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JPS6142769B2 - - Google Patents
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JPS6142769B2 - - Google Patents

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Publication number
JPS6142769B2
JPS6142769B2 JP3264382A JP3264382A JPS6142769B2 JP S6142769 B2 JPS6142769 B2 JP S6142769B2 JP 3264382 A JP3264382 A JP 3264382A JP 3264382 A JP3264382 A JP 3264382A JP S6142769 B2 JPS6142769 B2 JP S6142769B2
Authority
JP
Japan
Prior art keywords
manganese
residue
slurry
solution
iron
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
Application number
JP3264382A
Other languages
Japanese (ja)
Other versions
JPS58151437A (en
Inventor
Jitoku Honda
Minoru Oochi
Yoshihiro Nakayama
Keiichiro Ishikawa
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.)
Japan Metals and Chemical Co Ltd
Original Assignee
Japan Metals and Chemical Co Ltd
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 Japan Metals and Chemical Co Ltd filed Critical Japan Metals and Chemical Co Ltd
Priority to JP57032643A priority Critical patent/JPS58151437A/en
Publication of JPS58151437A publication Critical patent/JPS58151437A/en
Publication of JPS6142769B2 publication Critical patent/JPS6142769B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Inorganic Compounds Of Heavy Metals (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Electrolytic Production Of Metals (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

