JP2001226120A - Method for manufacturing ferric sulfate solution - Google Patents

Method for manufacturing ferric sulfate solution

Info

Publication number
JP2001226120A
JP2001226120A JP2000040038A JP2000040038A JP2001226120A JP 2001226120 A JP2001226120 A JP 2001226120A JP 2000040038 A JP2000040038 A JP 2000040038A JP 2000040038 A JP2000040038 A JP 2000040038A JP 2001226120 A JP2001226120 A JP 2001226120A
Authority
JP
Japan
Prior art keywords
solution
ferric sulfate
sulfate solution
manganese
permanganate
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.)
Granted
Application number
JP2000040038A
Other languages
Japanese (ja)
Other versions
JP4831589B2 (en
Inventor
Fumihiko Sato
文彦 佐藤
Tatsuhiko Miyazaki
達彦 宮崎
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.)
Taki Chemical Co Ltd
Original Assignee
Taki 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 Taki Chemical Co Ltd filed Critical Taki Chemical Co Ltd
Priority to JP2000040038A priority Critical patent/JP4831589B2/en
Publication of JP2001226120A publication Critical patent/JP2001226120A/en
Application granted granted Critical
Publication of JP4831589B2 publication Critical patent/JP4831589B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Landscapes

  • Inorganic Compounds Of Heavy Metals (AREA)

Abstract

PROBLEM TO BE SOLVED: To manufacture a ferric sulfate solution having an extremely low content of manganese by removing the manganese in the ferric sulfate solution obtained by dissolving an iron ore consisting essentially of FeOOH in sulfuric acid. SOLUTION: The iron ore consisting essentially of FeOOH is dissolved in sulfuric acid to obtain a ferric sulfate solution, a permanganate is added so as to obtain the solution in >=0.667 molar ratio of MnO4-/Mn as the permanganate to manganese in the solution, the solution is heated to insolubilize manganese, and the insolubilized component is separated from liquid to manufacture the ferric sulfate solution.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、各種廃水処理薬
剤、また近年は浄水処理用の凝集剤としても注目されて
いる硫酸第二鉄溶液の製造に際し、マンガン濃度の極め
て少ない硫酸第二鉄溶液を製造する方法に関するもので
ある。
The present invention relates to a ferric sulfate solution having an extremely low manganese concentration in the production of a ferric sulfate solution which has been attracting attention as a chemical for treating various wastewaters and also as a flocculant for water purification in recent years. And a method for producing the same.

【0002】[0002]

【従来の技術】硫酸第二鉄溶液は、従来から下水、し尿
あるいは各種産業排水処理用の凝集剤、あるいは汚泥、
スラッジの脱水助剤など広範囲にわたって使用されてい
る。同じような用途で、硫酸アルミニウム、ポリ塩化ア
ルミニウム等のアルミニウム塩も使用されているが、硫
酸第二鉄溶液はアルミニウム塩より、排水中の有機物除
去に優れている、凝集pHが広い、フロックの沈降速度が
速い、臭気特にイオウ系の臭気に対して脱臭効果がある
などの点が優れている。また同じ鉄塩溶液の塩化第二鉄
溶液と比較しても設備に対する腐食が少ないなどの利点
がある。
2. Description of the Related Art Ferric sulfate solution has conventionally been used as a flocculant for treating sewage, human waste or various industrial wastewater, or sludge.
Widely used, such as sludge dewatering aids. Aluminum salts such as aluminum sulfate and polyaluminum chloride are also used for similar applications.However, ferric sulfate solutions are superior to aluminum salts in removing organic substances in wastewater, have a wide flocculation pH, It is excellent in that it has a high sedimentation speed and has a deodorizing effect on odors, especially sulfur-based odors. In addition, there is an advantage that the corrosion to the equipment is small as compared with the ferric chloride solution of the same iron salt solution.

【0003】最近の水道水源は、環境汚染の影響から徐
々に悪化する傾向にあり、トリハロメタンや異臭味の問
題などが顕在化してきている。これらの原因の一つは水
道水源に存在する有機物に起因し、これらの除去に優れ
た硫酸第二鉄溶液などの鉄系凝集剤が近年アルミニウム
塩に代わり見直されつつある。しかし、現在市場に出回
っている硫酸第二鉄溶液などの大部分の鉄塩は、これを
浄水用として使用するに際しては種々の問題がある。そ
の一つとして、製品溶液中のマンガン濃度が高いことが
あげられる。従って、水道原水の処理過程で使用する凝
集剤にマンガンが含まれていると、後段の処理過程で注
入される塩素によってマンガンが徐々に酸化され、配水
管中での黒色沈殿物生成の問題、またそれらが剥がれる
ことにより「黒い水」の原因となる。
[0003] Recent tap water sources tend to gradually deteriorate due to the effects of environmental pollution, and problems such as trihalomethane and off-flavors have become apparent. One of these causes is due to organic substances present in a tap water source, and iron-based flocculants such as a ferric sulfate solution which is excellent in removing these substances have recently been reviewed in place of aluminum salts. However, most iron salts, such as a ferric sulfate solution currently on the market, have various problems when they are used for water purification. One of the reasons is that the manganese concentration in the product solution is high. Therefore, if manganese is contained in the coagulant used in the treatment of raw tap water, the manganese is gradually oxidized by chlorine injected in the subsequent treatment process, and the problem of black precipitate formation in the water distribution pipe, In addition, peeling off them causes "black water".

