JPS59169902A - Improvement in procedures for waste acid purification - Google Patents

Improvement in procedures for waste acid purification

Info

Publication number
JPS59169902A
JPS59169902A JP4081683A JP4081683A JPS59169902A JP S59169902 A JPS59169902 A JP S59169902A JP 4081683 A JP4081683 A JP 4081683A JP 4081683 A JP4081683 A JP 4081683A JP S59169902 A JPS59169902 A JP S59169902A
Authority
JP
Japan
Prior art keywords
iron
waste
liquid
acid
hydrochloric acid
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP4081683A
Other languages
Japanese (ja)
Inventor
Tadayoshi Karasawa
柄沢 忠義
Katsumi Kono
克己 河野
Takeshi Ida
伊田 壮
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP4081683A priority Critical patent/JPS59169902A/en
Publication of JPS59169902A publication Critical patent/JPS59169902A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C23COATING METALLIC MATERIAL; COATING MATERIAL WITH METALLIC MATERIAL; CHEMICAL SURFACE TREATMENT; DIFFUSION TREATMENT OF METALLIC MATERIAL; COATING BY VACUUM EVAPORATION, BY SPUTTERING, BY ION IMPLANTATION OR BY CHEMICAL VAPOUR DEPOSITION, IN GENERAL; INHIBITING CORROSION OF METALLIC MATERIAL OR INCRUSTATION IN GENERAL
    • C23GCLEANING OR DE-GREASING OF METALLIC MATERIAL BY CHEMICAL METHODS OTHER THAN ELECTROLYSIS
    • C23G1/00Cleaning or pickling metallic material with solutions or molten salts
    • C23G1/36Regeneration of waste pickling liquors

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)
  • Compounds Of Iron (AREA)

Abstract

PURPOSE:The waste acid, after iron-pickling, is heated by heat-exchange with the oxygen-containing waste gas to effect the concentration of the waste acid to near the saturation point of iron chloride, thus the soluble silicon is insolubilized, filtered off, then pyrolysis is effected to recover high-purity iron oxide and hydrochloric acid. CONSTITUTION:The iron-pickling waste acid resulting from passing iron plates through the hydrochloric acid bath for pickling oxidized surfaces is brought into contact in the heat exchanger with the high-temperature oxygen-containing waste gas from the roaster to raise its temperature up to 60 deg.C to the boiling point, further, waste is circulated under contact with the high temperature gas and effect the concentration of the solution until the content of iron chloride reaches 35% to the saturation point. Consequently, the soluble silicon precipitates. After filtration, the filtrate is heated up in the range from the decomposition point of iron chloride to 950 deg.C to recover iron oxide of less than 0.007 SiO2/Fe2O3 and 2.9-2.4 compression density as well as high-purity hydrochloric acid.

Description

【発明の詳細な説明】 本発明は鉄ピクリン液を精製して高純度の酸化鉄及び塩
酸を回収する処理方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a treatment method for purifying iron picrin liquid and recovering highly pure iron oxide and hydrochloric acid.

中 通常の鉄ビクーリン液は鉄板コイルを塩酸酸洗dτ走板
させ、酸化被膜を溶解した廃液である。この廃酸は21
〜26%程度のFeCl2とフリー酸その他め不純物を
含んだ単純な廃液である。
The medium-normal iron biculin solution is a waste solution obtained by dissolving the oxide film by running an iron plate coil through hydrochloric acid pickling dτ. This waste acid is 21
It is a simple waste liquid containing about 26% FeCl2, free acid, and other impurities.

k(01約lO%、FeCl□約25%、Fe013約
2%(時に12%位のものもある。)残部H,Qである
k (about 10% of 01, about 25% of FeCl□, about 2% of Fe013 (sometimes as much as 12%), and the balance H and Q.

不純物の主なものはMn、S i、A I、K、Na、
Oa。
The main impurities are Mn, Si, AI, K, Na,
Oa.