本発明はマンガン鉱石の処理法であつて、その
目的は、該マンガン鉱石粉末のスラリー中の固形
物の過分離を容易ならしめると共に、固形物を
分離した溶液中に、実質的に鉄、アルミニウムを
含まない溶液を得る方法を提供するにある。 また、本発明の他の目的は、スラリー中の固形
物を分離した溶液を電解金属マンガン、電解二酸
化マンガン等の製造用原料または各種工業用薬品
として使用すると共に、スラリーから過分離さ
れた固形物をフエロマンガン用原料として使用す
ることにある。 現在、電解金属マンガン、電解二酸化マンガン
等に使用されるマンガン塩溶液は、予めマンガン
鉱石を還元焙焼したものに、硫酸または塩酸等の
酸を添加し、マンガン鉱石中のマンガン分を硫酸
マンガンまたは塩化マンガン等のマンガン塩溶液
として製造している。 従来、前記抽出工程ではマンガン分を極力抽出
するため、スラリーのPHを2.0以下の強酸性と
し、マンガン抽出率を85%以上としている。 しかし、マンガン抽出時のPHを2.0以下とする
とマンガン鉱石中のマンガンのみならず、鉄、ア
ルミニウム等も同時に溶液中に抽出され溶解され
る。そのため、従来この鉄、アルミニウム等の不
純物を除去するため、溶液中にアルカリ分、例え
ば炭酸カルシウムを加えて中和し、鉄、アルミニ
ウム等を水酸化物の沈澱とし、これを過し、固
形物と共に分離している。 しかし、上述において沈澱する水酸化物は非常
に微細であつて、過助剤を使用しても速やかな
過は困難である。 また、炭酸カルシウムの代りに還元マンガン鉱
石を中和剤として使用する方法も提案されている
が、過性は炭酸カルシウムに比較して悪い。さ
らに、炭酸カルシウム、還元マンガン鉱石等を用
いて中和する場合は、固形物(以下残渣という)
の総量が増加し、従つて残渣の過を一層困難に
するという欠点がある。 前述のように残渣の過性の悪化は、同時に残
渣中に硫酸マンガン等の塩の含有を許し、数回の
洗滌によつても残渣中の硫酸マンガン等を除去す
ることは困難である。このように残渣中に硫酸根
を含むものは、必然的に原料中の硫黄の増加を招
来し、そのためかかる残渣はフエロマンガン用原
料として再利用することができず、また塩化マン
ガンを含むものは塩素ガスを発生し、環境汚染は
もとより、塩素ガスによつて炉上の機器が侵され
るため、かかる残渣は専ら廃棄されている。ま
た、廃棄する場合には、水溶性マンガン塩溶出防
止のために水酸化カルシウム、セメント等の添加
が必要である。 本発明は特許請求の範囲に記載した構成とする
ことによつて、前述従来法の有する諸欠点を解消
し、過が容易で、かつ液中に鉄、アルミニウ
ム等を実質的に含有しないものを得ると共に、該
溶液を電解金属マンガン、電解二酸化マンガン等
の原料または各種工業薬品として使用でき、過
によつて分離された残渣をフエロマンガン用原料
として再利用できる方法を得ることができた。 つぎに、抽出時のPHを種々変化させて、PHとマ
ンガン、鉄、アルミニウム等の溶解率との関係を
実験例1によつて説明する。 実験例 1 第1表に示すごとき還元マンガン鉱石を、撹拌
機付き10容器に該還元マンガン鉱石2500g、水
6を加えてスラリーとし、50%硫酸を注加し、
1.5時間後温度85℃で1.5時間保持した後過して
溶液中のマンガン、鉄、アルミニウムの溶解率を
求め、第2表の結果を得た。
The present invention is a method for treating manganese ore, and its purpose is to facilitate the excessive separation of solids in a slurry of manganese ore powder, and to substantially remove iron and aluminum from the solution from which the solids have been separated. The purpose of the present invention is to provide a method for obtaining a solution free of . Another object of the present invention is to use the solution from which the solids in the slurry have been separated as a raw material for producing electrolytic manganese metal, electrolytic manganese dioxide, etc. or as various industrial chemicals, and to The objective is to use it as a raw material for ferromanganese. Currently, the manganese salt solution used for electrolytic metal manganese, electrolytic manganese dioxide, etc. is made by adding acid such as sulfuric acid or hydrochloric acid to manganese ore that has been reduced and roasted in advance, and then converting the manganese content in the manganese ore into manganese sulfate or It is manufactured as a manganese salt solution such as manganese chloride. Conventionally, in the extraction process, in order to extract as much manganese as possible, the pH of the slurry is made strongly acidic at 2.0 or less, and the manganese extraction rate is set at 85% or more. However, if the pH during manganese extraction is set to 2.0 or less, not only the manganese in the manganese ore but also iron, aluminum, etc. will be extracted and dissolved into the solution at the same time. Therefore, conventionally, in order to remove impurities such as iron and aluminum, an alkaline component such as calcium carbonate is added to the solution to neutralize it, and the iron, aluminum, etc. are precipitated as hydroxide, which is then filtered to form solids. They are separated from each other. However, the hydroxide that precipitates in the above method is very fine and it is difficult to quickly filter it out even if a super-aid is used. A method of using reduced manganese ore as a neutralizing agent instead of calcium carbonate has also been proposed, but the neutralization is worse than that of calcium carbonate. Furthermore, when neutralizing with calcium carbonate, reduced manganese ore, etc., solid matter (hereinafter referred to as residue)
The disadvantage is that the total amount of filtrate increases, thus making filtering the residue more difficult. As mentioned above, the excessive deterioration of the residue also allows salts such as manganese sulfate to be contained in the residue, and it is difficult to remove manganese sulfate and the like from the residue even by washing several times. In this way, residues containing sulfate groups inevitably lead to an increase in sulfur in the raw material, and therefore such residues cannot be reused as raw materials for ferromanganese, and those containing manganese chloride are Such residue is exclusively discarded because it generates gas and not only pollutes the environment but also damages equipment on the furnace due to chlorine gas. Furthermore, when discarding, it is necessary to add calcium hydroxide, cement, etc. to prevent the elution of water-soluble manganese salts. The present invention solves the various drawbacks of the conventional methods described above by having the structure described in the claims, and provides a liquid that is easy to clean and does not substantially contain iron, aluminum, etc. At the same time, it was possible to obtain a method in which the solution can be used as a raw material for electrolytic manganese metal, electrolytic manganese dioxide, etc., or as various industrial chemicals, and the residue separated by filtration can be reused as a raw material for ferromanganese. Next, the relationship between PH and the dissolution rate of manganese, iron, aluminum, etc. will be explained using Experimental Example 1 by varying the PH during extraction. Experimental Example 1 Reduced manganese ore as shown in Table 1 was slurried by adding 2,500 g of the reduced manganese ore and 6 parts of water to 10 containers equipped with a stirrer, and adding 50% sulfuric acid.
After 1.5 hours, the temperature was maintained at 85° C. for 1.5 hours and filtered to determine the dissolution rate of manganese, iron, and aluminum in the solution, and the results shown in Table 2 were obtained.

