JPS5818335B2 - Processing method for blast furnace slag - Google Patents
Processing method for blast furnace slagInfo
- Publication number
- JPS5818335B2 JPS5818335B2 JP51021864A JP2186476A JPS5818335B2 JP S5818335 B2 JPS5818335 B2 JP S5818335B2 JP 51021864 A JP51021864 A JP 51021864A JP 2186476 A JP2186476 A JP 2186476A JP S5818335 B2 JPS5818335 B2 JP S5818335B2
- Authority
- JP
- Japan
- Prior art keywords
- blast furnace
- furnace slag
- sulfur content
- sulfur
- aqueous medium
- 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
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
Landscapes
- Processing Of Solid Wastes (AREA)
- Curing Cements, Concrete, And Artificial Stone (AREA)
- Fertilizers (AREA)
- Manufacture Of Iron (AREA)
Description
【発明の詳細な説明】
本発明は高炉滓(製銑滓)の処理法に関し、より詳細に
は高炉滓中に含有される硫黄分を分離し、高炉滓を有効
に利用し得る形態の資源とするための新規処理法に関す
る。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating blast furnace slag (pigment slag), and more specifically, to separate the sulfur content contained in blast furnace slag, and to create a form of resource that can effectively utilize blast furnace slag. Regarding new processing methods for
銑鉄の製造に際しては、鉄鉱石、コークス、石灰石又は
生石灰、及びマンガン鉱或いはスラグを高炉内に投入し
、鉄鉱石中に含まれる鉄分以外の不純物を高炉滓の形で
除去している。When producing pig iron, iron ore, coke, limestone or quicklime, and manganese ore or slag are charged into a blast furnace, and impurities other than iron contained in the iron ore are removed in the form of blast furnace slag.
この高炉滓の生成量は年間約2500万トンにも達する
と言オっれ、更に貯蔵乃至埋積中のものをも含めると、
厖大な量に達するものと思われる。It is said that the amount of blast furnace slag produced reaches approximately 25 million tons per year, and if we include that in storage or burial,
It is expected that the amount will reach a huge amount.
この高炉滓を、古くθ)ら高炉セメント、スラグウール
、肥料、セメントコンクリート用骨材等として利用する
ことが行われているが、これらの用途に供されている高
炉滓の量は、全体の10%にも満たない量であり、大部
分の高炉滓は工業用地や海岸の埋立用として処理され、
或いは港湾に廃棄処理されているのが現状である。This blast furnace slag has been used for blast furnace cement, slag wool, fertilizer, aggregate for cement concrete, etc. since ancient times, but the amount of blast furnace slag used for these purposes is The amount is less than 10%, and most of the blast furnace slag is disposed of for industrial use or as landfill on the coast.
Alternatively, the current situation is that they are disposed of at ports.
しかしながら、高炉滓中には硫黄分等の有害成分が含有
されており、環境汚染の点で埋立や廃棄処理等が非常に
困難な状態に至っている。However, blast furnace slag contains harmful components such as sulfur, making it extremely difficult to landfill or dispose of it due to environmental pollution.
しかして、高炉滓はシリカ、カルシア及びアルミナを主
成分としており、高炉滓中の硫黄分等の有害成分を有効
に除去すれば、環境汚染等のトラブルを生じることなし
に、前述した種々の分野に高度に利用し得ることが期待
される。Blast furnace slag is mainly composed of silica, calcia, and alumina, and if harmful components such as sulfur in blast furnace slag are effectively removed, it can be used in the various fields mentioned above without causing problems such as environmental pollution. It is expected that it will be highly applicable to
しかしながら、高炉滓は、その副生量が厖大なものであ
ることから、複雑な処理操作や高価な薬品を必要とする
処理操作には到底適さず、硫黄分等の除去操作は、簡単
で且つ低コストのものであることが要求される。However, since blast furnace slag produces a huge amount of by-products, it is completely unsuitable for complex processing operations or processing operations that require expensive chemicals, and removal of sulfur content, etc. is simple and easy. It is required to be low cost.
一方、高炉滓中に含有される硫黄分の量は高々1%のオ
ーダーであり、簡単な処理で含有硫黄分を実質的に除去
することは至って困難である。On the other hand, the amount of sulfur contained in blast furnace slag is on the order of 1% at most, and it is extremely difficult to substantially remove the sulfur content by simple treatment.
従って、本発明の目的は、高炉滓中に含有される硫黄分
を簡単な操作で除去し得る高炉滓の処理法を提供するに
ある。Therefore, an object of the present invention is to provide a method for treating blast furnace slag that can remove the sulfur content contained in the blast furnace slag with a simple operation.
本発明の他の目的は、高炉滓中に含有される硫黄分を除
去して、環境汚染の問題を生じることなしに、高炉滓を
種々の用途に提供し得るような高炉滓の処理法を提供す
るにある。Another object of the present invention is to provide a method for treating blast furnace slag that can remove the sulfur content contained in the blast furnace slag and provide the blast furnace slag for various uses without causing environmental pollution problems. It is on offer.
本発明の更に他の目的は、複雑な工程を必要とせずに且
つ高価な薬品類を必要とせずに、また、大量の熱エネル
ギーを使用、消費することなしに、高炉滓中に含有され
る硫黄分を有効に除去し得る高炉滓の処理法を提供する
にある。Still another object of the present invention is to contain blast furnace slag without requiring complicated processes, without requiring expensive chemicals, and without using or consuming large amounts of thermal energy. An object of the present invention is to provide a method for treating blast furnace slag that can effectively remove sulfur content.
本発明によれば、高炉滓を最大粒径が50μ以下となる
ように湿式粉砕し、生成する高炉滓微粒子スラリーをp
H10乃至13のアルカリ性水性媒質中で60乃至95
℃の温度で且つ90分を越えない時間接触させて、高炉
滓中に含有される硫黄分を前記水性媒質中に沈澱させる
ことなく溶出させ、硫黄分の抽出液と硫黄分が実質的に
除去された高炉滓とを分離し、次いで硫黄分の抽出液か
ら硫黄分をそれ自体公知の手段で分離することを特徴と
する高炉滓の処理法が提供される。According to the present invention, blast furnace slag is wet-pulverized so that the maximum particle size is 50μ or less, and the resulting blast furnace slag fine particle slurry is
H10-13 in alkaline aqueous medium 60-95
℃ and for a period not exceeding 90 minutes, the sulfur content contained in the blast furnace slag is eluted without precipitation into the aqueous medium, and the sulfur content is substantially removed from the sulfur extract. There is provided a method for treating blast furnace slag, which is characterized in that the blast furnace slag is separated from the blast furnace slag, and then the sulfur content is separated from the sulfur content extract by means known per se.
