CS244317B1 - Process for treating waste hydrochloric acid from the production of 2-methyl-4-chloro-phenoxyacetic acid - Google Patents

Process for treating waste hydrochloric acid from the production of 2-methyl-4-chloro-phenoxyacetic acid Download PDF

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CS244317B1
CS244317B1 CS846434A CS643484A CS244317B1 CS 244317 B1 CS244317 B1 CS 244317B1 CS 846434 A CS846434 A CS 846434A CS 643484 A CS643484 A CS 643484A CS 244317 B1 CS244317 B1 CS 244317B1
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neutralization
acid
methyl
neutralized
followed
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CS846434A
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CS643484A1 (en
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Peter Hauskrecht
Stanislav Demovic
Marta Cipova
Miroslav Marchalin
Frantisek Bocan
Blazej Vavra
Alojz Kollar
Jan Lehotsky
Tibor Guertler
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Peter Hauskrecht
Stanislav Demovic
Marta Cipova
Miroslav Marchalin
Frantisek Bocan
Blazej Vavra
Alojz Kollar
Jan Lehotsky
Tibor Guertler
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Priority to CS846434A priority Critical patent/CS244317B1/en
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Publication of CS244317B1 publication Critical patent/CS244317B1/en

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Abstract

Spůsob úpravy odpadnej kyseliny chloro- vodíkovej z výroby 2-metyl-4-chlórfenoxy- octovej kyseliny, ktorého podstata je v tom, že sa odpadná kyselina chlorovodíková predneutralizuje na hodnotu pH 2 až 5 a na doneutralizáciu sa použijú zlúčeniny, ktoré vytvárajú v blízkosti hodnoty pH 7 tlmivé prostredie. Spůsob je možné využit na neutralizáciu odpadných vůd z výroby kyseliny 2-metyl-4- -chlórfenoxyoctovej, ktorá sa používá ako herbicid, před ich vypuštěním do kanalizá- cie.Process for the treatment of waste hydrochloric acid from the production of 2-methyl-4-chlorophenoxyacetic acid, which is characterized in that the waste hydrochloric acid is pre-neutralized to a pH of 2 to 5, and compounds which form near the value of pH 7 buffer. The process can be used to neutralize the effluent from the production of 2-methyl-4-chlorophenoxyacetic acid, which is used as a herbicide, before it is discharged to the sewer.

Description

3 4 2443173 4 244317

Vynález sa týká neutralizácie odpadnejkyseliny chlorovodíkové], vznikajúcej přivýrobě 2-metyl-4-chlórfenoxyoctovej kyseli-ny. 2-metyl-4-chlórfenoxyoctová kyselina sanajčastejšie připravuje chloráciou 2-metyl-fenoxyoctovej kyseliny plynným chlórom a-lebo chlórňanom sodným. Chloráciu s chlór-ňanom sodným v přítomnosti minerálnej ky-seliny a získanie 2-metyl-4-chlórfenoxyocto-vej kyseliny z rcakčnej zmesi jej vyzráža-ním v přebytku minerálnej kyseliny popisu-je AO č. 179 200. Při výrobě odpadá minerál-na kyselina, najčastejšie kyselina chlorovodí-ková, ktorá je znečistěná fenoxyoctovými ky-selinami, ako sú kyseliny 2-metylfenoxyocto-vá, 2-metyl-4-chlórfenoxyoctová, 2-metyl-6--chlórfenoxyoctová, 2-metyl-4,6-dichlórfeno-xyoctová, minerálnymi soTami, predovšetkýmchloridom sodným, chlórderivátmi 2-metyl-fenolu. Hodnota pH odpadnej kyseliny je0 až 2, a to z toho dovodu, že vyzrážaná 2--metyl-4-chlórfenoxyoctová kyselina je z nej1'ahko filtrovatelná.BACKGROUND OF THE INVENTION The present invention relates to the neutralization of waste hydrochloric acid resulting from the production of 2-methyl-4-chlorophenoxyacetic acid. Often, 2-methyl-4-chlorophenoxyacetic acid prepares chlorination of 2-methyl-phenoxyacetic acid with chlorine gas or sodium hypochlorite. Chlorination with sodium hypochlorite in the presence of mineral acid to obtain 2-methyl-4-chlorophenoxyacetic acid from the reaction mixture by precipitating it in excess mineral acid of the description is AO no. an acid, most commonly 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, especially sodium chloride, chloro derivatives of 2-methylphenol. The pH of the waste acid is 0 to 2, with the result that the precipitated 2-methyl-4-chlorophenoxyacetic acid is easily filterable.