【表】【table】

【表】 第2表から明らかなごとく、PH3.0におけるマ
ンガンの溶解率は82%であり、PH0.5では90.5%
で、その溶解率の増加は僅かであるに対し、鉄、
アルミニウムの溶解率は、PH2.8以上では極く僅
かであるに対し、PH2.5以下では急激に増加して
いるのが認められる。 つぎに、マンガンを抽出した後のスラリーを
過分離する状態を実験例2として説明する。 実験例 2 実験例1と同一原料、同一装置で各PH値で溶解
処理し、撹拌しつつPHを5.0〜5.2とした後、直径
23cmのヌツチエで減圧吸引過して残渣を過分
離し、該残渣を1.5の水を3回に分けて洗滌
し、第3表のごとき結果を得た。なお、PH0.5〜
2.5の場合は還元マンガン鉱を添加してPH5.0〜5.2
に調整する。
[Table] As is clear from Table 2, the dissolution rate of manganese at PH3.0 is 82%, and at PH0.5 it is 90.5%.
The increase in the dissolution rate was small, whereas iron,
It is observed that the dissolution rate of aluminum is extremely small at pH 2.8 or higher, but rapidly increases at pH 2.5 or lower. Next, a state in which the slurry after extracting manganese is over-separated will be explained as Experimental Example 2. Experimental Example 2 The same raw materials and the same equipment as Experimental Example 1 were used for dissolution treatment at each pH value, and after adjusting the pH to 5.0 to 5.2 while stirring, the diameter
The residue was separated by vacuum suction using a 23 cm filter, and the residue was washed with 1.5 parts of water in three portions to obtain the results shown in Table 3. In addition, PH0.5~
If the pH is 2.5, add reduced manganese ore to adjust the pH to 5.0 to 5.2.
Adjust to.