【0004】このような硫酸第二鉄溶液は、一般に鉄鋼
の酸洗い廃液を酸化する方法、屑鉄等の金属鉄を硫酸に
溶解し酸化する方法、チタン製造時に排出される副生硫
酸第一鉄を酸化する方法等により得られるが、これらの
製法は、主に第一鉄を原料としているため、硫酸第二鉄
溶液を製造するためには酸化工程が必要であった。この
ような状況の中で、本発明者らは、第二鉄として30%以
上含有するFeOOHは硫酸に溶けやすく、かつ酸化工程が
殆ど不要であることから、容易に硫酸第二鉄溶液を製造
することができることを見い出し先に出願を行った。
(特願平11-309058号) また更に、FeOOHをFe3+として30%以上含有する鉄鉱石を
硫酸で溶解した硫酸第二鉄溶液からマンガンを減少させ
たものは、濁質除去効果に優れていることを見い出し先
に出願を行った。(特開平11-309059号) しかしながら、このようにして製造した硫酸第二鉄溶液
中のマンガン濃度は、概ねFe3+濃度が11%近傍である時
には、50〜1000mg/kg程度であることが多い。硫酸第二
鉄溶液中の鉄とマンガンとは非常に性質が類似してお
り、またマンガンに対し鉄濃度が100倍程度と大過剰に
あるため、選択的にマンガンだけを除去することは非常
に困難であった。
[0004] Such ferric sulfate solution is generally used to oxidize pickling waste solution of steel, to dissolve and oxidize metallic iron such as scrap iron in sulfuric acid, and to produce by-product ferrous sulfate discharged during titanium production. However, these methods mainly use ferrous iron as a raw material, so that an oxidation step was necessary to produce a ferric sulfate solution. Under such circumstances, the present inventors have found that FeOOH containing 30% or more as ferric iron is easily soluble in sulfuric acid, and the oxidation step is almost unnecessary. I found an application that I could do.
(Japanese Patent Application No. 11-309058) In addition, those in which manganese is reduced from a ferric sulfate solution obtained by dissolving iron ore containing FeOOH as Fe 3+ by 30% or more with sulfuric acid have excellent turbidity removing effect. Filed an application where they found it. However, the manganese concentration in the ferric sulfate solution thus produced may be about 50 to 1000 mg / kg when the Fe3 + concentration is approximately 11%. Many. Since iron and manganese in the ferric sulfate solution have very similar properties, and the iron concentration is about 100 times as large as manganese, it is very difficult to selectively remove only manganese. It was difficult.

【0005】以上のことから、マンガン濃度の低い製品
を製造するためには、マンガン含有量のきわめて低い原
材料を使用しなければならないが、これら原材料が市場
で不足しているため、安価に大量にマンガン濃度の低い
硫酸第二鉄溶液を製造することは困難であった。このよ
うに、マンガン濃度の低い硫酸第二鉄溶液の需要はある
ものの、硫酸第二鉄溶液中のマンガン除去に関してはこ
れまでほとんど成果の上がる研究がなされていなかった
のが現状である。
[0005] From the above, in order to produce a product having a low manganese concentration, it is necessary to use raw materials having a very low manganese content. It was difficult to produce a ferric sulfate solution having a low manganese concentration. As described above, although there is a demand for a ferric sulfate solution having a low manganese concentration, there has been almost no research on manganese removal in the ferric sulfate solution so far, with almost no results.

【0006】マンガンの除去方法については、一般に用
水、廃水処理等に於いて多数行われている。例えば、特
開平9-29267号公報には、マンガンを含有する排水に過
マンガン酸塩を添加し、排水中のマンガンを除去する方
法が開示されている。しかし、このような廃水等は一般
には中性であり、他の夾雑物の濃度も低いことから一般
にその除去は容易であるが、硫酸第二鉄溶液のように高
濃度の鉄塩を共存し、しかも強酸性条件での溶液中のマ
ンガンの除去は甚だ困難である。従って、マンガン等の
不純物を含有する鉄塩溶液中からの不純物の除去方法と
しては、溶液を濃縮、冷却して、鉄塩を晶析・分離する
方法(特開平10-273326号公報)等によらなければなら
ないが、このような方法はマンガンを非常に低濃度にで
きる反面、その工程が非常に複雑となり経済的でない。
[0006] Many manganese removal methods are generally used in water treatment, wastewater treatment and the like. For example, Japanese Patent Application Laid-Open No. 9-29267 discloses a method in which permanganate is added to wastewater containing manganese to remove manganese in the wastewater. However, such wastewater is generally neutral and has a low concentration of other contaminants, so that it is generally easy to remove it.However, such wastewater coexists with a high-concentration iron salt such as a ferric sulfate solution. Moreover, it is extremely difficult to remove manganese from the solution under strongly acidic conditions. Therefore, as a method of removing impurities from an iron salt solution containing impurities such as manganese, a method of concentrating and cooling the solution to crystallize and separate the iron salt (Japanese Patent Application Laid-Open No. 10-273326), etc. Although it must be noted that such a method can reduce the concentration of manganese to a very low level, but the process is very complicated and not economical.