Pri využití a spracovaní odpadnej kyselinysú problémy, vzhiadom k tomu, že je tak-mer nasýtenó anorganickými sofami a mámalá koncentráciu minerálnych kyselin.Ako odpad sa nemůže vypúštať do kanalizá-cie, pretože vodohospodářské orgány súhla-sia iba s vypúšfaním po neutralizovaní nahodnotu pH 6 až 8. Najjednoduchšia neu-tralizácia je s lúhmi, predovšetkým s NaOHalebo Ca (OH) 2, ktorá je popísaná vo výs-kumnej správě Ing. Truchlík, CSc. a kol.Zlepšeme kvality MCPA, č. P-61-21, VÚAgTBratislava (3980). Neurčitá nevýhoda je tuprudká změna hodnoty pH v blízkosti ekvi-valentného bodu pri hodnotě pH 7, čo mů-že vyvolávat fažkosti v priemyselnom me-radle.In the use and treatment of waste acid problems, since it is so saturated with inorganic salts and low mineral acid concentrations. As waste cannot be discharged into the sewage system, since the water management authorities only agree to discharge after neutralization of pH 6 to 8. The simplest neutralization is with lye, especially NaOH or Ca (OH) 2, which is described in Ing. Truchlík, CSc. Improve MCPA, No. P-61-21, VÚAgTBratislava (3980). An undesirable disadvantage is the slight change in pH close to an equivalence point at pH 7, which can induce difficulties in industrial scale.

Vyššie uvedené nedostatky sú zmiernenésposobom úpravy odpadnej kyseliny chloro-vodíkové]' z výroby 2-metyl-4-chlórfenoxy-octovej, podstata ktorého spočívá v tom, žesa kyselina chlorovodíková, obsahujúca ne-čistoty ako fenoxyoctové kyseliny, predo-všetkým 2-metylfenoxyoctovú, 2-metyl-4--chlórfenoxyoctovú, 2-metyl-4,6-dichlórfen-oxyoctovú, minerálně soli, najma chloridsodný, chlórderiváty 2-metylfenolu, predne-utralizuje s hydroxidom alebo uhličitanemvápenatým a/alebo hydroxidom horečnatýmalebo uhličitanom horečnatým koncentrácie0,1 až 99,5 % hmot. Hodnota pH je 2 až 5.The aforementioned drawbacks are alleviated by the treatment of the hydrochloric acid waste from the production of 2-methyl-4-chlorophenoxyacetic acid, characterized in that the hydrochloric acid containing impurities such as phenoxyacetic acids is predominantly 2-methylphenoxyacetic acid, 2-methyl-4-chlorophenoxyacetic acid, 2-methyl-4,6-dichlorophenoxyacetic acid, mineral salts, especially sodium chloride, chloro derivatives of 2-methylphenol, pre-alkaline with calcium hydroxide or carbonate and / or magnesium hydroxide or magnesium carbonate at a concentration of 0.1 to 99.5 wt. The pH is 2 to 5.

So stúpajúcou hodnotou pH reakčná rých-losť neutralizácie pri použití uhličitanu kle-sá. Reakčná zmes sa potom doneutralizujena hodnotu pH 6 až 8 vodným roztokomuhličitanu sodného koncentrácie 0,1 až 30 %hmot. alebo hydroxidu sodného koncen-trácie 0,1 až 45 % hmot. alebo suspenziouhydroxidu vápenatého š obsahom 0,1 až 35percent hmotnostných hydroxidu vápenaté-ho.With increasing pH, the reaction rate of neutralization with carbonate is reduced. The reaction mixture is then neutralized to a pH of 6 to 8 with aqueous sodium bicarbonate at a concentration of 0.1 to 30% by weight. or sodium hydroxide concentration of 0.1 to 45 wt. or a calcium hydroxide slurry containing 0.1 to 35 percent by weight calcium hydroxide.