【表】【table】

【表】 第3表から明らかなように過速度はPH2.5以
下では、PHの低下と共に大巾に減少しており、他
方過分離した残渣量はPHの低下と共に増大して
いるのが認められる。 これに対し、PH2.8〜4.0においては過速度お
よび残渣量には著しい変化は認められない。 また、残渣中の水分含量はPH2.5以下ではPHの
低下と共に増加しており、また残渣中の水溶性マ
ンガン量および全硫黄もPH2.5以下ではPHの低下
と共に増加している。 以上の結果から、PH2.5以下の場合では溶液中
に抽出された鉄、アルミニウムがPHを5.0〜5.2と
することによつてゲル状の沈澱となり、残渣とし
て分離されるが、鉄の沈澱物がゲル状であるた
め、これに水分および硫酸塩が捕捉されているた
め、PH0.5〜2.5では洗滌が充分に行えず、また
過速度を大巾に減少しているものと考えられる。 これに対し、PH2.8〜4.0とした場合には溶液中
に鉄、アルミニウムがほとんど抽出されていない
ため、前記のごときゲル状の沈澱物による過速
度の大巾な低下もなく、また残渣の洗滌不充分と
いうことがなく、従つて残渣中にマンガン塩の残
存するおそれは大巾に減少する。 さらにまた、本発明のようにスラリーのPHを
2.8〜4.0と保持して撹拌するときは、何等これに
炭酸カルシウムのごとき中和剤を添加することな
く単なる撹拌操作によつてPH5.0〜5.2とすること
ができるから、溶液中の遊離硫酸および溶液中に
抽出されている微量の鉄、アルミニウム等も除去
することができる。なお、前記実験例2では撹拌
保持後のPHが5.0〜5.2であるが、マンガン塩溶液
と残渣とのマンガンの分配割合によつてPH4.0〜
6.0の範囲で適宜調整することができ、またPH調
整時に撹拌しつつ還元マンガン鉱を少量添加して
もよい。 以上のごとく本発明はマンガン鉱石のスラリー
のPHを2.8〜4.0と保持し、何等中和剤を加えず撹
拌することによつて過速度を大巾に向上するこ
とができ、しかも過によつて得られるマンガン
塩溶液は鉄、アルミニウムの抽出のほとんどな
く、かつ遊離硫酸も除去することができるから、
該マンガン塩溶液を電解金属マンガン、電解二酸
化マンガンの製造さらに各種工業用薬品の原料と
して使用することができると共に、過分離によ
つて得られる残渣は硫酸塩、塩酸塩等が除去され
ているため、この残渣をフエロマンガン用原料と
して再使用することができ、未利用資源の活用が
図られ、さらにコストの低減を図ることができ
る。 実施例 1 実験例1で使用した還元マンガン鉱石粉末100
Kgを、内容積500の撹拌機付き溶解タンクに投
入し、水240を加えてスラリーとした。 つぎに(1+1)硫酸150Kgを、スラリーのPH
が約3.0を維持するように1.5時間を費やして注加
した。 その後30分間撹拌を継続した後、直径60cmの真
空過器で残渣を分離し、水40を3回に分けて
残渣を洗滌する(なお、この洗滌液は次回のスラ
リー調整用として使用)。この場合の過速度は
160/m2・Hrで過操作は非常に容易であつ
た。 前述過分離によつて2.9mol/の硫酸マンガ
ン溶液272と、0.87mol/の硫酸マンガンの洗
滌液110が得られた。これはマンガン抽出率
78.8%に相当する。またこの場合の鉄、アルミニ
ウムはほとんど抽出されていない。 また、残渣は乾重量37.9Kgであり全マンガン含
有率31.5%、全硫黄含有率1.1%で、これをフエ
ロマンガン製造の前処理工程の焼結工程において
マンガン鉱石に対し10%配合して使用し、従来品
と遜色のないフエロマンガンを得た。 実施例 2 実施例1と同一の還元マンガン鉱石粉末10Kgを
内容積60の撹拌機付き溶解タンクに投入し、水
6を加えてスラリーとした。 つぎに(1+1)塩酸31.9Kgを、スラリーのPH
が3.0〜3.5を維持するように1.5時間を費やして注
加した。 その後、30分間撹拌を継続した後、直径30cmの
ヌツチエで真空過し、水152回に分けて残渣
を洗滌する(洗滌液は実施例1と同様次回のスラ
リー調整用として使用)。この場合の過速度は
150/m2.Hrで過操作は非常に容易であつ
た。 前述において得られた塩酸マンガン溶液、洗滌
液および残渣は第4表の通りである。
[Table] As is clear from Table 3, the overspeed decreases significantly as the pH decreases below PH2.5, while the amount of over-separated residue increases as the pH decreases. It will be done. On the other hand, at pH 2.8 to 4.0, no significant changes were observed in the overspeed and amount of residue. Furthermore, the water content in the residue increases as the pH decreases below PH2.5, and the amount of water-soluble manganese and total sulfur in the residue also increases as the pH decreases below PH2.5. From the above results, when the pH is below 2.5, the iron and aluminum extracted into the solution become a gel-like precipitate by adjusting the pH to 5.0 to 5.2, and are separated as a residue. Since it is in the form of a gel, water and sulfate are trapped in it, so it is thought that cleaning cannot be performed sufficiently at pH 0.5 to 2.5, and that the overspeed is greatly reduced. On the other hand, when the pH is set to 2.8 to 4.0, almost no iron or aluminum is extracted into the solution, so there is no significant decrease in overspeed due to the gel-like precipitate mentioned above, and there is no residue. There is no problem of insufficient washing, and therefore the risk of manganese salt remaining in the residue is greatly reduced. Furthermore, as in the present invention, the pH of the slurry
When stirring while maintaining the pH at 2.8 to 4.0, the pH can be adjusted to 5.0 to 5.2 by simple stirring without adding any neutralizing agent such as calcium carbonate, so free sulfuric acid in the solution It is also possible to remove trace amounts of iron, aluminum, etc. extracted into the solution. In addition, in Experimental Example 2, the pH after stirring and holding is 5.0 to 5.2, but the pH varies from 4.0 to 4.0 depending on the distribution ratio of manganese between the manganese salt solution and the residue.
It can be adjusted as appropriate within the range of 6.0, and a small amount of reduced manganese ore may be added while stirring when adjusting the pH. As described above, the present invention can greatly improve the overspeed by maintaining the pH of the manganese ore slurry at 2.8 to 4.0 and stirring without adding any neutralizing agent. The resulting manganese salt solution has almost no extraction of iron and aluminum, and free sulfuric acid can also be removed.
The manganese salt solution can be used for the production of electrolytic manganese metal, electrolytic manganese dioxide, and as a raw material for various industrial chemicals, and the residue obtained by over-separation has sulfates, hydrochlorides, etc. removed. This residue can be reused as a raw material for ferromanganese, making use of unused resources and further reducing costs. Example 1 Reduced manganese ore powder 100 used in Experimental Example 1
Kg was put into a dissolution tank with an internal volume of 500 ml and equipped with a stirrer, and 240 ml of water was added to form a slurry. Next, add 150 kg of (1+1) sulfuric acid to the slurry's PH
I spent 1.5 hours adding it to keep it at about 3.0. After continuing stirring for 30 minutes, the residue is separated using a vacuum filter with a diameter of 60 cm, and the residue is washed with 40 g of water in three portions (this washing liquid will be used for the next slurry preparation). The overspeed in this case is
At 160/m 2 ·Hr, over-operation was very easy. Through the above-mentioned over-separation, a 2.9 mol/manganese sulfate solution 272 and a 0.87 mol/manganese sulfate washing solution 110 were obtained. This is the manganese extraction rate
This corresponds to 78.8%. Also, almost no iron or aluminum is extracted in this case. In addition, the residue has a dry weight of 37.9 kg, a total manganese content of 31.5%, and a total sulfur content of 1.1%, which is used in the sintering process of the pretreatment process for ferromanganese production by adding 10% to the manganese ore. We obtained fluoromanganese that is comparable to conventional products. Example 2 10 kg of the same reduced manganese ore powder as in Example 1 was put into a dissolving tank with an internal volume of 60 mm and equipped with a stirrer, and 66 g of water was added to form a slurry. Next, add 31.9 kg of (1+1) hydrochloric acid to the pH of the slurry.
I spent 1.5 hours adding it to keep it between 3.0 and 3.5. Thereafter, stirring was continued for 30 minutes, followed by vacuum filtration through a Nutsuie filter with a diameter of 30 cm, and the residue was washed with water 152 times (the washing liquid was used for the next slurry preparation as in Example 1). The overspeed in this case is
150/ m2 . It was very easy to over-operate with Hr. The manganese hydrochloride solution, washing solution and residue obtained above are shown in Table 4.

