CS266960B1 - Method of waste hydrogen chloride treatment - Google Patents

Method of waste hydrogen chloride treatment Download PDF

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CS266960B1
CS266960B1 CS865222A CS522286A CS266960B1 CS 266960 B1 CS266960 B1 CS 266960B1 CS 865222 A CS865222 A CS 865222A CS 522286 A CS522286 A CS 522286A CS 266960 B1 CS266960 B1 CS 266960B1
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acid
methyl
hydrochloric acid
neutralization
waste hydrochloric
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CS865222A
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Czech (cs)
Slovak (sk)
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CS522286A1 (en
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Peter Ing Hauskrecht
Robert Ing Csc Poor
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Hauskrecht Peter
Poor Robert
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Abstract

Odpadná kyselina chlorovodíková sa predneutralizuje s uhličitanom vápenatým a/alebo horečnatým a doneutralizuje sa s hydroxidom vápenatým v přítomnosti polyelektrolytu. Vyzrážané nečistoty sa oddelia sedimentáciou.Waste hydrochloric acid was added pre-neutralizes with calcium carbonate and / or magnesium and is neutralized with hydroxide calcium in the presence of polyelectrolyte. The precipitated impurities are separated by sedimentation.

Description

Vynález sa týká neutralizácie odpadnej kyseliny chlorovodíkovej, vznikájúcej pri výroběThe invention relates to the neutralization of waste hydrochloric acid produced during production

2-metyl-4-chlórfenoxyoctovej kyseliny:2-methyl-4-chlorophenoxyacetic acid:

2-metyl-4-chlórfenoxyoctová kyselina sa najčastejšie připravuje chloráciou 2-metylfenoxyoctovej kyseliny plynným chlórom alebo chlórňanom sodným. Chloráciu s chlórňanom sodným v přítomnosti minerálnej kyseliny a získanie 2-metyl-4-chlórfenoxyoctovej kyseliny popisuje AO 179 200. Pri výrobě odpadá minerálna kyselina, najčastejšie kyselina chlorovodíková, ktorá je znečistěná fenoxyoctovými kyselinami, ako sú kyseliny 2-metylfenoxyoctová, 2-metyl-4-chlórfenoxyoctová, 2-metyl-6-chlórfenoxyoctová, 2-metyl-4,6-dichlórfenoxyoctová, minerálnymi solami, predovšetkým chloridom sodným, chlórderivátmi 2-metylfenolu. Hodnota pH odpadnej kyseliny je 0 až 2, a to z toho důvodu, že vysrážaná 2-metyl-4-chlórfenoxyoctová kyselina je z nej lahko filtrovatelná.2-Methyl-4-chlorophenoxyacetic acid is most often prepared by chlorination of 2-methylphenoxyacetic acid with chlorine gas or sodium hypochlorite. Chlorination with sodium hypochlorite in the presence of mineral acid and recovery of 2-methyl-4-chlorophenoxyacetic acid is described in AO 179 200. Mineral acid, most often hydrochloric acid, which is contaminated with phenoxyacetic acids such as 2-methylphenoxyacetic acid, 2-methyl- 4-chlorophenoxyacetic acid, 2-methyl-6-chlorophenoxyacetic acid, 2-methyl-4,6-dichlorophenoxyacetic acid, mineral salts, in particular sodium chloride, 2-methylphenol chloride derivatives. The pH of the waste acid is 0 to 2, because the precipitated 2-methyl-4-chlorophenoxyacetic acid is easily filterable therefrom.

Pri využití a spracovaní odpadnej kyseliny sú problémy, vzhladom k tomu, že je takmer nasýtená anorganickými solami a má malú koncentráciu minerálnych kyselin. Ako odpad sa nemůže vypúšťať do kanalizácie, pretože vodohospodářské orgány súhlasia iba s vypúštaním po neutralizovaní na hodnotu pH 6 až 8. Najjednoduchšia neutralizácia je s lúhmi, predovšetkým s NaOH alebo Ca(OH)2< Určitá nevýhoda je tu prudká změna hodnory pH v blízkosti ekvivalentného bodu pri hodnote pH 7, čo může vyvolávat ťažkosti v priemyselnom meradle.There are problems in the use and processing of waste acid, due to the fact that it is almost saturated with inorganic salts and has a low concentration of mineral acids. It cannot be discharged as sewage, as water authorities only agree to discharge after neutralization to pH 6 to 8. The simplest neutralization is with lyes, especially NaOH or Ca (OH) 2 < A certain disadvantage here is a sharp change in the pH value in the vicinity equivalent point at pH 7, which can cause difficulties on an industrial scale.