Na predneutralizáciu odpadnej kyselinychlorovodíkovej sa použije odpadný uhliči-tan vápenatý, vznikájúci po absorpcii kys-ličnílsa uhličitého z odplynu po chlorácii fu-ralu, v suspenzii hydroxidu vápenatého. Výhodou spósobu podl'a vynálezu je, že sana predneutralizácii kyseliny chlorovodíko-vej použijú lačné chemikálie, ako napr. váp-no alebo vápenec, připadne dolomit. Pri do-neutralizácii je výhodné, že sa prakticky ne-může dostat reakčná zmes do alkalickej ob-lasti pH, pokial' obsahuje v roztoku nadby-tok Ca2 + iónov. Indikovanie požadovanejhodnoty pH je dané bielym zákalom reak-čnej zmesi a je jednoduché a lahko pozoro-vatelné. V oblasti pH 6 až 8 má reakčnázmes za týchto podmienok z hladiska hod-noty pil charakter tlmivého roztoku. Dopredneutralizácie je možné z reakčnej zme-si získávat fenoxyoctové kyseliny, ktoré sapoužívají! napr. ako herbicidy. Ak v rozto-ku po čiastočnej neutralizácii sú vápenatéióny, možno s výhodou na doneutralizáciupoužit uhličitan sodný, v případe, že sú vroztoku po čiastočnej neutralizácii horeč-naté soli, je výhodné na doneutralizáciupoužit hydroxid sodný alebo vápenatý. Napredneutralizáciu sa možu použit odpadněkaly z absorpcie CO v a Cl2 po chlorácii fu-ralu, ktoré sú odpad. Příklad 1 100 ml odpadnej kyseliny chlorovodíkovejpo odfiltrovaní kyseliny 2-metyl-4-chlórfe-noxyoctovej s obsahom IlCl 21,9 g/l, 108,5g/l Cl a 3,9 g/l fenoxyoctových kyselin0,19 g/l chlórderivátov 2-metylfenolu sapredneutralizovalo s vápencom na hodno-tu pil 3,1. Prebytočný vápenec sa odfiltro-val a 10 ml zmesi sa doneutralizovalo s 1 %(hmot.) roztokom Na2CO3. Závislost množ-stva přidaného roztoku od hodnoty pH jev tabufke 1:To pre-neutralize the waste hydrochloric acid, the spent calcium carbonate resulting from the absorption of carbon dioxide from the off-gas after chlorination of the fumarate is used in a calcium hydroxide suspension. An advantage of the process according to the invention is that pre-neutralizing hydrochloric acid is used in the preparation of fastening chemicals such as lime or limestone, possibly dolomite. In the neutralization process, it is preferred that the reaction mixture is virtually impossible to get into the alkaline pH range when it contains excess Ca 2+ ions in the solution. Indication of the desired pH value is given by the white haze of the reaction mixture and is simple and easy to observe. In the pH range 6 to 8, the reaction medium under these conditions has the character of a buffer. Pre-neutralization can be obtained from the reaction mixture by phenoxyacetic acids which are used! e.g. as herbicides. If the calcium carbonates are present in the solution after partial neutralization, sodium carbonate may advantageously be used for the neutralization, if sodium or calcium hydroxide is used in the solution after partial neutralization of the magnesium salt. Pre-neutralization may be avoided by the absorption of CO 2 and Cl 2 after the chlorination of the furoal which is waste. Example 1 100 ml of waste hydrochloric acid by filtration of 2-methyl-4-chlorophenoxyacetic acid with a content of IlCl of 21.9 g / l, 108.5 g / l Cl and 3.9 g / l of phenoxyacetic acids0.19 g / l of chloro derivatives 2 -methylphenol was neutralized with limestone at a pH of 3.1. Excess limestone was filtered off and 10 ml of the mixture was neutralized with 1% (w / w) Na2CO3 solution. The dependence of the amount of solution added from the pH in Table 1 is:

Claims (2)