SOI+、C1等の各イオンである。この廃液は熱交換
塔で濃縮され、ロースタ−で加熱分解され、塩酸と酸化
鉄として回収され回収酸化鉄 Fe、O,:99% Sin、   0.05〜0.01% A1.03 0.06〜0.03’ (0,03〜0.
01)%N aLQ =、 o、o+ 01−   0.5〜0.1 (0,01)%(3a 
□   o、o+ ) H2Q     O,3〜0.4 0内はfR槌の異なる場合の値。
These ions are SOI+, C1, etc. This waste liquid is concentrated in a heat exchange tower, thermally decomposed in a roaster, and recovered as hydrochloric acid and iron oxide. ~0.03' (0,03~0.
01)%N aLQ =, o, o+ 01- 0.5~0.1 (0,01)% (3a
□ o, o+ ) H2Q O, 3~0.4 Values within 0 are for different fR hammers.

以上の在来の回収酸及び回収酸化鉄はそのまま鹿業用に
供給されている。しかし前述の酸化鉄に含まれる不純物
は、例えばフェライト磁性材料に用いた場合は一般的特
性を示す1ご(まで高特性を得ることはできない。
The above-mentioned conventional recovered acids and recovered iron oxides are supplied as they are for the deer industry. However, when the impurities contained in the above-mentioned iron oxide are used in, for example, ferrite magnetic materials, it is not possible to obtain properties as high as 1, which exhibits general properties.

そこで本発明ではこの廃酸を従来の昂酸回収装置に若干
の精製処理工程を付加するだけで高純度化するごとに成
功した。
Therefore, in the present invention, this waste acid has been successfully purified to a high degree by simply adding a few purification steps to the conventional citric acid recovery apparatus.

以下、これを説明する。This will be explained below.

先ず廃酸を熱交換塔で、ロースタ−よりυト出する高湿
ガスと接触させra縮する。一般的概念では、廃酸と!
油温υ1ガスとの接触は均等に行なわれるように設■1
され、塩酸の吸収及び熱交換の効率尋を考慮して70’
C付近のガスとして塩酸吸収塔へ送入する。
First, the waste acid is brought into contact with the high humidity gas discharged from the roaster in a heat exchange tower to be condensed. In general concept, waste acid and!
Oil temperature υ1 Designed to ensure even contact with gas ■1
70' considering the efficiency of hydrochloric acid absorption and heat exchange.
It is sent to the hydrochloric acid absorption tower as a gas near C.

このような均等熱交換によって濃縮した場合はS+20
14又は5iC14等は一部酸化又は加水分解されて5
i202(OH) 01のよう!J形状をノfL定され
る物質になる。しかしこのような分子分散状線素水酸化
物は限外ろ過によっても完全を期すことは難かしい。
When concentrated by such uniform heat exchange, S+20
14 or 5iC14 etc. are partially oxidized or hydrolyzed to 5
i202 (OH) Like 01! It becomes a substance whose J shape is determined by fL. However, it is difficult to completely remove such molecularly dispersed linear hydroxide even by ultrafiltration.

以上のことから本発明では熱交換の機構を二段になし、
拝素及びアルミニューム塩を脱水、又は重合度広を進め
Si20゜(01−1)2の形態又はこれに類する不溶
化物あるいは連鎖状に成長する処理を行なう。
From the above, the present invention has a two-stage heat exchange mechanism,
The aluminum salt and the aluminum salt are dehydrated or the degree of polymerization is increased to form a Si20°(01-1)2 form or a similar insolubilized product or to grow in a chain form.

そのため、本発明では熱交換塔の濃縮液は80’C:程
度まで上昇させ、蔽濃度は40〜45%まで、でき得れ
は晶出寸imの濃度にする。この温度で品出すると2水
塩の結晶が生じ、又該高lIJ度液を液滴または、噴霧
状で、5熱ガス中に噴入熱交換させる。この場合噴入液
滴のmがガス量(カロリー量)の−lU捏度に佃えると
よい。このような方法で晶出τJ前の液がガス中に噴霧
されるとl水塩又は無水塩までに脱水される。
Therefore, in the present invention, the concentrate in the heat exchange tower is raised to about 80'C, and the concentration is increased to 40 to 45%, preferably at the crystallization size im. When the product is discharged at this temperature, dihydrate crystals are formed, and the high lIJ liquid is injected into pentathermal gas in the form of droplets or spray for heat exchange. In this case, it is preferable that m of the injected liquid droplet is equal to -1U of the gas amount (calorie amount). When the liquid before crystallization τJ is sprayed into the gas in this manner, it is dehydrated to a hydrated salt or anhydrous salt.

