JPS5842713A - Treatment of desulfurized slag - Google Patents
Treatment of desulfurized slagInfo
- Publication number
- JPS5842713A JPS5842713A JP14201181A JP14201181A JPS5842713A JP S5842713 A JPS5842713 A JP S5842713A JP 14201181 A JP14201181 A JP 14201181A JP 14201181 A JP14201181 A JP 14201181A JP S5842713 A JPS5842713 A JP S5842713A
- Authority
- JP
- Japan
- Prior art keywords
- slag
- desulfurized
- molten
- weight
- pan
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C21—METALLURGY OF IRON
- C21C—PROCESSING OF PIG-IRON, e.g. REFINING, MANUFACTURE OF WROUGHT-IRON OR STEEL; TREATMENT IN MOLTEN STATE OF FERROUS ALLOYS
- C21C5/00—Manufacture of carbon-steel, e.g. plain mild steel, medium carbon steel or cast steel or stainless steel
- C21C5/28—Manufacture of steel in the converter
- C21C5/36—Processes yielding slags of special composition
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Manufacturing & Machinery (AREA)
- Materials Engineering (AREA)
- Metallurgy (AREA)
- Organic Chemistry (AREA)
- Refinement Of Pig-Iron, Manufacture Of Cast Iron, And Steel Manufacture Other Than In Revolving Furnaces (AREA)
- Furnace Details (AREA)
Abstract
Description
【発明の詳細な説明】
本発明は崩壊性ををしたり苗木を溶出する脱硫スラグと
溶a製窮スラグ並びに適量の改質剤を溶融反応させて有
用地金(以下メタルと記す)を回収すると共に両スラグ
を改質する方法に関するものである。[Detailed description of the invention] The present invention recovers useful ingots (hereinafter referred to as metals) by melting and reacting desulfurized slag that has disintegrability or elutes seedlings, molten aluminum slag, and an appropriate amount of modifier. The present invention also relates to a method for modifying both slags.
一般に製鋼スラグはrおよびβ−2CaO−3iO2、
FIICAO(遊n石灰)主体で、ゲーレナイト(2C
aQ−AI、O,ll5IO,) 、アケルVナイト(
2CaO−1110・25102)、マグネタイト(h
、oヰ)、^マタイト(Fa、O,)、ウスレイトI禮
)等を含をしている。Generally, steelmaking slag is r and β-2CaO-3iO2,
Mainly FIICAO (played lime), Gehlenite (2C
aQ-AI, O, ll5IO,), Akel V Night (
2CaO-1110・25102), magnetite (h
, oii), ^matite (Fa, O,), usurite Ire), etc.
特殊なsI鯛ススラグペリクレース0−)を含佇する筋
合もあり、オートクレーブ処理jAsテ■法、200°
C%201E/a’、3時間保持、’Q 2 i〜1d
!111の粒度で、10に1以下を崩壊倫とする)を行
なうと約3011量%崩壊する。。There is also a case that contains a special sI sea bream slag periclase (0-), autoclave treatment, 200°
C%201E/a', held for 3 hours, 'Q2i~1d
! With a particle size of 111, if less than 1 in 10 is considered to be a disintegration rate, it will disintegrate by approximately 3011%. .
脱血スラグはカーバイドa硫スラッとソーダ脱硫スラグ
に大別される。カーバイド脱硫スラグはに1mの状りで
石灰やカーバイドを不活住ガスと共に吹込み、製鋼炉に
入れる前に取り除く。Blood removal slag is broadly classified into carbide a-sulfur slag and soda desulfurization slag. Carbide desulfurization slag is made by blowing lime and carbide into it along with inert gas in a 1 meter length, and removing it before putting it into the steelmaking furnace.
このスラグは不安定な砿黄分およびカルシウムと化合し
た確gI酸化物(例えばCn5)が生成していて冷′m
@象水したWDI+1水に■れたりすると砿黄分が19
出し、費水となったり、 P−Qd) ヤf −2ム←
510 xを合をするため膨張崩壊する性質があるし、
微小メタルやキッシェグラファイトな合イ1し、かつ未
反応のカーバイドがFA存しているとアセチレンを発生
することもある。This slag is composed of unstable copper and solid oxides (for example, Cn5) combined with calcium, and is cold.
@ Elephant water WDI + 1 When exposed to water, the yellow content is 19
P-Qd) Yaf -2mu←
510 It has the property of expanding and collapsing to combine x,
If fine metals or Kische graphite alloys 1 and unreacted carbides are present in the FA, acetylene may be generated.
ソーダ脱硫スラグはWIaの状態でm、鵠を投入し、k
i−炉に入れる前に取り除く。このスラグは鵬0が非常
に高い(r/J8〜28重ffi%)し、Nil、S
6を合をし不安定なN1tII酸化物を合會するため、
1btlJtnF?3水に需れたりすると硫黄分の溶出
1r−イオンの0出によりて円の高いN12となるし、
rb、oに営むため吸温しやすく崩壊住を盲するし、Q
小メタル、キッシェグラファイトを含をしている。Soda desulfurization slag was in the state of WIa, m
i-Remove before placing in oven. This slag has a very high concentration (r/J8~28 ffi%), Nil, S
6 to combine unstable N1tII oxide,
1btlJtnF? 3 When water is in demand, the sulfur content is eluted and 1r-ions are released, resulting in a high N12 value.
Because it lives in rb and o, it absorbs heat easily and is blind to collapse, and Q
Contains small metals and Quiche graphite.