2443X7 Objem (ml) 1 % (hmot.) Na2CO3 Hodnota pH Poznámka 0 3 4 5 6 7 89 10 11 3 4.5 6 slabý zákal 66 6,3 biely zákal 6.6 7,2 7,5 8 Příklad 2 Postupovalo sa podlá příkladu 1 s týmrozdielom, že sa na predneutralizáciu použilhydroxid vápenatý cca 5 % (hmot.) sus-penzia a hodnota pH po predneutralizáciibola 3,4. K 100 ml predneutralizovanej ky-seliny sa přidalo 30 ml 1 % (hmot.) roz-toku Na2CO3. Výsledná hodnota pH bola6,0. Příklad 3 Postupovalo sa podlá příkladu 1 s týmrozdielom, že sa na predneutralizáciu použildolomit a hodnota pH po predneutralizáciibola 4,3. Získaná zmes sa doneutralizovala 4 ml 1 % (hmot.) roztokom NaOH na hod-notu pH 6. Příklad 4 Postupovalo sa podlá příkladu 1 s týmrozdielom, že sa na predneutralizáciu použiluhličitan horečnatý a hodnota pH bola 3,9.Získaná zmes sa doneutralizovala 1 ml cca 5 % suspenzie Ca(OH)2. Hodnota pH poneutralizácii bola 6,2. Příklad 5 Postupovalo sa podlá příkladu 1 s týmrozdielom, že sa na predneutralizovanie po-užil dolomit a hodnota pH po predneutrali-zácii bola 4,4 a zmes sa doneutralizovala PREDMET 1. S.pósob úpravy odpadnej kyseliny chlo-rovodíkové) z výroby 2-metyl-4-chlórfenoxy-octovej kyseliny znečistenej fenoxyoctový-mi kyselinami, ako 2-metylfenoxyoctovou,2-metyl-4-chIórfenoxyoctovou, 2-metyl-4,6-di-chlórfenoxyoctovou, 2- metyl-6-chlórfenoxy-octovou, chlórderivátmi 2-metylfenolu, chlo-ridom sodným, neutralizáciou alkáliami, vy-značujúci sa tým, že sa odpadná kyselinachlorovodíková predneutralizuje na hodno-tu pH 2 až 5 uhličitanom vápenatým alebohydroxidom vápenatým a/alebo hydroxidomhorečnatým alebo uhličitanom horečnatýmkoncentrácie 0,1 až 99,5 % hmot. a takto 25 ml 1 % (hmot.) Na2CO3. Hodnota pHbola 6. Příklad 6 Postupovalo sa podlá příkladu 1 s týmrozdielom, že sa použil odpadný CaCOs, vzni-kajúci pri zachytávaní CO2 a zbytkov CI2 zchlorácie furalu plynným chlórom. Po pred-neutralizácii mala reakčná zmes hodnotupH 3,9. Na neutralizáciu sa použilo 3 ml1 % Na2CO3 (°/o hmot.). Hodnota pH po ne-utralizácii bola 6,1. Příklad 7 Postupovalo sa podlá příkladu 5 s týmrozdielom, že sa na doneutralizáciu použilo 1,2 ml 22 % (hmot.) Na2CO3. Výsledná hod-nota pH bola 6,4. Příklad 8 Postupovalo sa podlá příkladu 4 s týmrozdielom, že sa na doneutralizovanie použi-lo 0,5 g cca 30 % suspenzie Ca(OH)2. Hod-nota pH po neutralizácii bola 6,9. Vynález možno využil pri výrobě 2-metyl--4-chlórfenoxyoctových kyselin na neutrali-záciu vzniklej odpadnej kyseliny chlorovo-díkové). Neutralizácia na hodnotu pH 6 až8 je podmienka vodohospodářských orgánov,bez ktorej nie je možné vypúšťať odpadnúkyselinu chlorovodíkovú do odpadných vod. vynalezu upravená reakčná zmes sa doneutralizujena hodnotu pH 6 až 8 vodným roztokom uhli-čitanu sodného koncentrácie 0,1 až 30 %hmot. alebo hydroxidu sodného koncentrá-cie 0,1 až 45 % hmot. alebo suspenzie hyd-roxidu vápenatého s obsahom 0,1 až 35 %hmot. hydroxidu vápenatého.2443X7 Volume (ml) 1% (w / w) Na2CO3 pH value Note 0 3 4 5 6 7 89 10 11 3 4.5 6 turbidity 66 6.3 white turbidity 6.6 7.2 7.5 8 Example 2 Example 1 was followed with the difference that calcium hydroxide of about 5% (w / w) suspension and pH after pre-neutralization were 3.4 for pre-neutralization. To 100 mL of pre-neutralized acid, 30 mL of 1% (w / w) Na 2 CO 3 