この液滴又は噴霧は高熱のガス流に接触することが重要
で、散布節が飛散したそのy1シ東でもよい。即ち散布
節の飛沫が熱交間になし、無水化した粉末が塩酸吸収塔
に送入されないようにしてもよい。
It is important that the droplets or spray come into contact with the high-temperature gas stream, and may be on the y1 side where the dispersion node is scattered. That is, the droplets from the scattering node may be used for heat exchange, and the anhydrous powder may be prevented from being sent to the hydrochloric acid absorption tower.

要するに、熱交換塔の均等散布液の一部の液滴を高熱ガ
ス流の本流に接触させる状態にすることを骨子とした処
理方法である。このような方法は調整法が悪いと当然の
ことながらガス流は大きく乱ね、均等散布の一部が撹乱
され局部的熱奔流(チャンネリング)となり、塩酸吸収
及び熱交換の効率にも影響する現象が起こる。しかし噴
段のP!j滴又は霧、あるいは散布節の節部、飛沫等が
、高熱ガスの本流に対し満遍なく接触し無水塩又はこれ
に11する脱水状態になるように散布液と熱交換させる
と問題なく処理できる。
In short, this is a treatment method that consists of bringing some of the droplets of the uniformly distributed liquid in the heat exchange tower into contact with the main stream of the high-temperature gas stream. In such a method, if the adjustment method is incorrect, the gas flow will naturally be greatly disturbed, and a part of the uniform distribution will be disturbed, resulting in local heat torrent (channeling), which will also affect the efficiency of hydrochloric acid absorption and heat exchange. A phenomenon occurs. But the P of the fountain! It can be treated without problems if the droplets, mist, knots of spray nodes, splashes, etc. are evenly contacted with the main stream of high-temperature gas and are heat-exchanged with the spray liquid so that they are in a dehydrated state such as anhydrous salt or the like.

以」二の諸注意のもとに濃縮した液は次段の処理法とし
て次の各法がある。
The liquid concentrated under the above two precautions can be processed by the following methods.

1)濃縮液を晶出しない状態でろ過する。1) Filter the concentrated liquid without crystallization.

2)濃縮液に注水し、晶出を防止して冷却ろ過すご。2) Pour water into the concentrate to prevent crystallization and cool and filter.

3)濃縮液をlllr以上、vIましくは1週間程度放
14シ、ついで注水、結晶を溶M後ろ過する。
3) Leave the concentrated solution for at least 14 hours, or about 1 week, and then pour water to dissolve the crystals and filter.

4)濃縮液をFeで中−利し、ろ過する。4) The concentrated solution is neutralized with Fe and filtered.

5)上記中和液に炭酸塩を添加撹拌後ろ過する。5) Add carbonate to the neutralized solution, stir, and filter.

以−にの各法により得た液を加熱分解すると次のような
物が得られる。
When the liquid obtained by each method described above is thermally decomposed, the following products are obtained.

No、I    No、’2    No、3    
No、4    No、5Fe20399.34  9
9.3  99.3+   99.32  99.34
Mn0    O,290,280,300,280,
27Si02  0.005  0.Oo3   o、
o02  0.0045 0.0032A10  0.
04   0.05+   0.051  0.026
6 0.0+9401”−0,0560,0580,0
580,0590,0571−]2Q    O,26
0,270,270,300,31X      −−
−−−−−
No, I No, '2 No, 3
No, 4 No, 5Fe20399.34 9
9.3 99.3+ 99.32 99.34
Mn0O, 290, 280, 300, 280,
27Si02 0.005 0. Oo3 o,
o02 0.0045 0.0032A10 0.
04 0.05+ 0.051 0.026
6 0.0+9401"-0,0560,0580,0
580,0590,0571-]2Q O,26
0,270,270,300,31X --
------

Claims (1)