【表】 なお、前記残渣はフエロマンガン用原料として
充分使用できるものである。
[Table] Note that the above residue can be fully used as a raw material for ferromanganese.

Claims (1)

【特許請求の範囲】[Claims] 1 予め還元焙焼したマンガン鉱石粉末を水中に
添加してスラリーとし、該スラリーのPHを2.8〜
4.0の範囲に保持するように酸を注加した後、該
スラリーのPHが4.0〜6.0となるまで充分撹拌し、
ついで前記スラリー中の固形物を過分離してマ
ンガン塩溶液を得ると共に、前記固形物をフエロ
マンガン用原料として再利用することを特徴とす
るマンガン鉱石の処理法。
1. Add manganese ore powder that has been reduced and roasted in advance to water to make a slurry, and adjust the pH of the slurry to 2.8~2.8.
After adding acid to maintain the pH within the range of 4.0, stir thoroughly until the pH of the slurry is between 4.0 and 6.0.
A method for processing manganese ore, characterized in that the solid matter in the slurry is then over-separated to obtain a manganese salt solution, and the solid matter is reused as a raw material for ferromanganese.
JP57032643A 1982-03-02 1982-03-02 Treatment of manganese ore Granted JPS58151437A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57032643A JPS58151437A (en) 1982-03-02 1982-03-02 Treatment of manganese ore

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57032643A JPS58151437A (en) 1982-03-02 1982-03-02 Treatment of manganese ore

Publications (2)

Publication Number Publication Date
JPS58151437A JPS58151437A (en) 1983-09-08
JPS6142769B2 true JPS6142769B2 (en) 1986-09-24

Family

ID=12364526

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57032643A Granted JPS58151437A (en) 1982-03-02 1982-03-02 Treatment of manganese ore

Country Status (1)

Country Link
JP (1) JPS58151437A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
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JPH01109645A (en) * 1987-10-21 1989-04-26 Nec Corp Chip-in glass type fluorescent character display module

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20010097347A (en) * 2000-04-21 2001-11-08 우종일 Method for preparing nonferrous metal salts and nonferrous metal salts prepared using the method
CN103194768B (en) * 2013-04-16 2016-01-13 中南大学 High ferro high-phosphorus manganese is utilized to prepare the method for electrolytic metal Mn
CN105886781B (en) * 2016-06-29 2018-01-02 广西桂柳化工有限责任公司 Method for recovering manganese dioxide from electrolytic manganese anode mud
CN114984974B (en) * 2022-06-10 2024-05-14 常州大学 Method for improving low-temperature SCR denitration performance of natural ferro-manganese ore catalyst

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* Cited by examiner, † Cited by third party
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JPH01109645A (en) * 1987-10-21 1989-04-26 Nec Corp Chip-in glass type fluorescent character display module

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