JPS5822278B2 - Processing method for pickling waste acid - Google Patents
Processing method for pickling waste acidInfo
- Publication number
- JPS5822278B2 JPS5822278B2 JP2849778A JP2849778A JPS5822278B2 JP S5822278 B2 JPS5822278 B2 JP S5822278B2 JP 2849778 A JP2849778 A JP 2849778A JP 2849778 A JP2849778 A JP 2849778A JP S5822278 B2 JPS5822278 B2 JP S5822278B2
- Authority
- JP
- Japan
- Prior art keywords
- caustic soda
- waste acid
- pickling waste
- waste
- processing method
- 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.)
- Expired
Links
Landscapes
- Removal Of Specific Substances (AREA)
- Paper (AREA)
Description
【発明の詳細な説明】
本発明は鋳造品の砂落し等に使用した珪酸弁を含有する
所謂廃苛性ソーダ中から珪酸弁を除去して苛性ソーダを
再生する場合に発生する廃棄汚泥により酸洗廃酸を中和
処理する方法に関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention uses waste sludge generated when caustic soda is recycled by removing silicic acid valves from so-called waste caustic soda containing silicic acid valves used for removing sand from cast products, etc. to pickling waste acid. The present invention relates to a method for neutralizing.
従来砂鋳型を使用した鋳造品の表面若しくは内面に焼付
いた砂を除去する手段には、ノックアウト、ハイドロジ
ェット、ショツトブラストまたはサンドブラスト等があ
るが、鋳造品の内面に焼付いた砂を除去することが極め
て困難であると共に多大の工数を要する。Conventional methods for removing sand baked on the surface or inner surface of a cast product using a sand mold include knockout, hydro jet, shot blasting, sandblasting, etc.; This is extremely difficult and requires a large amount of man-hours.
特にロストワックス法等による所謂精密鋳造品において
は、鋳造品表面に打痕その他の疵が生成することは許さ
れない。Particularly in so-called precision casting products made by the lost wax method or the like, dents and other flaws are not allowed to form on the surface of the cast product.
従つて特に複雑な鋳造品若しくは寸法精度の厳しい鋳造
品の砂落しには、500〜550℃の溶融苛性ソーダ中
に浸漬するタルトバス法が使用されるのが一般である。Therefore, to remove sand from particularly complex cast products or cast products with strict dimensional accuracy, the tart bath method, in which the product is immersed in molten caustic soda at 500 to 550° C., is generally used.
この場合長期間の使用により、苛性ソーダ中に砂が堆積
若しくは一部が反応してNa2O・5i02等の水ガラ
スを形成し、ンルトの老化となるので、堆積した砂をメ
ルトバス中から掻揚げる必要がある。In this case, due to long-term use, sand accumulates in the caustic soda or a part of it reacts to form water glass such as Na2O. be.
このようにして掻揚げた堆積砂は微粒であるため多量の
苛性ソーダと共存し、直ちに廃棄することができず、一
般に塩酸、硫酸等によって中和処理を行なっている。Since the accumulated sand scraped up in this way is fine particles, it coexists with a large amount of caustic soda and cannot be immediately disposed of, so it is generally neutralized with hydrochloric acid, sulfuric acid, etc.
しかしながら、上記中和処理によって廃苛性ソーダを廃
棄することは徒らに廃棄物のみを増加させるのみならず
、省資源および生産性の観点から極めて不都合である。However, disposing of waste caustic soda through the above-mentioned neutralization process not only increases the amount of waste, but is also extremely inconvenient from the viewpoint of resource conservation and productivity.
本発明は上記従来分法に存する欠点を解消し、所謂廃苛
性ソーダを廃棄することな(、これを有効に利用するこ
とにより、単に苛性ソーダとして再生することのみに留
まらず、多方面への利用方法を提供することを目的とす
るものである。The present invention eliminates the drawbacks of the conventional separation method described above, and by effectively utilizing so-called waste caustic soda, it is not limited to simply recycling it as caustic soda, but it can also be used in a variety of ways. The purpose is to provide the following.
第1図は本発明方法の実施例を示す説明図である。FIG. 1 is an explanatory diagram showing an embodiment of the method of the present invention.
同図において1は溶解槽であり、珪酸弁を含有する所謂
廃苛性ンーダaを水すと共に収容する。In the figure, reference numeral 1 denotes a dissolution tank, which accommodates so-called waste caustic powder a containing silicic acid valves together with a water basin.
攪拌機2によって攪拌することにより、廃苛性ソーダa
中に含有若しくは混入する鋳物砂は溶解槽1底部に沈殿
分離する。By stirring with the stirrer 2, waste caustic soda a
The foundry sand contained or mixed therein is precipitated and separated at the bottom of the melting tank 1.