本発明を以下に詳細に説明する。The invention will be explained in detail below.
本発明は、高炉から排出される任意の鉱滓に広く適用で
きる。The present invention is widely applicable to any slag discharged from a blast furnace.
高炉滓には、その処理方式によって所謂水滓と空冷滓と
に大別されるが、本発明の処理法は、これら何れの高炉
滓、特に高炉滓の大部分を占める窒冷滓に好適に適用で
きる。Blast furnace slag is broadly classified into so-called water slag and air-cooled slag depending on its treatment method, and the treatment method of the present invention is suitable for both of these types of blast furnace slag, especially nitrogen-cooled slag, which accounts for the majority of blast furnace slag. Applicable.
これらの高炉滓は、各製鉄所によっても相違するが、カ
ルシア(CaO)、シリカ及びアルミナを主成分とし、
他に少量のマンガン、マグネシウム、チタン、鉄等の金
属成分及び硫黄分を含有している。These blast furnace slags mainly contain calcia (CaO), silica, and alumina, although they differ depending on the steelworks.
It also contains small amounts of metal components such as manganese, magnesium, titanium, and iron, as well as sulfur.
高炉滓の代表的なものについてその組成の例を示すと、
下記の通りである。An example of the composition of typical blast furnace slag is as follows:
It is as follows.
成 分 重量%
Ca0 38−43Si
n229−38
A120313−19.5
g03−8
Mn0 0.3−3T10
2 0 3Fe203
o、 5−1SO15−1,5
灼熱減量 0−3
本発明によれば先ず、高炉滓を微細粒子に粉砕するこ吉
が、高炉滓中の少量の硫黄分を有効に除去するために重
要である。Component Weight% Ca0 38-43Si
n229-38 A120313-19.5 g03-8 Mn0 0.3-3T10
2 0 3Fe203
o, 5-1SO15-1,5 Loss on ignition 0-3 According to the present invention, first, the grinding of blast furnace slag into fine particles is important for effectively removing a small amount of sulfur content in blast furnace slag. be.
高炉滓の粉砕の程度は、一般的に言って、最高粒径が5
0μ以下、最も好適には20μ以下であることが、硫黄
分を有効に除去するために重要である。Generally speaking, the degree of pulverization of blast furnace slag has a maximum particle size of 5.
It is important that the sulfur content be 0μ or less, most preferably 20μ or less, in order to effectively remove the sulfur content.
後述する比較例2に示す通り、粒径が100〜80μ程
度の粗い粉末の高炉滓では、含有硫黄分の高々05%程
度が除去されるにすぎない。As shown in Comparative Example 2, which will be described later, in the case of coarse powder blast furnace slag with a particle size of about 100 to 80 microns, only about 05% of the sulfur content is removed at most.
これに対して、本発明によれは、以下の各実施例に示す
通り、高炉滓を微細粉砕し、次いでこれを、アルカリ性
の水性媒質と接触させるという簡単な操作で高炉滓中の
含有硫黄分の実質的な量、即ち、例えば60重量%以上
を容易に除去することが可能となるのである。On the other hand, according to the present invention, as shown in the following examples, the sulfur content in the blast furnace slag can be reduced by a simple operation of finely pulverizing the blast furnace slag and then contacting it with an alkaline aqueous medium. This makes it possible to easily remove a substantial amount of, for example, 60% by weight or more.
粉砕は、ボールミル、リングロールミル、ロッドミル、
衝撃粉砕機、円板粉砕機、ジェット粉砕機、ピキウス、
コロイドミル、略式摩砕機等のそれ自体公知の微粉砕機
を用いて、湿式或いは乾式で行うことができる。Grinding can be done using ball mills, ring roll mills, rod mills,
Impact crusher, disc crusher, jet crusher, Pichius,
The pulverization can be carried out wet or dry using a known pulverizer such as a colloid mill or an informal pulverizer.
勿論、用いる高炉滓の径が大きい場合には、微粉砕する
に先立って、ショークラッシャー、ジャイレートリクラ
ッシャー等の粗砕機や、ハンマーミル、ロールクラッシ
ャー等の中間破砕機を用いて、微粉砕機に供するに適し
た粒径の砕料とすることができる。Of course, if the diameter of the blast furnace slag to be used is large, before pulverizing it, use a coarse crusher such as a show crusher or gyrate recrusher, or an intermediate crusher such as a hammer mill or roll crusher. The powder can be made into a powder with a particle size suitable for use.
高炉滓C空冷滓)は、内部に多数の気孔を有する脆い塊
であり、例えば0.5乃至6時間の比較的短時間のボー
ルミル処理で本発明の目的に適した高炉滓の微粉末が得
られる。Blast furnace slag (air-cooled slag) is a brittle lump with many pores inside, and a fine powder of blast furnace slag suitable for the purpose of the present invention can be obtained by ball milling for a relatively short time, for example, 0.5 to 6 hours. It will be done.
本発明の処理法においては、高炉滓を水性媒質中で湿式
粉砕することが特に望ましい。In the treatment method of the present invention, it is particularly desirable to wet-mill the blast furnace slag in an aqueous medium.
即ち、高炉滓を乾式で粉砕する場合には、高炉滓中の硫
黄分が硫化水素の形で揮散したり、或いは粉砕時、或い
は移送中に粉塵の飛散が生じたりして二次公害を惹起す
るおそれがあり、これを防止するために格別の設備が必
要となる。In other words, when blast furnace slag is dry-pulverized, the sulfur content in the blast furnace slag may volatilize in the form of hydrogen sulfide, or dust may be scattered during grinding or transportation, causing secondary pollution. Special equipment is required to prevent this.
これに対して、水性媒質中で高炉滓を湿式粉砕するとき
には、高炉滓中に含有される硫黄分が水性媒質中に有効
に捕集され且つ粉塵飛散の問題も解消される。On the other hand, when blast furnace slag is wet-pulverized in an aqueous medium, the sulfur content contained in the blast furnace slag is effectively captured in the aqueous medium, and the problem of dust scattering is also solved.