【0007】[0007]

【発明が解決しようとする課題】このような状況に鑑
み、本発明者らはFeOOHを主成分とする鉄鉱石を硫酸で
溶解して得られる硫酸第二鉄溶液からマンガンのみを選
択的に除去し、浄水処理等に於いても使用できるような
低マンガン量の硫酸第二鉄溶液を製造する方法について
鋭意検討を重ねた。その結果、このようなFeOOHを主成
分とする鉄鉱石を硫酸で溶解して得られる硫酸第二鉄溶
液に、特定量以上の過マンガン酸塩を添加し、この溶液
を加熱処理しマンガンを不溶化させ、この不溶化分を分
離、除去することにより、溶液中のマンガン濃度が変化
する原料に於いても安定して低マンガン濃度の硫酸第二
鉄溶液を製造することができることを見い出し、係る知
見に基づき本発明を完成させたものである。
In view of such a situation, the present inventors selectively remove only manganese from a ferric sulfate solution obtained by dissolving iron ore containing FeOOH as a main component with sulfuric acid. Further, the present inventors have conducted intensive studies on a method for producing a ferric sulfate solution having a low manganese content that can be used in water purification treatment and the like. As a result, a specific amount or more of permanganate is added to a ferric sulfate solution obtained by dissolving iron ore containing FeOOH as a main component with sulfuric acid, and this solution is heated to insolubilize manganese. By separating and removing the insolubilized component, it was found that a ferric sulfate solution having a low manganese concentration can be stably produced even in a raw material in which the manganese concentration in the solution changes. Based on this, the present invention has been completed.

【0008】[0008]

【課題を解決するための手段】即ち、本発明はFeOOHを
主成分とする鉄鉱石を硫酸で溶解して得られる硫酸第二
鉄溶液に対して、該溶液中のマンガン量に対する過マン
ガン酸塩量がMnO4 -/Mn(モル比)として0.667以上になる
ように過マンガン酸塩を添加し、この溶液を加熱処理す
ることによりマンガンを不溶化させた後、該不溶化分を
固液分離することからなる硫酸第二鉄溶液の製造方法に
関する。
That is, the present invention relates to a ferric sulfate solution obtained by dissolving iron ore containing FeOOH as a main component with sulfuric acid, a permanganate relative to the amount of manganese in the solution. Permanganate is added so that the amount becomes 0.667 or more as MnO 4 / Mn (molar ratio), and the solution is heated to insolubilize manganese, and then the insoluble matter is subjected to solid-liquid separation. And a method for producing a ferric sulfate solution comprising:

【0009】本発明の製造方法は、FeOOHを主成分とす
る鉄鉱石を硫酸で溶解して得られるマンガンを含む硫酸
第二鉄溶液に対して、過マンガン酸塩を理論量以上添加
し、かつ加熱することにより、硫酸第二鉄溶液中のマン
ガンと過剰分の過マンガン酸塩を不溶化させ、それを濾
別することによって効率的に低マンガン濃度の硫酸第二
鉄溶液を製造する方法である。従って、過マンガン酸塩
を理論量より多く添加しても、或いは硫酸第二鉄溶液中
の含有マンガン濃度が変化しても、安定して低マンガン
濃度の硫酸第二鉄溶液を製造することができる。また、
溶液中にFe2+などの還元性無機物質あるいは過マンガン
酸塩を消費する有機物などがあると、過マンガン酸塩添
加量の算出が困難となるが、本発明の製造方法によれば
安定して低マンガン量の硫酸第二鉄溶液を製造すること
ができる。
[0009] In the production method of the present invention, a permanganate salt is added in a theoretical amount or more to a ferric sulfate solution containing manganese obtained by dissolving iron ore containing FeOOH as a main component with sulfuric acid; By heating, it is a method of insolubilizing the manganese in the ferric sulfate solution and the excess permanganate, and efficiently producing a low manganese ferric sulfate solution by filtering it out. . Therefore, even if the permanganate is added in a larger amount than the theoretical amount or the manganese content in the ferric sulfate solution changes, it is possible to stably produce a ferric sulfate solution having a low manganese concentration. it can. Also,
When there is a reducing inorganic substance such as Fe 2+ or an organic substance that consumes permanganate in the solution, it becomes difficult to calculate the amount of permanganate to be added. To produce a ferric sulfate solution having a low manganese content.

【0010】[0010]

【発明の実施の形態】本発明で使用するFeOOHを主成分
とする鉄鉱石とは、FeOOHを主成分とする天然に産出す
る鉄鉱石であって、天然に産する鉄鉱石としては、褐鉄
鉱、針鉄鉱、鱗鉄鉱と呼ばれる鉄の水酸化鉱物が例示さ
れるが、これらに限定されるものではない。このような
鉄鉱石を硫酸で溶解して得られる硫酸第二鉄溶液を本発
明は使用するが、このような硫酸第二鉄溶液は、正塩は
もちろん、遊離の酸を含むもの或いは塩基性塩であって
もよい。
BEST MODE FOR CARRYING OUT THE INVENTION The iron ore containing FeOOH as a main component used in the present invention is a naturally occurring iron ore containing FeOOH as a main component, and the naturally occurring iron ore includes limonite, Examples include iron hydroxide minerals called goethite and lepite, but are not limited thereto. The present invention uses a ferric sulfate solution obtained by dissolving such iron ore with sulfuric acid. Such a ferric sulfate solution contains not only a normal salt but also a free acid or a basic acid. It may be a salt.