次に水溶液をポンプ3によって反応槽4に移送し、例え
ば高温蒸気Cによって加熱すると共に石灰乳dを添加し
、攪拌機5によって攪拌する。Next, the aqueous solution is transferred to a reaction tank 4 by a pump 3, heated, for example, with high-temperature steam C, milk of lime d is added, and stirred by a stirrer 5.
この場合水溶液中に溶存するNa2O・5i02等水ガ
ラスは、下記皮革によって分解する。In this case, water glasses such as Na2O.5i02 dissolved in the aqueous solution are decomposed by the following leather.
Na20−8 i 02 +Ca (OH) 2−+2
NaOH+CaO−8i02
次にdz’cポンプ6によって冷却器7を介してタラリ
ファイヤー8に移送してCaO−8iO2を沈殿分離す
れば、タラリファイヤ−8上部の溢水樋9よりNaOH
水溶液eを抽出し得るのである。Na20-8 i 02 +Ca (OH) 2-+2
NaOH+CaO-8i02 Next, the dz'c pump 6 transfers the CaO-8iO2 to the tallifier 8 via the cooler 7 to precipitate and separate the CaO-8iO2.
The aqueous solution e can be extracted.
なお沈殿物若しくは汚泥fはタラリファイヤ−8下部か
ら抽出する。Incidentally, the sediment or sludge f is extracted from the lower part of the tallifier-8.
次に第1図における反応槽4における加熱温度とCa添
加量の関係について説明する。Next, the relationship between the heating temperature in the reaction tank 4 and the amount of Ca added in FIG. 1 will be explained.
第2図はCa / S io 2のモル比と5i02の
除去率との関係を示す図である。FIG. 2 is a diagram showing the relationship between the molar ratio of Ca/S io 2 and the removal rate of 5i02.
同図において曲線AおよびBは各々常温および80℃に
加熱した場合を示すもので、5i02除去率は明らかに
曲線Bにおけるものの方が高い。In the figure, curves A and B show the cases when heated to room temperature and 80° C., respectively, and the 5i02 removal rate in curve B is clearly higher.
すなわち常温における曲MAの場合には、Ca/5i0
2のモル比が10以上にならないと5i02の除去率が
満足できないのに対して、80℃に加熱した場合の曲線
Bにおいては、同モル比が3〜4において同等の除去率
が得られている。In other words, in the case of song MA at room temperature, Ca/5i0
The removal rate of 5i02 cannot be satisfied unless the molar ratio of 2 is 10 or more, whereas in curve B when heated to 80°C, the same removal rate is obtained when the molar ratio is 3 to 4. There is.
これは反応槽4内の水溶液を加熱することによって、前
記の分離反応が促進される結果である。This is a result of the separation reaction being promoted by heating the aqueous solution in the reaction tank 4.
。なお5i02に対する添加Caのモル比が3未満であ
るときは、5i02除去率が不満足であるので3以上と
するが、第2図から明らかなように、モル比が6付近で
略飽和するので、経済的範囲で適宜選定すればよい。. Note that when the molar ratio of added Ca to 5i02 is less than 3, the 5i02 removal rate is unsatisfactory, so it is set to 3 or more, but as is clear from FIG. 2, the molar ratio is approximately saturated at around 6, so It may be selected appropriately within an economical range.
また反応槽4内における水溶2液の加熱温度は、本実施
しlにおいては80℃としたが、実験の結果60℃以上
であれば、前記モル比の範囲内で満足し得るSiO□除
去率が得られる。In addition, the heating temperature of the two aqueous solutions in the reaction tank 4 was 80°C in this experiment, but as a result of the experiment, if it is 60°C or higher, the SiO□ removal rate can be satisfied within the above molar ratio range. is obtained.
更にまた反応槽4において添加すべきCaとしては、C
a (OH) 2の他CaOであっても同様のS分離沈
殿作用を呈することは勿論である。Furthermore, as the Ca to be added in the reaction tank 4, C
Of course, CaO other than a (OH) 2 exhibits the same S separation and precipitation effect.
而して第1図においてタラリファイヤー8の上澄液eは
、NaOHの再生手段に移送するが、沈殿した汚泥fは
強アルカリ性を有するが、一般には廃棄物として処理さ
れる。In FIG. 1, the supernatant liquid e from the tallifier 8 is transferred to NaOH regeneration means, but the precipitated sludge f has strong alkalinity, but is generally treated as waste.
本発明においては、この汚泥を脱液手段10に移送して
脱液し、貯槽11にケーキとして収容する。In the present invention, this sludge is transferred to a dewatering means 10 to be dehydrated and stored in a storage tank 11 as a cake.