湿式粉砕の液体媒質としては、水理外の液体、例えばメ
タノール、トルエン、キシレン、トリクレン、パークレ
ン等の各種有機液体も勿論使用可能であるが、水は最も
安価に入手し得る液体であり且つまた、粉砕後の高炉滓
をアルカリ性の水性媒体で処理(抽出・熟成処理)する
関係で、水が最も好適である。As a liquid medium for wet grinding, non-hydraulic liquids such as methanol, toluene, xylene, trichlene, perchlorene, and various other organic liquids can of course be used, but water is the least expensive liquid available, and Since the blast furnace slag after pulverization is treated with an alkaline aqueous medium (extraction/ripening treatment), water is most suitable.
本発明によれば、上述した粒度に湿式粉砕された高炉滓
微粒子を、pH10乃至13のアルカリ性水性媒質中で
60乃至95℃の温度で且つ90分を越えない時間接触
させることにより、高炉滓中の硫黄分を、沈澱として再
析出させるこさなく安定な溶液の形で水性媒質中に溶出
させ、高炉滓中の硫黄分を有効に除去できる。According to the present invention, blast furnace slag fine particles wet-milled to the above particle size are brought into contact with an alkaline aqueous medium having a pH of 10 to 13 at a temperature of 60 to 95° C. for a period not exceeding 90 minutes. The sulfur content in the blast furnace slag can be effectively removed by eluting the sulfur content in the aqueous medium in the form of a stable solution without re-precipitating as precipitate.
即ち、水性媒質中に溶出させた硫黄分が沈澱として析出
するような条件では、沈澱した硫黄分が処理後の高炉滓
に混入し、硫黄分の除去率も濾過性を著しく低下するこ
とになる。In other words, under conditions where the sulfur content eluted into the aqueous medium is precipitated, the precipitated sulfur content will be mixed into the blast furnace slag after treatment, and the sulfur content removal rate and filterability will be significantly reduced. .
力)かる見地からは、高炉滓中の硫黄分を迅速に水性媒
質中に移行させるこ吉、及び溶出させた硫黄分を溶液の
形で処理中安定化させるこさが必要となる。From this point of view, it is necessary to quickly transfer the sulfur content in the blast furnace slag into an aqueous medium, and to stabilize the eluted sulfur content in the form of a solution during treatment.
先ず、高炉滓を最大粒径が50μ以下となるように湿式
粉砕することは、硫黄分の水性媒質中への溶出を促進す
る上で重要であり、また水性媒質のpHを、10乃至1
3の範囲に保つことも、硫黄分の溶出速度を高め、更に
水性媒質に溶出した硫黄分を沈澱させることなく安定に
維持する上で重要な意味を有する。First, wet grinding of blast furnace slag to a maximum particle size of 50μ or less is important in promoting the elution of sulfur content into the aqueous medium, and the pH of the aqueous medium is adjusted to 10 to 1.
Maintaining the sulfur content within the range of 3 also has an important meaning in increasing the elution rate of sulfur content and further stably maintaining the sulfur content dissolved in the aqueous medium without precipitating it.
更に、接触時の温度を60乃至95°Cとすることも硫
黄分の溶出速度を向上させ、溶出した硫黄分を安定に保
ち、更に処理後の高炉滓粒子の沖過性を向上させる上で
重要であり、し力)も硫黄の沈澱生成を抑制する上では
、この処理は90分以内で完結しなければならない。Furthermore, setting the temperature at the time of contact to 60 to 95°C also improves the leaching rate of sulfur content, keeps the eluted sulfur content stable, and further improves the permeability of blast furnace slag particles after treatment. In order to suppress the formation of sulfur precipitates, this treatment must be completed within 90 minutes.
接触処理時のpHが上記範囲外では、何れも硫黄溶出液
の安定性が低下する傾向があり、また温度が95℃を越
えると、やはり硫黄分が沈澱として析出する傾向がある
。If the pH during contact treatment is outside the above range, the stability of the sulfur eluate tends to decrease, and if the temperature exceeds 95°C, sulfur content tends to precipitate.
水性媒体のpHを上記範囲に維持するために、水酸化ナ
トリウム、炭酸ソーダ等のアルカリ金属の水酸化物や炭
酸塩;或いは水酸化カルシウム等のアルカリ土類金属の
水酸化物や炭酸塩アンモニア等のアルカリ剤を積極的に
水性媒体中に添加し、。In order to maintain the pH of the aqueous medium within the above range, alkali metal hydroxides and carbonates such as sodium hydroxide and soda carbonate; or alkaline earth metal hydroxides and carbonates such as calcium hydroxide, ammonia, etc. The alkaline agent is actively added into the aqueous medium.
このアルカリ性媒質中で硫黄分の溶出を行わせるこきが
特に望ましい。Particularly desirable is a wood that causes the sulfur content to be leached out in this alkaline medium.
また、高炉滓は38〜43%のCaOを含有することか
らも明ら力)な如く、強い塩基性を有しており、高炉滓
を水性媒体中で湿式粉砕したスラリー・は、一般に11
乃至12の強いアルカリ性を示す。In addition, blast furnace slag has a strong basicity as shown by the fact that it contains 38 to 43% CaO, and slurry obtained by wet grinding blast furnace slag in an aqueous medium generally has a
Shows strong alkalinity of 1 to 12.
力)<シて、本発明の接触処理は、この湿式粉砕で得ら
れたスラリーをそのま5熟成処理に賦してもよいが、こ
の場合には2段以上の接触処理を行うことが特に望まし
い。In the contact treatment of the present invention, the slurry obtained by this wet grinding may be directly subjected to a 5-stage aging treatment, but in this case, it is particularly preferable to carry out two or more stages of contact treatment. desirable.
接触処理に際して、高炉滓のスラリー濃度は広範囲に変
化させ得るが、一般的に言って、10乃至60重量%、
特に20乃至45重量%の固形分濃度とするのが好まし
い。During the contact treatment, the slurry concentration of the blast furnace slag can be varied over a wide range, but generally speaking, it is between 10 and 60% by weight;
In particular, a solid content concentration of 20 to 45% by weight is preferred.