【特許請求の範囲】 /)鉄ピクリン廃酸に酸素含有布ガスを接触させ、60
+C−沸pa温度以下の間に昇温し、塩化鉄分を35%
〜飽和点までの間で熱高酸を循環し、且高熱ガスと接触
させながら濃縮することに1め よって溶解性踵素を不溶化し、該濃縮液をろ過し、後ろ
液をの酸化鉄及び高純度塩酸を回収する廃酸処理方法。 2)特許請求範囲第一項の濃縮液に晶出防止のできる爪
の純水を注水して冷却し、ろ過加熱分解する特許請求範
囲第一項の処理方法。 3)特許請求範囲第一項の濃縮液を24時間以上放置し
、ついで注水して結晶を溶解し、ろ過、加熱分解する特
許請求範囲第一項の処理方法。 ≠)特許請求範囲第一項のl1IlF4液をFeで中和
し、ろ過、加熱分解する特許請求範囲第一項の処理方法
。 S)特許請求範囲第四項の中和液に炭酸鉄、炭酸グワニ
ジン、炭酸亜鉛、炭酸マンガンの一種又は二種以上を添
加し加熱、撹拌後、ろ過、加熱分解する特許請求範囲第
四項の処理方法。
[Claims] /) Bringing oxygen-containing cloth gas into contact with iron picrin waste acid,
+C- Raise the temperature while below the boiling temperature and reduce the iron chloride content to 35%
~ the saturation point, circulating hot high acid, and concentrating while contacting with high temperature gas to insolubilize the soluble hexachloride, filter the concentrated liquid, and remove the residual liquid from iron oxide and A waste acid treatment method that recovers high-purity hydrochloric acid. 2) The treatment method according to claim 1, which comprises pouring nail pure water that can prevent crystallization into the concentrated liquid according to claim 1, cooling it, filtering and heating it for decomposition. 3) The treatment method according to claim 1, which comprises leaving the concentrated solution according to claim 1 for 24 hours or more, then pouring water to dissolve the crystals, filtering, and thermally decomposing the solution. ≠) A treatment method according to claim 1, in which the l1IIF4 liquid according to claim 1 is neutralized with Fe, filtered, and thermally decomposed. S) Adding one or more of iron carbonate, guanidine carbonate, zinc carbonate, and manganese carbonate to the neutralized liquid in claim 4, heating and stirring, filtering, and thermal decomposition. Processing method.
JP4081683A 1983-03-14 1983-03-14 Improvement in procedures for waste acid purification Pending JPS59169902A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4081683A JPS59169902A (en) 1983-03-14 1983-03-14 Improvement in procedures for waste acid purification

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4081683A JPS59169902A (en) 1983-03-14 1983-03-14 Improvement in procedures for waste acid purification

Publications (1)

Publication Number Publication Date
JPS59169902A true JPS59169902A (en) 1984-09-26

Family

ID=12591173

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4081683A Pending JPS59169902A (en) 1983-03-14 1983-03-14 Improvement in procedures for waste acid purification

Country Status (1)

Country Link
JP (1) JPS59169902A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5296001A (en) * 1990-06-15 1994-03-22 Sollac Process for separating silicic compounds from cleaning baths and plant for its application
AT13601U1 (en) * 2012-09-06 2014-04-15 Astec Engineering Gmbh Purification and desiccation of spent acid baths using combined microfiltration techniques
CN105862053A (en) * 2016-04-06 2016-08-17 中冶南方工程技术有限公司 Regeneration method and system for hydrochloric acid waste liquid
CN105887108A (en) * 2016-04-06 2016-08-24 中冶南方工程技术有限公司 Hydrochloric acid waste liquid regenerating method and system

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5296001A (en) * 1990-06-15 1994-03-22 Sollac Process for separating silicic compounds from cleaning baths and plant for its application
AT13601U1 (en) * 2012-09-06 2014-04-15 Astec Engineering Gmbh Purification and desiccation of spent acid baths using combined microfiltration techniques
CN105862053A (en) * 2016-04-06 2016-08-17 中冶南方工程技术有限公司 Regeneration method and system for hydrochloric acid waste liquid
CN105887108A (en) * 2016-04-06 2016-08-24 中冶南方工程技术有限公司 Hydrochloric acid waste liquid regenerating method and system

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