なお脱液手段10からの漬液gは、反応槽4に返戻して
再び処理するのである。The soaking liquid g from the liquid removing means 10 is returned to the reaction tank 4 and processed again.
次に12は酸洗廃酸処理手段であり、貯槽11に収容す
るケーキを上記酸洗廃酸処理手段12中において混合す
ることにより、酸の中和処理が可能である。Next, 12 is a pickling waste acid treatment means, and by mixing the cake stored in the storage tank 11 in the pickling waste acid treatment means 12, acid neutralization treatment is possible.
廃酸処理においては一般に苛性ソーダが使用されるが、
上記汚泥fによる中和処理の方が、苛性ソーダによるも
のより沈殿作用が良好である。Caustic soda is generally used in waste acid treatment, but
The neutralization treatment using the sludge f has a better settling effect than the neutralization treatment using caustic soda.
本発明は以上記述のような構成および作用であるから、
下記の効果がある。Since the present invention has the structure and operation as described above,
It has the following effects.
(1)廃苛性ソーダの再生手段において発生する分離沈
殿汚泥を廃棄することなく活用できるため、省資源効果
と共に、廃棄物による環境汚染を完全に防止し得る。(1) Since the separated and precipitated sludge generated in the means for recycling waste caustic soda can be utilized without being disposed of, it is possible to save resources and completely prevent environmental pollution caused by waste.
(2)廃酸中和作用、特に沈殿作用が苛性ソーダより良
好であると共に、ケーキ状であるため取扱いが容易であ
る。(2) It has a better neutralizing action, especially a precipitation action, than caustic soda, and is easy to handle because it is cake-like.
第1図は本発明方法の実施例を示す説明図、第2図はC
a/SiO2モル比とSiO□除去率との関係を示す線
図である。
1・・・溶解槽、4・・・反応槽、8川タラリフアイヤ
ー、10・・・脱液手段、12・・・廃酸処理手段。FIG. 1 is an explanatory diagram showing an embodiment of the method of the present invention, and FIG. 2 is a C
FIG. 2 is a diagram showing the relationship between the a/SiO2 molar ratio and the SiO□ removal rate. DESCRIPTION OF SYMBOLS 1...Dissolution tank, 4...Reaction tank, 8-river dryer, 10...Deliquor removal means, 12...Waste acid treatment means.
Claims (1)
粒分を沈殿除去した後、Ca(OH)2またはCaOを
5i02に対するCaのモル比が3以上になるように添
加1すると共に、水溶液を60℃以上に加熱して珪酸弁
をCa()SiO□ として沈殿分離し、該汚泥を脱液
して酸洗廃酸と混合させることを特徴とする酸洗廃酸の
処理方法。1. After dissolving waste caustic soda containing a silicic acid valve in water and precipitating and removing sand grains, add Ca(OH)2 or CaO so that the molar ratio of Ca to 5i02 is 3 or more, and add an aqueous solution. A method for treating pickling waste acid, which comprises heating to 60° C. or higher to precipitate and separate silicate valves as Ca()SiO□, deliquifying the sludge and mixing it with pickling waste acid.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2849778A JPS5822278B2 (en) | 1978-03-13 | 1978-03-13 | Processing method for pickling waste acid |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2849778A JPS5822278B2 (en) | 1978-03-13 | 1978-03-13 | Processing method for pickling waste acid |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS54120282A JPS54120282A (en) | 1979-09-18 |
JPS5822278B2 true JPS5822278B2 (en) | 1983-05-07 |
Family
ID=12250301
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2849778A Expired JPS5822278B2 (en) | 1978-03-13 | 1978-03-13 | Processing method for pickling waste acid |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5822278B2 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111233217A (en) * | 2020-04-24 | 2020-06-05 | 佛山市锐创冶金设备制造有限公司 | A waste liquid recovery unit and stainless steel pickling line for stainless steel production |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6045692A (en) * | 1983-08-18 | 1985-03-12 | 石川島播磨重工業株式会社 | Removal of silica from pulp black liquor and green liquor |
-
1978
- 1978-03-13 JP JP2849778A patent/JPS5822278B2/en not_active Expired
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111233217A (en) * | 2020-04-24 | 2020-06-05 | 佛山市锐创冶金设备制造有限公司 | A waste liquid recovery unit and stainless steel pickling line for stainless steel production |
CN111233217B (en) * | 2020-04-24 | 2020-08-04 | 佛山市锐创冶金设备制造有限公司 | A waste liquid recovery unit and stainless steel pickling line for stainless steel production |
Also Published As
Publication number | Publication date |
---|---|
JPS54120282A (en) | 1979-09-18 |
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