即ち、スラリー濃度が上記範囲よりも高い場合には、硫
黄分の抽出除去率が低下する傾向があり、またスラリー
濃度を上記範囲よりも低くすることは、大量の液を取扱
はねはならない点で操作上不利となる。That is, if the slurry concentration is higher than the above range, the extraction removal rate of sulfur content tends to decrease, and reducing the slurry concentration lower than the above range is important because it is necessary to avoid handling a large amount of liquid. This is disadvantageous for operation.
前述した接触時間とは、高炉滓と一定の水性媒体との接
触時間であり、バッチ式接触操作において、ワンバッチ
で90分間よりも長時間の接触は避けるべきであるとい
うことである。The above-mentioned contact time is the contact time between the blast furnace slag and a certain aqueous medium, and in a batch contact operation, contact for a longer time than 90 minutes in one batch should be avoided.
勿論、バッチ式接触操作でも、多段式に接触を行なう場
合には、全体として90分間よりも長時間の接触を行っ
ても同等差支えなく、またカラムに高炉滓を充填し、こ
れに水性媒体を連続又は間欠的に通して両者の接触を行
う場合にも長時間にわたる接触が可能である。Of course, even in batch-type contact operations, when contact is carried out in multiple stages, there is no problem even if the total contact time is longer than 90 minutes. Contact over a long period of time is also possible when the two are brought into contact continuously or intermittently.
本発明において、高炉滓の粉砕及び水性媒体との接触処
理により、高炉滓中の硫黄分が水性媒体中に溶出する機
構の詳細は未だ不明である。In the present invention, the details of the mechanism by which the sulfur content in the blast furnace slag is eluted into the aqueous medium by the grinding of the blast furnace slag and the contact treatment with the aqueous medium are still unknown.
しかしながら、接触後分離された抽出液が黄色の透明な
液であること、及びこの硫黄抽出液がアルカリ性の媒質
中で形成されることからみて、高炉滓中の硫黄分はポリ
硫化物の形で水性媒体中に溶出しているものと信じられ
る。However, considering that the extract separated after contact is a yellow transparent liquid and that this sulfur extract is formed in an alkaline medium, the sulfur content in blast furnace slag is in the form of polysulfides. It is believed that it is eluted into the aqueous medium.
湿式粉砕時における硫黄の析出を防止するには、(1)
湿式粉砕を可及的に短時間で行なう、(11)湿式粉砕
の温度を可及的に低くする、曲)湿式粉砕時の水性媒体
のpHをあまり高くしない等の配慮が望ましい。To prevent sulfur precipitation during wet grinding, (1)
It is desirable to carry out wet pulverization in as short a time as possible, (11) to keep the temperature of wet pulverization as low as possible, and (1) to not make the pH of the aqueous medium during wet pulverization too high.
粉砕工程及び接触工程はバッチでも連続操作でも行い得
る。The milling and contacting steps can be carried out in batch or continuous operations.
例えば、チューブミル等に粗砕された高炉滓と水性媒体
とを供給し、微粉砕された高炉滓の水性スラリーを連続
的に取出すこきにより連続的に粉砕することができる。For example, it is possible to supply coarsely crushed blast furnace slag and an aqueous medium to a tube mill or the like, and continuously take out an aqueous slurry of the finely crushed blast furnace slag to continuously crush the blast furnace slag.
勿論、この際高炉滓の湿式粉砕スラリーを液体サイクロ
ンの如き分級機に通して、所定粒度以外の高炉滓は微粉
砕機に循環するようにする。Of course, at this time, the wet-pulverized slurry of blast furnace slag is passed through a classifier such as a hydrocyclone, and blast furnace slag other than a predetermined particle size is circulated to the pulverizer.
また、高炉滓さアルカリ性水性媒体との接触処理は、一
段にも或いは多段にも行うこさができ、一般には、接触
処理を少なくとも二段に行うことが後述する実施例に示
す通り、好ましい。Further, the contact treatment of the blast furnace slag with the alkaline aqueous medium can be carried out in one stage or in multiple stages, and it is generally preferable to carry out the contact treatment in at least two stages, as shown in the examples below.
更に高炉滓とアルカリ土類金属体とを、向流式或いは併
流式に連続して接触させ、熟成を行うことができる。Furthermore, the blast furnace slag and the alkaline earth metal body can be brought into continuous contact in a countercurrent or cocurrent manner to effect aging.
或いは更に、高炉滓さアルカリ性水性媒体とを流動床を
用いて接触させ、抽出及び熟成を行ってもよい。Alternatively, extraction and aging may be performed by bringing the blast furnace slag into contact with an alkaline aqueous medium using a fluidized bed.
前述した接触処理により形成された硫黄分の抽出液き硫
黄分が除去された鉱炉滓とは、濾過、遠心分離、デカン
テーション等の任意の固−液分離操作で分離する。The sulfur extract formed by the above-mentioned contact treatment and the slag from which the sulfur content has been removed are separated by any solid-liquid separation operation such as filtration, centrifugation, or decantation.
この際、本発明の接触処理を経た高炉滓微粒子は濾過性
等に優れていることが顕著な利点であり、固−液分離操
作を至って容易に行い得る。At this time, the blast furnace slag fine particles subjected to the contact treatment of the present invention have a remarkable advantage that they are excellent in filterability, etc., and the solid-liquid separation operation can be carried out very easily.
分離された硫黄抽出液からの硫黄分の回収はそれ自体公
知の手段で容易に行い得る。The sulfur content from the separated sulfur extract can be easily recovered by means known per se.
例えば、この硫黄分抽出液に、硝酸等の酸水溶液を添加
して、液のpHを3〜4の範囲とすることにより、硫黄
分を固体の形で容易に沈殿させることができる。For example, by adding an aqueous acid solution such as nitric acid to the sulfur extract to adjust the pH of the solution to a range of 3 to 4, the sulfur can be easily precipitated in solid form.
また、充分アルカリ側の硫黄抽出液に、例えば過酸化水
素を少量添加して硫黄分を析出させることもできる。Furthermore, the sulfur content can be precipitated by adding, for example, a small amount of hydrogen peroxide to the sufficiently alkaline sulfur extract.
71)<L、て、この沈殿を濾過等の固−液分離操作に
賦することにより硫黄分を高純度の固体の形で回収し得
る。71)<L, the sulfur content can be recovered in the form of a highly pure solid by subjecting this precipitate to a solid-liquid separation operation such as filtration.