solution was added. The resulting pH was 6.0. EXAMPLE 3 The procedure of Example 1 was followed, with the difference that the pre-neutralization was 4.3 and the pH was pre-neutralized. The resulting mixture was neutralized with 4 ml of a 1% (w / w) NaOH solution to pH 6. Example 4 Example 1 was followed with the difference that magnesium carbonate was used for the pre-neutralization and the pH was 3.9. ml of Ca (OH) 2 suspension. The pH of the poneutralization was 6.2. EXAMPLE 5 Example 1 was followed with the difference that dolomite was used for the pre-neutralization and the pH after pre-neutralization was 4.4 and the mixture was neutralized with the object 1. Preparation of the waste hydrochloric acid 2). methyl 4-chlorophenoxyacetic acid contaminated with phenoxyacetic acids such as 2-methylphenoxyacetic acid, 2-methyl-4-chlorophenoxyacetic acid, 2-methyl-4,6-dichlorophenoxyacetic acid, 2-methyl-6-chlorophenoxyacetic acid, chloro derivatives 2-methylphenol, sodium chloride, neutralizing with alkali, characterized in that the waste hydrochloric acid is pre-neutralized to a pH of 2 to 5 with calcium carbonate or calcium hydroxide and / or magnesium hydroxide or magnesium carbonate at a concentration of 0.1 to 99.5% wt. and thus 25 ml of 1% (w / w) Na2CO3. PHbola 6. EXAMPLE 6 Example 1 was followed with the difference that the CaCO3 waste formed during the capture of CO2 and Cl2 residues from chlorination of the fural by chlorine gas was used. After pre-neutralization, the reaction mixture was rated 3.9. 3 ml of 1% Na2CO3 (% w / w) were used for neutralization. The pH after the neutralization was 6.1. EXAMPLE 7 Example 5 was followed with the difference that 1.2 ml of 22% (w / w) Na2CO3 was used for the neutralization. The resulting pH was 6.4. EXAMPLE 8 Example 4 was followed with the difference that 0.5 g of about 30% Ca (OH) 2 suspension was used to be neutralized. The pH after neutralization was 6.9. The invention can be used to produce 2-methyl-4-chlorophenoxyacetic acids to neutralize the resulting hydrochloric acid waste. Neutralization to a pH of 6 to 8 is a condition of the water authorities without which it is not possible to discharge the hydrochloric acid wastewater into the wastewater. The resulting reaction mixture is neutralized to a pH of 6-8 with an aqueous solution of sodium carbonate at a concentration of 0.1 to 30% by weight. or sodium hydroxide concentration of 0.1 to 45% by weight. or a calcium hydroxide suspension containing 0.1 to 35 wt. calcium hydroxide. 2. Sposob podlá bodu 1, vyznačujúci satým, že na predneutralizáciu odpadnej ky-seliny chlorovodíkovej sa použije odpadnýuhličitan vápenatý, vznikajúci po absorpciikysličníka uhličitého a chlóru z odplynu, pochlorácii furalu v suspenzii hydroxidu vá-penatého.2. Process according to claim 1, characterized in that calcium carbonate resulting from the absorption of carbon dioxide and chlorine from the off-gas, chlorination of the fural in a slurry of calcium hydroxide hydroxide is used to pre-neutralize the hydrochloric acid.
CS846434A 1984-08-27 1984-08-27 Process for treating waste hydrochloric acid from the production of 2-methyl-4-chloro-phenoxyacetic acid CS244317B1 (en)

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