【0011】本発明の硫酸第二鉄溶液の製造方法は、先
ず上記のFeOOHを主成分とする鉄鉱石を硫酸で溶解して
得られる硫酸第二鉄溶液に、過マンガン酸塩を加え、こ
の溶液を加熱処理することによりマンガンを不溶化させ
る。使用する過マンガン酸塩の種類としては、過マンガ
ン酸カリウム、過マンガン酸ナトリウム、過マンガン酸
アンモニウム等を例示できる。過マンガン酸塩の添加量
は、溶液中に存在するFe2+などの還元性無機物質、ある
いは過マンガン酸塩を消費する有機物質などの存在量に
より一概には云えないが、硫酸第二鉄溶液中に含まれる
マンガン量に対する過マンガン酸塩添加量がMnO4 -/Mn
(モル比)として0.667以上、より好ましくは0.667〜6.00
の範囲になるように過マンガン酸塩を添加する。
[0011] The method for producing a ferric sulfate solution of the present invention comprises:
Dissolve iron ore containing FeOOH as a main component with sulfuric acid
To the resulting ferric sulfate solution, add permanganate and add
Manganese is insolubilized by heating the solution
You. The type of permanganate used is
Potassium phosphate, sodium permanganate, permanganate
Ammonium and the like can be exemplified. Addition amount of permanganate
Is the Fe present in the solution2+There are reducing inorganic substances, such as
Or the amount of organic substances that consume permanganate
More specifically, it is contained in ferric sulfate solution
The amount of permanganate added to the amount of manganese is MnOFour -/ Mn
(Molar ratio) as 0.667 or more, more preferably 0.667 to 6.00
The permanganate is added so as to be within the range.

【0012】次に、加熱温度に関しては、70℃以上であ
ればマンガンを除去でき、高温となるほどマンガンの不
溶化効率は向上するが、この温度が低ければ加熱時間が
長く必要となることから、好ましくは80℃以上である。
加熱時間は加熱温度、マンガンの目標除去率等によって
異なるが、概ね30分〜6時間程度である。また、過マン
ガン酸塩の添加方法は、これを溶液として添加しても、
或いは粉体のまま添加してもよい。また添加必要量を一
度に全量添加しても、或いは分割して添加してもよい。
また、添加時期は、加熱開始前、溶液が目標加熱温度と
なった後、或いは昇温段階の何れであってもよい。ま
た、過マンガン酸塩の添加方法として、前述のFeOOHを
主成分とする鉄鉱石を硫酸で溶解して硫酸第二鉄溶液を
製造する際に、過マンガン酸塩を予め添加して硫酸第二
鉄溶液を製造する添加方法も採用できる。
Regarding the heating temperature, if the temperature is 70 ° C. or higher, manganese can be removed, and the higher the temperature, the higher the manganese insolubilization efficiency. However, if the temperature is lower, the heating time is longer, so it is preferable. Is 80 ° C. or higher.
The heating time varies depending on the heating temperature, the target removal rate of manganese, and the like, but is generally about 30 minutes to 6 hours. Also, the method of adding permanganate, even if it is added as a solution,
Alternatively, it may be added as a powder. Further, the necessary amount of addition may be added all at once, or may be added in portions.
In addition, the timing of addition may be before the start of heating, after the solution has reached the target heating temperature, or at the temperature raising stage. Further, as a method of adding a permanganate, when the iron ore containing FeOOH as a main component is dissolved in sulfuric acid to produce a ferric sulfate solution, the permanganate is added in advance to form a sulfated iron ore. An addition method for producing an iron solution can also be adopted.

【0013】以上のような処理を行うことにより、硫酸
第二鉄溶液中に含まれるマンガンは不溶性のMnO2あるい
はその水和物になり、また過剰量の過マンガン酸塩も自
己分解によって同様に不溶性のMnO2あるいはその水和物
となる。
By performing the above treatment, manganese contained in the ferric sulfate solution becomes insoluble MnO 2 or a hydrate thereof, and an excess amount of permanganate is similarly decomposed by autolysis. It becomes insoluble MnO 2 or its hydrate.

【0014】次に、不溶化したマンガンは、これを溶液
から分離することにより、本発明の目的とするマンガン
濃度の低い硫酸第二鉄溶液を得ることができる。分離手
段については、沈降分離後濾過する方法、遠心分離等何
れの手段を用いてもよい。
Next, by separating the insolubilized manganese from the solution, the ferric sulfate solution having a low manganese concentration, which is the object of the present invention, can be obtained. As the separation means, any method such as a method of filtering after sedimentation and separation, and a method of centrifugation may be used.

【0015】[0015]

【実施例】以下に、本発明の実施例を挙げ更に説明を行
う。尚、実施例に於いて%は特に断らない限り全て重量
%を示す。
The present invention will be further described below with reference to examples of the present invention. In the examples, all percentages are by weight unless otherwise specified.