また、硫黄抽出液に石灰、炭酸バリウム等を添加すると
、硫化カルシウム、硫化バリウム等の形で硫黄分を回収
し得る。Furthermore, by adding lime, barium carbonate, etc. to the sulfur extract, sulfur content can be recovered in the form of calcium sulfide, barium sulfide, etc.
本発明において、硫黄抽出液から硫黄分を回収する方法
は上に例示した方法に限定されない。In the present invention, the method for recovering sulfur from the sulfur extract is not limited to the method exemplified above.
硫化物の水溶液から硫黄分を種々の形で回収する方法は
多数公知であり、これら公知の手法は何れも本発明に適
用可能である。There are many known methods for recovering sulfur in various forms from an aqueous sulfide solution, and any of these known methods can be applied to the present invention.
本発明において、硫黄分を回収して得られる母液は、清
澄で無色の液であり、直接或いは所望によりpuを適当
な範囲に調節した後、前述した湿式粉砕工程、或いは接
触処理工程の水性媒体として反復使用することができ、
これにより廃水処理の煩わしさを解消することができる
。In the present invention, the mother liquor obtained by recovering the sulfur content is a clear and colorless liquid, and it can be used directly or after adjusting the PU to an appropriate range as desired, and then used as an aqueous medium in the wet grinding process or the contact treatment process described above. can be used repeatedly as
This eliminates the hassle of wastewater treatment.
硫黄分が実質的に除去された高炉滓は、必要により水洗
、乾燥或いはその他の後処理を行うことができる。The blast furnace slag from which the sulfur content has been substantially removed can be washed with water, dried, or subjected to other post-treatments, if necessary.
例えば、この高炉滓を300℃以上の高温で焼成し、或
いは粒状に焼結して形態や性質を安定化させることがで
きる。For example, this blast furnace slag can be fired at a high temperature of 300° C. or higher or sintered into particles to stabilize its morphology and properties.
まfこ、この高炉滓を硫酸、硝酸、塩酸等の酸で処理し
て、高炉滓の塩基度を中性或いはその近辺に調節するこ
とができる。By treating this blast furnace slag with an acid such as sulfuric acid, nitric acid, or hydrochloric acid, the basicity of the blast furnace slag can be adjusted to be neutral or close to it.
本発明の処理を行った高炉滓は有害な硫黄分が実質的に
除去されているため、埋立材、或いは道路、線路、空港
等の路盤材として、また七メント原料、スラグウール、
その他の窯業用原料、各種充填剤、肥料、土壌改質材等
の用途に有利に使用することができる。Since the blast furnace slag treated according to the present invention has substantially removed harmful sulfur content, it can be used as landfill material, roadbed material for roads, railways, airports, etc., as well as as raw material for slag wool, slag wool, etc.
It can be advantageously used for other ceramic raw materials, various fillers, fertilizers, soil improvement materials, etc.
本発明を次の例で説明する。The invention is illustrated by the following example.
実施例 1
下記組成
成 分 重量%
Ca0 40.9AI2
0314.6
S io 2 35−4Mg0
5.8Ti020.6
Fe6Fe2O
3060,7
S O,83
灼熱減量 0.6
を有する空冷源の粗砕物10kgを、水151と共に、
内容積301のボールミル中に装入し、30℃以下の温
度に保持しつX、6時間湿式粉砕して、300メツシユ
(タイラー標準)師全通(粒径44μ以下)の高炉滓粉
末の水性スラリー(固形濃度40重量%)131を得た
。Example 1 The following composition components Weight % Ca0 40.9AI2
0314.6 S io 2 35-4Mg0
5.8Ti020.6 Fe6Fe2O 3060,7 S O,83
10 kg of crushed material from an air-cooled source having a loss on ignition of 0.6 was mixed with 151 kg of water,
Charged into a ball mill with an internal volume of 301, the water-based blast furnace slag powder was charged into a ball mill with an internal volume of 301, and wet-milled for 6 hours while maintaining the temperature at 30°C or lower to obtain a 300-mesh (Tyler standard) grain size (particle size of 44μ or less). Slurry 131 (solid concentration 40% by weight) was obtained.
この水性スラリーのpHは12であった。The pH of this aqueous slurry was 12.
得られた水性スラリーを、100A’の攪拌機付容器に
入れ、85℃の温度で1時間加温接触を行つ1こ。The obtained aqueous slurry was placed in a 100 A' container equipped with a stirrer, and heated and contacted at a temperature of 85° C. for 1 hour.
接触後のスラリーを、濾紙(別3)を備えた減圧PJ機
(即ち直径50crrLのヌツチェに供給し、650m
mH,V差圧の減圧下に濾過した。The slurry after contact is supplied to a vacuum PJ machine (i.e., 50 crrL in diameter) equipped with a filter paper (Separate 3),
It was filtered under reduced pressure of mH, V differential pressure.
濾過速度は単位時間当りのP液量(ll/m1n)で表
示して、3.211/minであツタ。The filtration rate is expressed as the amount of P liquid per unit time (ll/ml), and is 3.211/min.
得られたP液は透明な黄色液であった。The obtained P liquid was a transparent yellow liquid.
一方得られたケーキは前記濾過方式で上部よりゆっくり
と25℃の水61を流しつN洗浄し、硫黄分の除去され
た高炉滓を回収した。On the other hand, the obtained cake was washed with N by slowly flowing water 61 at 25° C. from the top using the above-mentioned filtration method, and the blast furnace slag from which the sulfur content had been removed was recovered.
次いで、ろ液及び洗液を集め、3規定硝酸を攪拌下に添
加して、液のpHを3.5に調節し、溶解している硫黄
分を固体硫黄として析出せしめ、ここに生成した固体硫
黄を濾過により分離した。Next, the filtrate and washing liquid were collected, 3N nitric acid was added under stirring to adjust the pH of the liquid to 3.5, and the dissolved sulfur content was precipitated as solid sulfur. The sulfur was separated by filtration.
処理後の高炉滓粉末の分析結果より硫黄分の除去率は6
2.1重量%であった。Based on the analysis results of the blast furnace slag powder after treatment, the sulfur content removal rate was 6.
It was 2.1% by weight.
またろ液から回収した固体硫黄より高炉滓に含有される
硫黄の回収率を算出した結果、59.5%であった。Furthermore, the recovery rate of sulfur contained in the blast furnace slag was calculated from the solid sulfur recovered from the filtrate and was found to be 59.5%.