Vyššie uvedené nedostatky sú zmiernené spůsobom úpravy odpadnej kyseliny chlorovodíkovej z výroby 2-metyl-4-chlórfenoxyoctovej kyseliny, podstata ktorého spočívá v tom, že sa odpadná kyselina chlorovodíková predneutralizuje s uhličitanom vápenatým a/alebo horečnatým na hodnotu pH 2 až 6,5 a doneutralizuje sa s hydroxidem vápenatým v přítomnosti polyelektrolytu. Polyelektrolyt sa přidává na lepšiu koaguláciu vyzrážaných častí a urýchlenie ich sedimentácie.The above drawbacks are alleviated by the method of treating waste hydrochloric acid from the production of 2-methyl-4-chlorophenoxyacetic acid, which consists in pre-neutralizing the waste hydrochloric acid with calcium and / or magnesium carbonate to a pH of 2 to 6.5 and done with calcium hydroxide in the presence of a polyelectrolyte. The polyelectrolyte is added to better coagulate the precipitated parts and accelerate their sedimentation.

Výhodou spůsobu podlá vynálezu je, že sa na predneutralizovanie kyseliny chlorovodíkovej použijú poměrně lačné suroviny, ktoré sa nachádzajú bežne v prírode ako vápenec, alebo dolomit. Výhodou uvedených látok je, že sú prakticky nerozpustné vo vodě a že prebytkom vápenca alebo dolomitu nie je možné prejsť do alkalickéj oblasti hodnoty pH. Doneutralizácia s hydroxidem vápenatým sa robí, ak je požiadavky, aby výsledná hodnota pH bola v blízkosti 7 alebo nad hodnotou 7. Hodnotu pH po doneutralizovaní určujú pri vypúšťaní do vodných tokov příslušné vodohospodářské orgány. Niekedy sa hodnota pH po doneutralizovaní určí z toho, do akej miery sa majú z odpadnej kyseliny chlorovodíkovej odstániť znečisťujúce látky, například kationy Fe, Mg, Zn a pod. Výhodné je možné predneutralizáciu odpadnej kyseliny chlorovodíkovej robit vo výrobní 2-metyl-4-chlórfenoxyoctovej kyseliny a doneutralizáciu robit na centrálnej neutralizačnej stanici v podniku, po zmiešaní predneutralizovanej odpadnej kyseliny chlorovodíkovej s inými odpadnými vodami z iných výrobní podniku. Predneutralizovaná kyselina chlorovodíková je menej korozívna a z toho důvodu sú menšie nároky na materiál, z ktorého je zhotovené potrubie.An advantage of the process according to the invention is that relatively fasting raw materials, which are commonly found in nature, such as limestone or dolomite, are used for the pre-neutralization of hydrochloric acid. The advantage of these substances is that they are practically insoluble in water and that it is not possible to pass into the alkaline pH range with an excess of limestone or dolomite. Donated neutralization with calcium hydroxide is done if the resulting pH value is required to be close to 7 or above 7. The pH value after done-neutralization is determined by the relevant water authorities when discharged into watercourses. Sometimes the pH value after donation is determined by the extent to which contaminants, for example Fe, Mg, Zn cations and the like, are to be removed from the waste hydrochloric acid. Advantageously, the pre-neutralization of the waste hydrochloric acid can be done in the 2-methyl-4-chlorophenoxyacetic acid production and the neutralization can be done at the central neutralization station in the plant, after mixing the pre-neutralized waste hydrochloric acid with other effluents from other plants. Pre-neutralized hydrochloric acid is less corrosive and therefore the material from which the pipe is made is less demanding.

Příklad 1Example 1

Odpadná kyselina chlorovodíková z výroby 2-metyl-4-chlórfenoxyoctovej kyseliny podlá čs. AO 179 200 málo následovně zloženie:Waste hydrochloric acid from the production of 2-methyl-4-chlorophenoxyacetic acid according to MS. AO 179 200 has the following composition:

chlorovodík 1,8 % hmot.hydrogen chloride 1.8% by weight

fenoxyoctové kyseliny 4,1 g/1phenoxyacetic acid 4.1 g / l

Cl chlórderiváty 2-metylfenoluCl chlorine derivatives of 2-methylphenol

92,8 g/192.8 g / l

0,16 g/10.16 g / l

000 ml odpadnej kyseliny chlorovodíkovej sa zneutralizovalo s vápencem na hodnotu pH 3,1. Po oddělení vápenca sa k reakčnej zmesi přidalo 0,2 ml 0,1 % hmot, vodného gelu polyelektrolytu (Magnaflor). Potom sa s 5,5 % hmot, suspenziu Ca(OH)2 reakčná zmes zneutralizovala na hodnotu pH 7,2. Vysrážané nečistoty sa oddělili sedimentáciou.000 ml of waste hydrochloric acid were neutralized with limestone to pH 3.1. After separating the limestone, 0.2 ml of a 0.1% by weight aqueous polyelectrolyte gel (Magnaflor) was added to the reaction mixture. Then, with a 5.5% by weight suspension of Ca (OH) 2, the reaction mixture was neutralized to pH 7.2. The precipitated impurities were separated by sedimentation.