【0016】[実施例1、比較例1]環流冷却器付きの
3Lの四つ口フラスコに70%硫酸を267.2g、水を148.4g添
加し、300rpmで攪拌しながら、鉄鉱石(FeOOHを主成分と
し、全Fe濃度63.9%)の120gを徐々に加えた。攪拌を続け
ながら溶液を105℃に加熱し、この温度で3時間加熱を続
けた。加熱後溶液を冷却し、これに水90g、珪藻土(昭和
化学工業(株)製,商品名:ラシ゛オライト#2000)を5g加え、攪拌
後No.5C濾紙で濾過し硫酸第二鉄溶液を得た。この硫酸
第二鉄溶液の組成は、Fe3+11.62%、Fe2+0.01%以下、SO4
30.0%、Mn56mg/kgであった。
Example 1, Comparative Example 1
267.2 g of 70% sulfuric acid and 148.4 g of water were added to a 3 L four-necked flask, and 120 g of iron ore (mainly FeOOH, total Fe concentration of 63.9%) was gradually added while stirring at 300 rpm. The solution was heated to 105 ° C. with continued stirring, and heating was continued at this temperature for 3 hours. After heating, the solution was cooled, and thereto was added 90 g of water and 5 g of diatomaceous earth (trade name: Rashiolite # 2000, manufactured by Showa Chemical Industry Co., Ltd.), and the mixture was stirred and filtered with No. 5C filter paper to obtain a ferric sulfate solution. Was. The composition of the ferric sulfate solution, Fe 3+ 11.62%, Fe 2+ 0.01% or less, SO 4
30.0% and Mn was 56 mg / kg.

【0017】この硫酸第二鉄溶液の200gを環流冷却器の
ついた500mlの四つ口フラスコにとり、過マンガン酸カ
リウム(関東化学(株)製,試薬特級)をイオン交換水で5%
に溶解した溶液の1.94g(MnO4 -/Mnモル比=3.01)を加え、20
0rpmで攪拌しながら溶液を加熱し、沸騰状態(103℃)を
維持しながら3時間加熱を続けた。加熱終了後冷却し、
この溶液に濾過助剤として珪藻土(昭和化学工業(株)製,
商品名:ラシ゛オライト スヘ゜シャルフロー)を1g加え、攪拌後No.5C濾紙
で濾過し、マンガンを除去した硫酸第二鉄溶液を得た。
[実施例1] また別に、前記鉄鉱石より得たMn56mg/kgを含有する硫
酸第二鉄溶液を使用し、この硫酸第二鉄溶液の200gを50
0mlの四つ口フラスコにとり、前記5%過マンガン酸カリ
ウム溶液の1.94gとマンガン砂(トーケム社製,商品名:MC-2)
を100g加え、溶液を加熱せずに3時間放置した。3時間
経過後、珪藻土(昭和化学工業(株)製,商品名:ラシ゛オライト#2
000)を1g加え、攪拌後No.5C濾紙で濾過した。[比較例
1] 実施例1及び比較例1で得られた硫酸第二鉄溶液の鉄濃
度とマンガン濃度を測定した。結果を表1に示した。
200 g of the ferric sulfate solution was placed in a 500 ml four-necked flask equipped with a reflux condenser, and potassium permanganate (Kanto Chemical Co., Ltd., special grade reagent) was added with 5% ion-exchanged water.
1.94 g of a solution dissolved in (MnO 4 / Mn molar ratio = 3.01) was added, and 20
The solution was heated while stirring at 0 rpm, and heating was continued for 3 hours while maintaining the boiling state (103 ° C.). After heating, cool
Diatomaceous earth (manufactured by Showa Chemical Industry Co., Ltd.)
1 g of trade name (Rashiolite Special Flow) was added, and the mixture was stirred and filtered with No. 5C filter paper to obtain a ferric sulfate solution from which manganese had been removed.
[Example 1] Separately, a ferric sulfate solution containing 56 mg / kg of Mn obtained from the iron ore was used.
In a 0 ml four-necked flask, 1.94 g of the 5% potassium permanganate solution and manganese sand (manufactured by Tochem Co., Ltd., trade name: MC-2)
Was added and the solution was left for 3 hours without heating. After 3 hours, diatomaceous earth (manufactured by Showa Chemical Co., Ltd., trade name: Rashiolite # 2
000), and the mixture was stirred and filtered with No. 5C filter paper. Comparative Example 1 The iron and manganese concentrations of the ferric sulfate solutions obtained in Example 1 and Comparative Example 1 were measured. The results are shown in Table 1.

【0018】[0018]

【表1】 [Table 1]

【0019】[実施例2、比較例2]環流冷却器付きの
5Lの三つ口フラスコに70%硫酸を519.6g、水を288.8g添
加し、300rpmで攪拌しながら、鉄鉱石(FeOOHを主成分と
し、全Fe濃度63.9%)の240gを徐々に加えた。攪拌を続け
ながら溶液を105℃に加熱し、この温度で3時間加熱を続
けた。加熱後溶液を冷却し、これに水180g、珪藻土(昭
和化学工業(株)製,商品名:ラシ゛オライト#2000)を8g加え、攪
拌後No.5C濾紙で濾過し塩基性硫酸第二鉄溶液を得た。
この塩基性硫酸第二鉄溶液の組成は、Fe3+11.57%、Fe2+
0.01%、SO429.0%、Mn63mg/kgであった。
Example 2 and Comparative Example 2 With a reflux cooler
To a 5 L three-necked flask, 519.6 g of 70% sulfuric acid and 288.8 g of water were added, and while stirring at 300 rpm, 240 g of iron ore (having FeOOH as a main component and a total Fe concentration of 63.9%) was gradually added. The solution was heated to 105 ° C. with continued stirring, and heating was continued at this temperature for 3 hours. After heating, the solution was cooled, and 180 g of water and 8 g of diatomaceous earth (manufactured by Showa Chemical Industry Co., Ltd., trade name: Rashiolite # 2000) were added.After stirring, the solution was filtered through a No. 5C filter paper, and the basic ferric sulfate solution was added. I got
The composition of this basic ferric sulfate solution is Fe 3+ 11.57%, Fe 2+
The results were 0.01%, SO 4 29.0%, and Mn 63 mg / kg.