比較例 1
実施例1において湿式粉砕にて回収したpH12の高炉
滓粉末の水性スラリーを加熱接触処理することなしに、
前記直径40cIrtのヌツチェを用いて同様の条件下
に濾過し1こところ、その濾過速度は1、117m1
nであった。Comparative Example 1 The aqueous slurry of blast furnace slag powder with a pH of 12 recovered by wet pulverization in Example 1 was treated without heating and contact treatment.
When filtration was performed under the same conditions using the Nutsche with a diameter of 40 cIrt, the filtration rate was 1,117 m1.
It was n.
また、PJ後の高炉滓の分析結果より硫黄分の除去率は
24.8%であり、p液から回収した硫黄分から回収率
は19.7%であった。Furthermore, from the analysis results of the blast furnace slag after PJ, the removal rate of sulfur content was 24.8%, and the recovery rate of sulfur content recovered from P liquid was 19.7%.
実施例 2
本実施例は、硫黄分を分離した後の母液を本発明の処理
に反復使用し得ることを示す。Example 2 This example shows that the mother liquor after separation of the sulfur content can be used repeatedly in the process of the present invention.
更に、実施例1で得られた硫黄除去率62.1重量%の
ケーキを、実施例1で得た硫黄を回収した母液15Aと
混合して、スラリーとし、そのスラリーを実施例1と同
様に攪拌機付容器に入れて、攪拌しながら約90℃に加
熱して約1時間接触処理した。Furthermore, the cake with a sulfur removal rate of 62.1% by weight obtained in Example 1 was mixed with the mother liquor 15A from which sulfur was recovered obtained in Example 1 to form a slurry, and the slurry was mixed in the same manner as in Example 1. The mixture was placed in a container equipped with a stirrer, heated to about 90° C. while stirring, and subjected to contact treatment for about 1 hour.
スラリーのpHは12で、同じ減圧条件での濾過性は若
干向上した(濾過速度:3.61/m1n)。The pH of the slurry was 12, and the filterability under the same reduced pressure conditions was slightly improved (filtration rate: 3.61/ml).
戸別したケーキは約51の水で洗浄し、これを110℃
の温度で乾燥して硫黄除去率93.5 (重量)%の高
炉滓微粉末を得た。The cake that was sent from door to door was washed with about 51 degrees of water and then heated to 110 degrees Celsius.
The blast furnace slag powder was dried at a temperature of 93.5% (by weight) with a sulfur removal rate of 93.5% (by weight).
また、硫黄含有液に3規定硝酸を加えてpHを約35に
調整し硫黄を析出させた。Further, 3N nitric acid was added to the sulfur-containing liquid to adjust the pH to about 35 to precipitate sulfur.
実施例1で得た硫黄分と併せて、全体としての硫黄分回
収率は85.6%であった。Including the sulfur content obtained in Example 1, the overall sulfur content recovery rate was 85.6%.
実施例 3
この例は湿式粉砕スラリーに石灰を加えて接触処理を行
う場合を説明する。Example 3 This example describes a case where lime is added to a wet milled slurry and contact treatment is performed.
実施例1に用いた高炉空冷滓200gを水500m1に
加え、約6時間ボールミル粉砕処理して、実質的に30
0メツシユ以下の微細粉末高炉滓からなるスラリーを得
た。200 g of the blast furnace air-cooled slag used in Example 1 was added to 500 ml of water, and the mixture was ball-milled for about 6 hours to obtain a
A slurry consisting of finely powdered blast furnace slag of 0 mesh or less was obtained.
このスラリーのpHは約12であつ1こ。The pH of this slurry was about 12.
このスラリーに石灰12gを加えて約80℃に加温し、
攪拌条件下に1時間接触処理した。Add 12g of lime to this slurry and heat it to about 80℃,
The contact treatment was carried out for 1 hour under stirring conditions.
直ちに減圧濾過し、r液に30%過酸化水素水数滴を加
えてよく攪拌した。Immediately, the mixture was filtered under reduced pressure, and several drops of 30% hydrogen peroxide were added to the r solution, followed by thorough stirring.
液のpHは約9.7に低下し、微粒状硫黄分が析出した
。The pH of the liquid decreased to about 9.7, and fine sulfur particles were precipitated.
この液から硫黄分を戸別し、約20rrLlの水で洗浄
し、洗液を母液と合し1こ。The sulfur content is removed from this liquid, washed with about 20rrLl of water, and the washing liquid is combined with the mother liquor to make 1 bottle.
この硫黄分を除いた液と上記の戸別されたケーキを混合
し再度抽出処理した。The liquid from which the sulfur content had been removed was mixed with the above-mentioned cake, and extracted again.
処理条件は同様にスラリーを約80℃の温度に保ち攪拌
下に約1時間接触処理させた。The treatment conditions were as follows: the slurry was kept at a temperature of about 80° C. and the contact treatment was carried out for about 1 hour while stirring.
スラリーのpH,は約12.5であった。The pH of the slurry was approximately 12.5.
このスラリーを直ちに濾過し、温度30℃の約100
m、eの水でケーキを洗浄し、ケーキは105℃の恒温
槽中で乾燥した。This slurry was immediately filtered and
The cake was washed with water in m and e, and the cake was dried in a constant temperature bath at 105°C.
洗浄液を含むP液に数滴の濃過酸化水素水を攪拌下に滴
加し、析出した硫黄分をP過分離し1こ。A few drops of concentrated hydrogen peroxide solution are added dropwise to the P solution containing the cleaning solution while stirring, and the precipitated sulfur content is separated by P over-separation.
ケーキを乾燥した処理高炉滓の分析値から、硫黄分の除
去率は99.7%であり、硫黄分は完全に除去されてい
ることが確認され1こ。Analysis of the treated blast furnace slag obtained by drying the cake showed that the sulfur content removal rate was 99.7%, confirming that the sulfur content was completely removed1.
比較例 2
本例は、高炉滓粉末の粒径が硫黄分の抽出に重要な影響
を与えることを示す。Comparative Example 2 This example shows that the particle size of blast furnace slag powder has an important effect on the extraction of sulfur content.