CS 266 960 BlCS 266 960 Bl

Příklad 2Example 2

Postupovalo sa podlá příkladu 1 s tým rozdielom, že sa odpadná kyselina chlorovodíková predneutralizovala na hodnotu pH 4,3. Potom sa reakčný roztok zmiešal s odpadnými vodami z výrobní CHZJD, aby výsledný roztok představoval chemicky znečistenú vodu, ktorá v súčasnosti v CHZJD vzniká a ktorá mala následovně zloženie:The procedure of Example 1 was followed, except that the waste hydrochloric acid was pre-neutralized to pH 4.3. Then, the reaction solution was mixed with the wastewater from the production CHZJD, so that the resulting solution was chemically contaminated water, which is currently formed in the CHZJD and which had the following composition:

hodnota pH so2pH value with 2 " 2,9 1 600 2.9 1 600 mg/1 mg / 1 Cl Cl 1 025 1 025 mg/1 mg / 1 ChSK (2 hod.) Zn2+ ChSK (2 hours) Zn 2+ 865 12 865 12 mg O2/l mg/1mg O 2 / l mg / 1 Al3+ Al 3+ 15 15 mg/1 mg / 1 Fe3+ Fe 3+ 9 9 mg/1 mg / 1 Mg2+ Mg 2+ 48 48 mg/1 mg / 1 K jednému litru reakčnej To one liter of reaction zmesi sa přidalo 0 0 was added to the mixture

,2 ml 0,1 % hmot, vodného gelu polyelektrolytu (Magnoflor) a potom sa přidala 5,5 % hmot, suspenzia Ca(OH)?. Hodnota pH po neutralizá2+ 3+ 3+ 2+ cii bola 7,6. Vysrážené nečistoty, predovšetkým hydralované oxidy Zn , Fe , AI , Mg sa oddělili sedimentáciou., 2 ml of 0.1% by weight of an aqueous polyelectrolyte gel (Magnoflor) and then 5.5% by weight of a suspension of Ca (OH) ? . The pH after neutralization 2 + 3+ 3+ 2+ cii was 7.6. The precipitated impurities, especially the hydrated oxides of Zn, Fe, Al, Mg, were separated by sedimentation.

Příklad 3Example 3

Postupovalo sa podlá příkladu 1 s tým rozdielom, že sa odpadná kyselina chlorovodíková predneutralizovala s mikromletým magnezitom na hodnotu pH 6,4. Hodnota pH po doneutralizovaní bola 7,4. Vyzrážené nečistoty sa odstránili sedimentáciou.The procedure of Example 1 was followed, except that the waste hydrochloric acid was pre-neutralized with micronized magnesite to pH 6.4. The pH after doneutralization was 7.4. Precipitated impurities were removed by sedimentation.

Vynález nájde uplatnenie pri neutralizávii odpadnej kyseliny chlorovodíkovéj vznikajúcej pri výrobě kyseliny 2-metyl-4-chlórfenoxyoctovej. Výhodné je možno predneutralizovať odpadnú kyselinu chlorovodíková vo výrobní 2-metyl-4-chlórfenoxyoctovej kyseliny a doneutralizáciu urobit na centrálnej neutralizačnej stanici kyslých odpadných vód.The invention finds application in the neutralization of waste hydrochloric acid formed in the production of 2-methyl-4-chlorophenoxyacetic acid. Preferably, the waste hydrochloric acid can be pre-neutralized in the production of 2-methyl-4-chlorophenoxyacetic acid and the neutralization can be done at a central acid waste water neutralization station.

Claims (1)

PREDMET VYNÁLEZUOBJECT OF THE INVENTION SpSsob úpravy odpadnej kyseliny chlorovodíkovej z výroby 2-metyl-4-chlórfenoxyoctovej kyseliny znečistenej 2-metyl-fenoxyoctovou kyselinou, 2-metyl-4-chlórfenoxyoctovou kyselinou, 2-metyl-4,6-dichlórfenoxyoctovou kyselinou, 2-metylfenolu, chloridom sodným, neutralizáciou alkáliami, pozostávajúcej z predneutralizácie odpadnej kyseliny chlorovodíkovej na hodnotu pH 2 až 6,5 uhličitanom vápenatým a/alebo horečnatým, vyznačujúci sa tým, že takto upravená reakčná zmes sa doneutralizuje s hydroxidom vápenatým v přítomnosti polyelektrolytu a vyzrážané nečistoty sa oddelia sedimentáciou.Process for the treatment of waste hydrochloric acid from the production of 2-methyl-4-chlorophenoxyacetic acid contaminated with 2-methylphenoxyacetic acid, 2-methyl-4-chlorophenoxyacetic acid, 2-methyl-4,6-dichlorophenoxyacetic acid, 2-methylphenol, sodium chloride, alkali neutralization, consisting of pre-neutralization of the waste hydrochloric acid to a pH of 2 to 6.5 with calcium and / or magnesium carbonate, characterized in that the reaction mixture thus treated is neutralized with calcium hydroxide in the presence of a polyelectrolyte and the precipitated impurities are separated by sedimentation.
CS865222A 1986-07-09 1986-07-09 Method of waste hydrogen chloride treatment CS266960B1 (en)

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