【0020】この塩基性硫酸第二鉄溶液の400gを環流冷
却器付きの1Lの四つ口フラスコにとり、過マンガン酸
カリウム(関東化学(株)製,試薬特級)を193.5mg添加し、
攪拌しながら温度90℃で5時間溶液を加熱した。加熱終
了後冷却し、この溶液に濾過助剤として珪藻土(昭和化
学工業(株)製,商品名:ラシ゛オライト スヘ゜シャルフロー)を1g加え、攪
拌後No.5C濾紙で濾過し、マンガンを除去した塩基性硫
酸第二鉄溶液を得た。[実施例2] また別に、前記鉄鉱石より得たMn63mg/kgを含有する塩
基性硫酸第二鉄溶液を使用し、この塩基性硫酸第二鉄溶
液の400gを環流冷却器付きの四つ口フラスコにとり、こ
れに過マンガン酸カリウム(関東化学(株)製,試薬特級)4
3.6mgを加え、攪拌しながら温度90℃で5時間溶液を加熱
した。加熱後冷却し、珪藻土(昭和化学工業(株)製,商品
名:ラシ゛オライト スヘ゜シャルフロー)を1g加え、攪拌後No.5C濾紙で濾
過した。[比較例2] 実施例2及び比較例2で得られた塩基性硫酸第二鉄溶液
の鉄濃度とマンガン濃度を測定した。結果を表2に示し
た。
400 g of this basic ferric sulfate solution was placed in a 1 L four-necked flask equipped with a reflux condenser, and 193.5 mg of potassium permanganate (Kanto Chemical Co., Ltd., reagent grade) was added.
The solution was heated at 90 ° C. for 5 hours with stirring. After completion of heating, the solution was cooled, 1 g of diatomaceous earth (manufactured by Showa Chemical Industry Co., Ltd., trade name: Rashiolite Special Flow) was added to this solution as a filter aid, and the mixture was stirred and filtered with No. 5C filter paper to remove manganese. A ferric sulfate solution was obtained. [Example 2] Separately, a basic ferric sulfate solution containing 63 mg / kg of Mn obtained from the iron ore was used, and 400 g of the basic ferric sulfate solution was supplied to a four-hole with a reflux condenser. Take the flask and add potassium permanganate (Kanto Chemical Co., Ltd., reagent grade) 4
3.6 mg was added and the solution was heated at 90 ° C. for 5 hours with stirring. After heating, the mixture was cooled, 1 g of diatomaceous earth (trade name: Rashiolite Special Flow, manufactured by Showa Chemical Industry Co., Ltd.) was added, and the mixture was stirred and filtered with No. 5C filter paper. Comparative Example 2 The iron concentration and the manganese concentration of the basic ferric sulfate solutions obtained in Example 2 and Comparative Example 2 were measured. The results are shown in Table 2.

【0021】[0021]

【表2】 [Table 2]

【0022】[実施例3、比較例3]環流冷却器付きの
5Lの三つ口フラスコに70%硫酸を519.6g、水を288.8g添
加し、300rpmで攪拌しながら、鉄鉱石(FeOOHを主成分と
し、全Fe濃度63.9%)の240gを徐々に加えた。攪拌を続け
ながら溶液を105℃に加熱し、この温度で3時間加熱を続
けた。加熱後溶液を冷却し、これに水180g、珪藻土(昭
和化学工業(株)製,商品名:ラシ゛オライト#2000)を8g加え、攪
拌後No.5C濾紙で濾過し塩基性硫酸第二鉄溶液を得た。
この塩基性硫酸第二鉄溶液の組成は、Fe3+11.20%、Fe2+
0.01%、SO428.2%、Mn55mg/kgであった。
Example 3 and Comparative Example 3 With a reflux condenser
To a 5 L three-necked flask, 519.6 g of 70% sulfuric acid and 288.8 g of water were added, and while stirring at 300 rpm, 240 g of iron ore (having FeOOH as a main component and a total Fe concentration of 63.9%) was gradually added. The solution was heated to 105 ° C. with continued stirring, and heating was continued at this temperature for 3 hours. After heating, the solution was cooled, and 180 g of water and 8 g of diatomaceous earth (manufactured by Showa Chemical Industry Co., Ltd., trade name: Rashiolite # 2000) were added.After stirring, the solution was filtered through a No. 5C filter paper, and the basic ferric sulfate solution was added. I got
The composition of this basic ferric sulfate solution is Fe3 + 11.20%, Fe2 +
It was 0.01%, SO 4 28.2%, and Mn 55 mg / kg.

