastewater in pulp and paper production |
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| Publication Number | Publication Date |
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| CS86885A1 CS86885A1 (en) | 1986-11-13 |
| CS251513B1 true CS251513B1 (en) | 1987-07-16 |
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| Application Number | Title | Priority Date | Filing Date |
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| CS85868A CS251513B1 (en) | 1985-02-08 | 1985-02-08 | A method of multistage biological activation purification of wastewater in pulp and paper production |
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1985
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| CS86885A1 (en) | 1986-11-13 |
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