実施例1の空冷滓を乾式粉砕して、各種粒度に調整した
ものを用いて脱硫処理を行った。The air-cooled slag of Example 1 was dry-pulverized and adjusted to various particle sizes, which were then subjected to desulfurization treatment.
処理条件は試料滓200gを500m1の水に投入懸濁
させ、攪拌下に処理し、硫黄分を溶出せしめた。The treatment conditions were as follows: 200 g of the sample dregs was suspended in 500 ml of water and treated under stirring to elute the sulfur content.
この抽出時の温度及び時間を変えて、各種粒度範囲のも
のについて接触処理を行った際の硫黄除去率(%)を下
記第2表にまとめた。Table 2 below summarizes the sulfur removal rate (%) when contact treatment was performed on particles in various particle size ranges by changing the temperature and time during this extraction.
上掲第2表から、150メツシユ篩を通過しない粒度(
最大粒径80μより木)の高炉滓では、硫黄分の実質的
な量を抽出せしめ得ないことが明白である。From Table 2 above, the particle size that does not pass through a 150 mesh sieve (
It is clear that a substantial amount of sulfur cannot be extracted from blast furnace slag with a maximum particle size of 80 μm or more.
ま1こ、乾式粉砕の際に、かなりの量の硫化水素が発生
することが酢酸鉛塗布試験紙の変色から確認された。Furthermore, it was confirmed from the discoloration of the lead acetate coated test paper that a considerable amount of hydrogen sulfide was generated during dry grinding.
実施例 4
本実施例は、湿式粉砕時の水性媒体の種類及び時間を変
化させ1こ場合について説明する。Example 4 This example describes cases in which the type of aqueous medium and time during wet grinding are varied.
実施例1で用いた高炉滓200gを、下記第3表に示す
水性媒体250m1と共に、1.51内容積のボールミ
ル中に装入し、第3表に示す時間湿式粉砕した。200 g of the blast furnace slag used in Example 1 was charged into a ball mill having an internal volume of 1.51 ml together with 250 ml of the aqueous medium shown in Table 3 below, and wet-pulverized for the time shown in Table 3.
300メツシュ通過の湿式粉砕スラリーに水を添加して
500m1とし、これを85℃で30分間加温処理し、
減圧沢過し、洗滌なしに残渣を乾燥した。Water was added to the wet-pulverized slurry that had passed through 300 meshes to make 500ml, and this was heated at 85°C for 30 minutes,
It was filtered under reduced pressure and the residue was dried without washing.
残渣の分析結果より、硫黄分の除去率を求め、第3表に
示した。Based on the analysis results of the residue, the sulfur content removal rate was determined and shown in Table 3.
上記第3表の結果は、長時間の湿式粉砕は硫黄分除去率
の低下をもたらし、6時間以内での湿式粉砕が望才しい
ことを示している。The results in Table 3 above show that long-term wet milling results in a decrease in the sulfur content removal rate, and that wet milling within 6 hours is desirable.
比較例 3 本例は、高炉滓粉末の抽出処理時のpHの影響を示す。Comparative example 3 This example shows the influence of pH during the extraction process of blast furnace slag powder.
実施例1において得られ1こ湿式粉砕スラリー200m
Aに硝酸を加えて、pHを8.0に維持し、85℃で1
時間加湿処理した後、減圧下にFJして残渣を分離し1
こ。200 m of wet milled slurry obtained in Example 1
Add nitric acid to A, maintain the pH at 8.0, and heat at 85°C for 1
After humidifying for a period of time, perform FJ under reduced pressure to separate the residue.
child.
この操作を3回行ない、得られた結果を、実施例1及び
2の結果と比較して第4表に示す。This operation was performed three times, and the results obtained are shown in Table 4 in comparison with the results of Examples 1 and 2.
上記第4表の結果から、抽出時のpHを8よりも高くす
ることが硫黄分の除去に重要なことが了解される。From the results in Table 4 above, it is understood that increasing the pH during extraction to a value higher than 8 is important for removing sulfur content.
実施例 5
本例は、水性媒体に添加するアルカリ剤の種類及び添加
量を変化させた場合について説明する。Example 5 This example describes a case where the type and amount of the alkaline agent added to the aqueous medium are changed.
実施例1で得た湿式粉砕スラリー200m1に、下記第
5−A表に示す種類及び量のアルカリ剤を含む水溶液3
00m1を添加し、実施例4と同様に処理した。Aqueous solution 3 containing the type and amount of alkali agent shown in Table 5-A below was added to 200 ml of the wet-pulverized slurry obtained in Example 1.
00ml was added and treated in the same manner as in Example 4.
得られた結果を第5−A表に示す。上記第5−A表によ
ると、何れのアルカリ剤を用いる場合にも、硫黄除去率
の向上かも1こらされる。The results obtained are shown in Table 5-A. According to Table 5-A above, no matter which alkali agent is used, the sulfur removal rate can be improved by 1.
同第5−A表中Na2CO3の欄の0内の数字はNaO
H換算のグラム数を示す。The numbers within 0 in the Na2CO3 column in Table 5-A are NaO.
Shows the number of grams converted into H.
尚、実験番号1乃至3及び7乃至9については、水性媒
体中に添加したアルカリ分を硫黄分の抽出に反復再利用
可能であることを、炉液のNa分を定量することにより
確認した。For Experiments Nos. 1 to 3 and 7 to 9, it was confirmed by quantifying the Na content of the furnace liquid that the alkaline content added to the aqueous medium could be repeatedly reused for extracting sulfur content.
下記第5−B表には、抽出用水性媒体中に含有されるア
ルカリ分のろ液への移行率(%)を示す。Table 5-B below shows the transfer rate (%) of alkaline content contained in the aqueous extraction medium to the filtrate.
実施例 6 本例は、水性媒体での抽出時間の影響を示す。Example 6 This example shows the effect of extraction time in aqueous media.
実施例1で得た湿式粉砕スラ’J−200mlに、(a
)試薬1級CaO1及び(b)硝酸カルシウムの熱分解
で得られ7jCaO各々3yを含む水300m1!を加
え、時間を30分、60分及び120分と変化させて、
実施例4と同様に抽出・熟成処理を行った。To 200 ml of wet pulverized slurry 'J-obtained in Example 1, (a
) reagent primary CaO1 and (b) 300 ml of water each containing 3y of 7jCaO obtained by thermal decomposition of calcium nitrate! and changing the time to 30 minutes, 60 minutes and 120 minutes,
Extraction and ripening treatments were performed in the same manner as in Example 4.