【0023】この塩基性硫酸第二鉄溶液の300gを環流冷
却器の付いた1Lの四つ口フラスコにとり、40%過マン
ガン酸ナトリウム水溶液(日本化学工業(株)製,SPM-40)
の0.34gを添加し、95℃で4時間溶液の加熱を続けた。加
熱終了後冷却し、この溶液に濾過助剤として珪藻土(昭
和化学工業(株)製,商品名:ラシ゛オライト スヘ゜シャルフロー)を1.5g加
え、攪拌後No.5C濾紙で濾過し、マンガンを除去した塩
基性硫酸第二鉄溶液を得た。[実施例3] また別に、前記鉄鉱石より得たMn55mg/kgを含有する塩
基性硫酸第二鉄溶液を使用し、この塩基性硫酸第二鉄溶
液の300gを環流冷却器付きの四つ口フラスコにとり、40
%過マンガン酸ナトリウム水溶液(日本化学工業(株)製,S
PM-40)の0.34gを加え、50℃で4時間溶液の加熱を続け
た。加熱終了後冷却し、この溶液に珪藻土(昭和化学工
業(株)製,商品名:ラシ゛オライト スヘ゜シャルフロー)を1.5g加え、攪拌
後No.5C濾紙で濾過した。[比較例3] 実施例3及び比較例3で得られた塩基性硫酸第二鉄溶液
の鉄濃度とマンガン濃度を測定した。結果を表3に示し
た。
300 g of the basic ferric sulfate solution is placed in a 1 L four-necked flask equipped with a reflux condenser, and a 40% aqueous solution of sodium permanganate (Nippon Chemical Industry Co., Ltd., SPM-40) is used.
Was added and heating of the solution was continued at 95 ° C. for 4 hours. After the heating was completed, the solution was cooled, 1.5 g of diatomaceous earth (trade name: Rashiolite Special Flow, manufactured by Showa Chemical Industry Co., Ltd.) was added to the solution, and the mixture was stirred and filtered with No. 5C filter paper to remove manganese. A basic ferric sulfate solution was obtained. [Example 3] Separately, a basic ferric sulfate solution containing 55 mg / kg of Mn obtained from the iron ore was used, and 300 g of the basic ferric sulfate solution was supplied to a four-hole with a reflux condenser. 40 in a flask
% Sodium permanganate aqueous solution (Nippon Chemical Industry Co., Ltd., S
0.34 g of PM-40) was added, and heating of the solution was continued at 50 ° C. for 4 hours. After completion of the heating, the mixture was cooled, 1.5 g of diatomaceous earth (trade name: Radiolite Special Flow, manufactured by Showa Chemical Industry Co., Ltd.) was added to the solution, and the mixture was stirred and filtered with No. 5C filter paper. Comparative Example 3 The iron concentration and the manganese concentration of the basic ferric sulfate solutions obtained in Example 3 and Comparative Example 3 were measured. The results are shown in Table 3.

【0024】[0024]

【表3】 [Table 3]

【0025】[0025]

【発明の効果】本発明の硫酸第二鉄溶液の製造方法は、
FeOOHを主成分とする鉄鉱石を硫酸で溶解して得られる
硫酸第二鉄溶液からマンガンのみを選択的に除去し、浄
水処理等に於いても使用できるような低マンガン量の硫
酸第二鉄溶液を製造する方法である。また、本発明の方
法は、硫酸第二鉄溶液中のマンガン濃度が変化しても安
定して低マンガン濃度の硫酸第二鉄溶液を得ることがで
きる。更には、溶液中にFe2+などの還元性無機物質ある
いは過マンガン酸塩を消費する有機物などがあっても、
過マンガン酸塩添加量の算出が容易であるだけでなく、
硫酸第二鉄溶液中のこれら不純物の除去にも効果的であ
る。従って、本発明の方法によって得られる硫酸第二鉄
溶液は、アルミニウム塩に代わる浄水用の凝集剤として
特に有用である。
The method for producing a ferric sulfate solution of the present invention comprises:
A ferric sulfate solution obtained by dissolving iron ore containing FeOOH as the main component with sulfuric acid selectively removes only manganese from the ferric sulfate solution, and has a low manganese content of ferric sulfate that can be used in water purification treatment etc. This is a method for producing a solution. Further, the method of the present invention can stably obtain a ferric sulfate solution having a low manganese concentration even when the manganese concentration in the ferric sulfate solution changes. Furthermore, even if there are reducing inorganic substances such as Fe 2+ or organic substances consuming permanganate in the solution,
Not only is it easy to calculate the amount of permanganate added,
It is also effective in removing these impurities from the ferric sulfate solution. Therefore, the ferric sulfate solution obtained by the method of the present invention is particularly useful as a flocculant for water purification instead of an aluminum salt.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 FeOOHを主成分とする鉄鉱石を硫酸で溶
解して得られる硫酸第二鉄溶液に対して、該溶液中のマ
ンガン量に対する過マンガン酸塩量がMnO4 -/Mn(モル
比)として0.667以上になるように過マンガン酸塩を添加
し、この溶液を加熱処理することによりマンガンを不溶
化させた後、該不溶化分を固液分離することからなる硫
酸第二鉄溶液の製造方法。
1. A ferric sulfate solution obtained by dissolving iron ore containing FeOOH as a main component with sulfuric acid, the amount of permanganate relative to the amount of manganese in the solution is MnO 4 / Mn (mol Ratio) is 0.667 or more as permanganate is added, and the solution is heated to insolubilize the manganese, and then the ferrous sulfate solution is produced by solid-liquid separation of the insoluble matter. Method.
【請求項2】 溶液の加熱処理が70℃以上の温度で30分
以上行うことである請求項1記載の硫酸第二鉄溶液の製
造方法。
2. The method for producing a ferric sulfate solution according to claim 1, wherein the heat treatment of the solution is performed at a temperature of 70 ° C. or more for 30 minutes or more.
JP2000040038A 2000-02-17 2000-02-17 Method for producing ferric sulfate solution Expired - Fee Related JP4831589B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000040038A JP4831589B2 (en) 2000-02-17 2000-02-17 Method for producing ferric sulfate solution

