CS248237B1 - Method of hydrochloric acid neutralization] from the production of phenylhydrazine hydrochloride - Google Patents
Method of hydrochloric acid neutralization] from the production of phenylhydrazine hydrochloride Download PDFInfo
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Abstract
Riešenie sa týká neutralizácie odpadne) kyseliny chlorovodíkovej z výroby fenylhydrazínhydrochloridu vápenatými kalmi z výroby kaptaxu. Po neutralizácii je výsledná hodnota pH 4 až 7, s výhodou 4,5 až 6,5. Nerozpustné látky ako kaiptax, smolovité látky, hydroxid železnatý, zinočnatý, nečistoty z technického hydroxidu vápenatého sa oddelia, s výhodou sedimentáciou.The solution concerns the neutralization of waste) hydrochloric acid from the production of phenylhydrazine hydrochloride with calcium sludge from the production of captax. After neutralization, the resulting pH value is 4 to 7, preferably 4.5 to 6.5. Insoluble substances such as caiptax, pitch-like substances, iron hydroxide, zinc hydroxide, impurities from technical calcium hydroxide are separated, preferably by sedimentation.
Description
248237248237
Vynález sa týká sposobu neutralizácie od-padne] kyseliny chlorovodíkové], ktorá vzni-ká pri výrobě fenylhydrazínhydírochloridu.BACKGROUND OF THE INVENTION The present invention relates to a process for the neutralization of hydrochloric acid, which is produced by the preparation of phenylhydrazine dihydrochloride.
Fenylhydrazínhydrochlorid sa vyrába zanilínu diazotáciou s dusitanom sodným vpřebytku kyseliny chlorovodíkové] a reduk-ciou vzniklého ibenzéndiazóniumchloridu sroztokom hydrogénsiričitanu a siričitanusodného a doredukuje sa so zinkovým pra-chom. Fenylhydrazínhydírochlorid sa odfilt-ruje od matečnej kyseliny chlorovodíkové],ktorá obsahuje ako nečistoty fenythydra-zínhydrochlorid, chlorid sodný, síran sodný,zinočnaté ióny a nezreagovaný anilín. V súčastnosti odpadná kyselina chlorovo-díková nemá využitie a odchádza do odpad-ných vod. Niekedy sa před vypuštěním ne-utralizuje s hydroxidom sodným alebo vá-penatým. 2-merkaptobenztiazol (kaptaxj sa najčas-tejšie vyrába kondenzáciou anilínu, síry, sí-rouhlíka a surový kaptax sa čistí s hydro-xidom vápenatým. Pri čistění odpadajúvápenaté kaly, ktoré obsahujú okrem hyd-roxidu vápenatého ako nečistoty vápenatásol' ikaptaxu a živičnaté látky vznikajúce privýrobě kaptaxu. Vápenné kaly sa nevyuží-vajú a uskladňujú sa na skládike chemické-ho odpadu.Phenylhydrazine hydrochloride is produced by zaniline by diazotization with sodium nitrite in excess of hydrochloric acid] and reduction of the resulting ibenzenediazonium chloride with a hydrogen sulfite / sulfite solution and reduction with zinc powder. The phenylhydrazine dihydrochloride is filtered off from the mother hydrochloric acid], which contains impurities such as phenylhydrazine hydrochloride, sodium chloride, sodium sulfate, zinc ions and unreacted aniline. At present, the spent hydrochloric acid is not used and goes to wastewater. Sometimes it is not neutralized with sodium hydroxide or calcium hydroxide prior to discharge. 2-mercaptobenzothiazole (which is most commonly produced by condensation of aniline, sulfur, sulfur, and crude captax is purified with calcium hydroxide. In the purification process, waste calcium lime sludges that contain calcium calcium hydroxide as calcium and calcium carbonate impurities) Lime sludge is not used and stored in a chemical waste dump.
Vyššie uvedené nedostatky sú zmiernenésposobom neutralizácie kyseliny chlorovo-díkové] z výroby fenylhydrazínhydrochlori-du. Odpadná kyselina chlorovodíková jeznečistěná chloridom a síranom sodným,zinočnatým a niekedy železnatým iónom,fenylhydrazínom a anilínom. Kyselina chlo-rovodíková sa neutralizuje odpadnými vá-penatými ikalmi, ktoré obsahujú 1 až 40 %hmotnosti hydroxidu vápenatého, 0,1 až 5percent hmotnosti vápenatej soli kaptaxu,1 až 15 % hmotnosti živičnatých látok vzni-tkajúcieh pri výrobě kaptaxu a nečistoty po-chádzajúce z technického hydroxidu vápe-natého.The above drawbacks are alleviated by the process of neutralizing hydrochloric acid from the production of phenylhydrazine hydrochloride. Waste hydrochloric acid is purified by chloride and sodium sulfate, zinc and sometimes iron (II), phenylhydrazine and aniline. The hydrochloric acid is neutralized by waste lye which contains 1 to 40% by weight of calcium hydroxide, 0.1 to 5% by weight of calcium salt of calcium, 1 to 15% by weight of bituminous matter formed in the manufacture of the capta and impurities following from technical calcium hydroxide.