結果を第6表に示す。The results are shown in Table 6.
上掲第6表は60分間程度までの接触処理が説硫率の向
上に望ましいことを示している。Table 6 above shows that contact treatment for up to about 60 minutes is desirable for improving the sulfur rate.
尚、実験番号5の残渣を、そのp液力)ら実施例3のよ
うに硫黄を除去し1こ液中で、且つ85℃で30分間接
触処理を行ない、次いて沖過分離を行った残渣は938
%の硫黄除去率を示した。In addition, the residue of Experiment No. 5 was subjected to contact treatment for 30 minutes at 85°C for 30 minutes after removing sulfur from the p liquid as in Example 3, and then subjected to Oki separation. The residue is 938
% sulfur removal rate.
実施例 7
本例は高炉滓とアルカリ性媒体とを接触させる際の液量
比の影響を示す。Example 7 This example shows the influence of the liquid volume ratio when bringing blast furnace slag and alkaline medium into contact.
実施例1で得た湿式粉砕スラ’J −200mlに、3
gの水酸化カルシウム及び水をサスペンションの形で加
え、全液量を下記第7表に示す量とした。To 200 ml of wet pulverized slurry 'J obtained in Example 1, 3
g of calcium hydroxide and water were added in the form of a suspension, making the total liquid volume as shown in Table 7 below.
次いで、実施例4と同様に処理した。It was then treated in the same manner as in Example 4.
結果を第7表に示す。The results are shown in Table 7.
実施例 8 本例は、2段接触処理の例を示す。Example 8 This example shows an example of two-stage contact processing.
実施例1で得た湿式粉砕スラリー200m1に、(a)
試薬1級CaO2,5,i7及び、(b)試薬1級Ca
(OH)23gを夫々含有する水を添加し、下記第8
表に液量のスラリーとした。To 200 ml of the wet pulverized slurry obtained in Example 1, (a)
Reagent 1st class CaO2,5,i7 and (b) reagent 1st class Ca
Add water each containing 23 g of (OH) and
The liquid volume is shown in the table as a slurry.
このスラリーを実施例4と同様に1時間処理し、瀘過分
離し1こ。This slurry was treated in the same manner as in Example 4 for 1 hour, and filtered and separated.
このr液から実施例3の方法で硫黄分を除去し、この炉
液の第8表に示す量を前記ケーキに添加し、このスラリ
ーを更び実施例4と同様に30分間処理し、沖過脱液し
た。The sulfur content was removed from this R liquid by the method of Example 3, the amount of this furnace liquid shown in Table 8 was added to the cake, and this slurry was further treated for 30 minutes in the same manner as in Example 4. Excessive fluid removal occurred.
結果を第8表に示す。The results are shown in Table 8.
Claims (1)
砕し、生成する高炉滓微粒子スラリーをpH10乃至1
3のアルカリ性水性媒質中で60乃至95℃の潟+iで
且つ90分を越えない時間接触させて、高炉滓中に含有
される硫黄分を前記水性媒質中に沈澱させることなく溶
出させ、硫黄分の抽出液き硫黄分が実質的に除去された
高炉滓きを分離し、次いで硫黄分の抽出液から硫黄分を
それ自体公知の手段で分離することを特徴とする高炉滓
の処理法。 2 高炉滓粉末とアルカリ性水性媒体との接触を少なく
きも二段にわたって行なう特許請求の範囲第1項の処理
法。[Claims] 1. Blast furnace slag is wet-pulverized so that the maximum particle size is 50μ or less, and the resulting blast furnace slag fine particle slurry has a pH of 10 to 1.
The sulfur contained in the blast furnace slag is eluted without precipitating in the aqueous medium by contacting the blast furnace slag in an alkaline aqueous medium at 60 to 95°C for a period not exceeding 90 minutes. A method for treating blast furnace slag, which comprises separating the blast furnace slag from which the sulfur content has been substantially removed from the extract, and then separating the sulfur content from the sulfur-containing extract by means known per se. 2. The treatment method according to claim 1, wherein the contact between the blast furnace slag powder and the alkaline aqueous medium is carried out in at least two stages.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51021864A JPS5818335B2 (en) | 1976-03-02 | 1976-03-02 | Processing method for blast furnace slag |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51021864A JPS5818335B2 (en) | 1976-03-02 | 1976-03-02 | Processing method for blast furnace slag |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS52105576A JPS52105576A (en) | 1977-09-05 |
| JPS5818335B2 true JPS5818335B2 (en) | 1983-04-12 |
Family
ID=12066975
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP51021864A Expired JPS5818335B2 (en) | 1976-03-02 | 1976-03-02 | Processing method for blast furnace slag |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5818335B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS58182216A (en) * | 1982-04-19 | 1983-10-25 | 松下電器産業株式会社 | Condenser |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5637254A (en) * | 1979-08-31 | 1981-04-10 | Kogyo Gijutsuin | Surface property impreved water glanulated slag |
| JPH0616565U (en) * | 1992-02-20 | 1994-03-04 | エクスト化成株式会社 | Rain gutter equipment |
| JP5549375B2 (en) * | 2010-05-25 | 2014-07-16 | Jfeスチール株式会社 | Desulfurization slag treatment method, desulfurization flux manufacturing method, desulfurization slag continuous use method, and desulfurization slag treatment apparatus |
| JP5983537B2 (en) * | 2012-05-29 | 2016-08-31 | Jfeスチール株式会社 | Method for removing sulfur from slag containing sulfur |
Family Cites Families (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE2344324C3 (en) * | 1972-09-12 | 1979-02-08 | The Calumite Co. Europe, Antwerpen (Belgien) | Process for the treatment of sulphurous slag and its use |
| JPS5230922B2 (en) * | 1972-12-31 | 1977-08-11 | ||
| JPS535878B2 (en) * | 1973-08-27 | 1978-03-02 | ||
| JPS5324034B2 (en) * | 1973-09-28 | 1978-07-18 |
-
1976
- 1976-03-02 JP JP51021864A patent/JPS5818335B2/en not_active Expired
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS58182216A (en) * | 1982-04-19 | 1983-10-25 | 松下電器産業株式会社 | Condenser |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS52105576A (en) | 1977-09-05 |
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