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000040038A JP4831589B2 (en) 2000-02-17 2000-02-17 Method for producing ferric sulfate solution

Publications (2)

Publication Number Publication Date
JP2001226120A true JP2001226120A (en) 2001-08-21
JP4831589B2 JP4831589B2 (en) 2011-12-07

Family

ID=18563500

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000040038A Expired - Fee Related JP4831589B2 (en) 2000-02-17 2000-02-17 Method for producing ferric sulfate solution

Country Status (1)

Country Link
JP (1) JP4831589B2 (en)

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61286228A (en) * 1985-06-13 1986-12-16 Nittetsu Mining Co Ltd Production of iron-system flocculant
JPH04104912A (en) * 1990-08-24 1992-04-07 Daido Chem Eng Kk Method for treating and recovering etching waste liquor
JPH0647205A (en) * 1992-07-29 1994-02-22 Tsurumi Soda Co Ltd Production of iron base coagulant
JPH07241404A (en) * 1994-03-07 1995-09-19 Honshu Paper Co Ltd Iron based inorganic flocculant and its production
JPH0929267A (en) * 1995-07-24 1997-02-04 Tohoku Electric Power Co Inc Treatment method for manganese-containing wastewater
JPH09241664A (en) * 1996-03-11 1997-09-16 Toa Netsuken Kk Additive for preventing corrosion and its usage
WO1998037022A1 (en) * 1997-02-21 1998-08-27 Tioxide Group Services Limited Treatment of a solution containing iron salts
JPH10330850A (en) * 1997-06-03 1998-12-15 Nkk Corp Production of sintered ore
JP2001187391A (en) * 1999-12-28 2001-07-10 Ebara Corp Method for removing manganese ion in iron(iii) salt aqueous solution

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61286228A (en) * 1985-06-13 1986-12-16 Nittetsu Mining Co Ltd Production of iron-system flocculant
JPH04104912A (en) * 1990-08-24 1992-04-07 Daido Chem Eng Kk Method for treating and recovering etching waste liquor
JPH0647205A (en) * 1992-07-29 1994-02-22 Tsurumi Soda Co Ltd Production of iron base coagulant
JPH07241404A (en) * 1994-03-07 1995-09-19 Honshu Paper Co Ltd Iron based inorganic flocculant and its production
JPH0929267A (en) * 1995-07-24 1997-02-04 Tohoku Electric Power Co Inc Treatment method for manganese-containing wastewater
JPH09241664A (en) * 1996-03-11 1997-09-16 Toa Netsuken Kk Additive for preventing corrosion and its usage
WO1998037022A1 (en) * 1997-02-21 1998-08-27 Tioxide Group Services Limited Treatment of a solution containing iron salts
JPH10330850A (en) * 1997-06-03 1998-12-15 Nkk Corp Production of sintered ore
JP2001187391A (en) * 1999-12-28 2001-07-10 Ebara Corp Method for removing manganese ion in iron(iii) salt aqueous solution

Also Published As

Publication number Publication date
JP4831589B2 (en) 2011-12-07

Similar Documents

Publication Publication Date Title
JP4839653B2 (en) Method for treating waste containing chlorine and heavy metals
JP4662059B2 (en) Purification process for steel manufacturing wastewater
JP5128735B2 (en) Recovery and reuse of phosphorus and flocculant in wastewater
JP2004008860A (en) Treatment method for harmful anion-containing wastewater and agent used therein
CN101049978A (en) Method for preparing polymerized iron chloride by using cinder of sulfur iron ore
JP2008126168A (en) Coagulating sedimentation method of waste water
RU2013124426A (en) METHOD FOR WASTE WATER CLEANING FROM STAINLESS STEEL SLAG TREATMENT PROCESS
JP2004290777A (en) Method for treating arsenic-containing water
JPH08206410A (en) Coagulant for water treatment
JP3642516B2 (en) Method and apparatus for removing COD components in water
JP4831589B2 (en) Method for producing ferric sulfate solution
JP5218082B2 (en) Method and apparatus for coagulating sedimentation of low organic matter concentration wastewater
JP5693992B2 (en) Method for recovering dissolved iron from wastewater containing various metal ions
JP4630776B2 (en) Water purification agent and water purification method
JP2002079003A (en) Inorganic flocculant using highly purified ferric salt and manufacturing method thereof and processing apparatus in water-purification processing
JP4408167B2 (en) Method for removing manganese from ferric sulfate solution
JP2010279877A (en) Method for treating emulsion type wastewater
JP2017136539A (en) Method for treating blast furnace drain water
JP2001226121A (en) Method for removing manganese in ferric sulfate solution
JPH10156391A (en) Treatment of phosphorus recovered from treated water of sewerage
JPS591118B2 (en) How to treat organic wastewater
JP2001187391A (en) Method for removing manganese ion in iron(iii) salt aqueous solution
JPH09314182A (en) Treatment process for selenium containing drain
JP3341835B2 (en) Treatment method for selenium-containing water
JPH0647114B2 (en) Wastewater purification method

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20061016

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20081209

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20091106

A521 Written amendment

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20091209

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20101018

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20110914

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20110914

R150 Certificate of patent or registration of utility model

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20140930

Year of fee payment: 3

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

LAPS Cancellation because of no payment of annual fees