Hodnota pH po neutralizácii je 4 až 7, svýhodou 4,5 až 6,5. Z odpadných kalov prak-ticky vápenaté ióny prejdú do roztoku avyzráža sa kaptax. Nerozpustné ostanu tiežsmolo vité látky. Z odpadne] kyseliny chlo-rovodíkové] sa vyzrážajú ióny železa a zin-ku vo formě hydroxidu. Zo suspenzie sa ne-rozpustné látky oddelia s výhodou sedimen-táciou. Výhodou sposobu neutralizácie kyselinychlorovodíkové]’ z výroby fenylhydrazínhyd-rochloridu je, že sa na jej neutralizáciu po-užijú odpadne vápenné kaly z výroby kap-taxu. Z vápenných kalov sa využije praktic-ky všetok vápník, ktorý přejde na rozpustnýchlorid vápenatý. Z vápenných kalov zosta-ne nerozpustný kaptax a smolovité látky,ktorých objem je podstatné menší ako ob- jem póvodných vápenatých kalov, čím saznížia náklady na ich uskladnenie na sklád-ke chemických odpadov. Z odpadnej kyseli-ny sa vyzrážajú zinkové a železnaté ióny voformě hydroxidu. Příklad 1The pH after neutralization is 4 to 7, preferably 4.5 to 6.5. From the sewage sludge, the practically calcium ions pass into solution and precipitation is precipitated. Also insoluble matter remains insoluble. Iron and zinc ions are precipitated from the precipitated hydrochloric acid as hydroxide. The insoluble matter is preferably separated from the suspension by sedimentation. The advantage of the process for the neutralization of hydrochloric acid from the production of phenylhydrazine hydrochloride is that the lime sludge from the production of kappa is used to neutralize it. From the lime sludge, practically all of the calcium that is converted to calcium soluble is used. The lime sludge still has insoluble captax and pitch-like substances, the volume of which is substantially less than the volume of the calcium calcium sludge, thus lowering the cost of storing them in chemical waste. Zinc and ferrous ions are precipitated from the waste acid in hydroxide. Example 1
Do banky sa dala odpadná kyselina chlo-rovodíková z výroby fenylhydrazínhydro-chloridu, ktorá obsahovala: 81 g/1 HC1„ 121 g/1 Cl", 152 g/1 SO42", 98 g/1 Na+, 742 mg/1 Zn2+, 940 mg/1 anilínu, 5.6 g/1 fenylhyidrazínhydrochloridu.The flask was charged with waste hydrochloric acid from the production of phenylhydrazine hydrochloride containing: 81 g / l HCl "121 g / l Cl", 152 g / l SO42 ", 98 g / l Na +, 742 mg / l Zn 2+, 940 mg / l of aniline, 5.6 g / l of phenylhyidrazine hydrochloride.
Na neutralizáciu sa použili vápenné kaly,ktoré obsahovali: 2.1 % hmotnosti hydroxidu vápenatého, 0,2 % hmotnosti vápenatej soli kaptaxu a 1,9 % hmotnosti smolovitých látok. Výsledná hodnota pH bola 4,8. Výslednáhodnota pH po odfiltrovaní nerozpustnýchlátok zo· suspenzie bola 4,9. Příklad 2Calcium sludges were used for neutralization, containing: 2.1% by weight calcium hydroxide, 0.2% by weight calcium salt and 1.9% by weight pitch. The resulting pH was 4.8. The resulting pH value after filtration of the insoluble precipitates from the suspension was 4.9. Example 2
Postupovalo sa podlá příkladu 1 s týmrozdielom, že kyselina chlorovodíková ob-sahovala: 3.2 % hmotnosti HC1, 6.8 % hmotnosti Cl-, 6.1 % hmotnosti SO42“, 3.6 % hmotnosti Na+, 226 mg/1 Zn2+, 360 mg/1 anilínu a 3.1 g/1 fenylhydrazínhydrochloridu. Vápenaté kaly obsahovali: 36,0 % hmotnosti hydroxidu vápenatého, 3,9 % hmotnosti vápenatej soli kaptaxu, 13.8 % hmotnosti smolovitých látok. Výsledná hodnota pH po neutralizácii bo-la 6,7. Vyzrážané nečistoty sa nechali vyse-dimentovať. Získaný vodný roztok mal hod-notu pH 6,7.Example 1 was followed, except that hydrochloric acid contained: 3.2% by weight HCl, 6.8% by weight Cl-, 6.1% by weight SO42, 3.6% by weight Na +, 226 mg / l Zn2 +, 360 mg / l aniline and 3.1 g / l of phenylhydrazine hydrochloride. Calcium sludges contained: 36.0% by weight calcium hydroxide, 3.9% by weight calcium salt, 13.8% by weight pitch. The resulting pH after neutralization was 6.7. The precipitated impurities were allowed to sediment. The aqueous solution obtained had a pH of 6.7.
Vynález najde uplatněme pri neutralizáciiodpadnej kyseliny chlorovodíkovej, čím sazníži kysloisť odpadných vod. Na neutralizá-ciu sa použijú odpadně vápenaté kaly, kto-ré nahradia hydroxid vápenatý alebo sodný.The invention is applicable to the neutralization of waste hydrochloric acid, thereby reducing the waste water acidity. For neutralization, waste calcium sludge is used to replace calcium or sodium hydroxide.
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CS548285A CS248237B1 (en) | 1985-07-25 | 1985-07-25 | Method of hydrochloric acid neutralization] from the production of phenylhydrazine hydrochloride |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CS548285A CS248237B1 (en) | 1985-07-25 | 1985-07-25 | Method of hydrochloric acid neutralization] from the production of phenylhydrazine hydrochloride |
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| Publication Number | Publication Date |
|---|---|
| CS248237B1 true CS248237B1 (en) | 1987-02-12 |
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CS548285A CS248237B1 (en) | 1985-07-25 | 1985-07-25 | Method of hydrochloric acid neutralization] from the production of phenylhydrazine hydrochloride |
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| CS (1) | CS248237B1 (en) |
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1985
- 1985-07-25 CS CS548285A patent/CS248237B1/en unknown
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