すなわち、齢記ヨ種のスラグは4L崩壊したり、背水を
溶出したりするので、利用方法は少なく、一部セメント
Ix料等に利用されて、大部分は坦32:絽棄されてい
るが、公害防止上程立地の硼保等が鼎しくなり処分に困
りている−そこで本原ではこれらスラグの膨張・崩壊原
因テアルFIIcao、と一2caO−1aozを安定
鉱物組成、すなわち3ω・動212伽e岨03*!1G
、、2ωMIgO−2sio2% 2CaO@ Fe2
G3.4cao @ u、o、a &、03等Kil七
SV、急冷せずとも膨張、崩壊しないスラグとするもの
である。In other words, the slag of the 4L type collapses and releases backwater, so there are few uses for it, and some are used as cement Ix materials, but most of it is discarded. , pollution control sites are becoming more and more difficult to dispose of.Therefore, Motohara has investigated the causes of expansion and collapse of these slags, FIIIcao, and 12caO-1aoz, with a stable mineral composition, that is, 3ω and 212caO-1aoz.岨03*! 1G
,,2ωMIgO-2sio2% 2CaO@Fe2
G3.4cao @ u, o, a &, 03 etc. Kil7 SV, which is a slag that does not expand or collapse even without quenching.
又、不安定な硫費化合ぐ(例えば伽S等)と反応させ水
に対するり騨度の小さい―S 、 NS、保町等に疫化
させ背水のWaaSを防止する。なお、溶滓の粘性、固
化温度を低下さす[熱をW効刑用し1か)脱硫スラグに
合をしているキッシェグラファイトを窓部させたり1ス
ラグに含有するメタルをのる鍋の底部に凝集沈降させて
大きいメタル粒となす。更に1脱硫スラグに含有してい
る動イオンがC出するのを防止するためのろ鈎の9滓に
ランス状物を装入し、バブリングガスな送り、バブリン
グを行いながら粘板岩、頁岩、マサ土、カラミ、WJ’
ta廃砂等の一日以上から成る改質材、並びに脱硫スラ
グを投入し、静融拡歌反応を十分に行わせると、メタル
の回収が68でかつ躇スラグは改質され路盤材や骨材と
して利用することができるものである。In addition, by reacting with unstable sulfur compounds (for example, Kasa S, etc.) and infecting S, NS, Homachi, etc., which have a low tolerance to water, it is possible to prevent backwater WaaS. In addition, to reduce the viscosity and solidification temperature of the slag (by applying heat to the W), it is possible to make a window with Kische graphite that has been combined with the desulfurization slag, or to make a pan on which the metal contained in the slag is placed. It coagulates and settles at the bottom to form large metal particles. Furthermore, a lance-shaped material was charged into the 9 slags of the filter hook to prevent the mobile ions contained in the desulfurization slag from releasing C, and while bubbling gas was being fed, slate, shale, and masa soil were removed. , Karami, W.J.'
By introducing a modification material consisting of waste sand, etc. for more than one day, and desulfurization slag, and allowing the static melting reaction to occur sufficiently, the metal recovery will be 68%, and the slag will be modified and can be used as roadbed material or bone. It can be used as a material.
なお、粘性低下、固化温度低下等の目的で添加する上記
改質材の添加方法としては次の各nが考えられる。Note that the following methods of adding the above-mentioned modifier added for the purpose of lowering viscosity, lowering solidification temperature, etc. can be considered.
0製しノ炉内にIOHの最初又は途中から投入する。Insert the IOH into the 0-making furnace from the beginning or halfway.
■n国炉に出偏り投入する。■Input into the reactor of country n.
■c21炉から排出する溶滓流に接して投入する。■Put it in contact with the slag flow discharged from the c21 furnace.
ΦrAJ炉から排出する溶滓流の落下位置と戻して投入
する。The molten slag flow discharged from the ΦrAJ furnace is placed back to the falling position.
0のろ鍋の敷滓の代用として使Nする。Use as a substitute for slag in a pot.
・のろ缶内で溶滓とサンドイヲチ状になる様に投入する
。・Pour it into a slow can so that it forms a sandwich with the slag.
■のる飼内の溶滓にランス状oe装入し、バブリングガ
スを吹送みバブリングを行いながら投入する。■ A lance-shaped OE is charged to the molten slag in the Noru feedstock, and bubbling gas is blown into the slag while bubbling is performed.
・000・の方法で投入し、ランス状物を装入しバブリ
ングガスを吹込み、バブリングを行なう。-000- method, insert a lance-shaped object, blow bubbling gas, and perform bubbling.
ここで、スラグが溶りl状m1lk:ある間に、畠0.
、ju203 % re、03及び−20等を含有する
未利用資源や麿業廃索ぐを添加するのは溶敞調鯛滓の顕
熱を有効利用する為であり%m加物としてs1転あるい
はAI、O,のみでも充分であるが、溶a瀉度が高iの
で反応が生起しan欠点がある。Here, while the slag melts into an l-shaped m1lk: Hatake 0.
, ju203 % RE, 03 and -20, etc. are added to the unused resources and Maro Yasui to make effective use of the sensible heat of the sea bream slag. Although AI and O alone are sufficient, there is a disadvantage that reactions occur due to the high degree of solubility.
次に本願の作用効果を確かめる為に行なった実験及びそ
の結果を述べる。Next, an experiment conducted to confirm the effects of the present application and its results will be described.
実験試料は下お第1表に示すものを用いた。The experimental samples shown in Table 1 below were used.
これらの試料を10ト110″CのtriIa@肖ff
iテ24時間以上乾f!に61% i飼−脱硫スラグと
粘板岩q添加&9質は豐ンプルグラインダーで3W以下
に粗砕後、製嗣・脱硫スラグにつ−てのみa!遣して、
更にQ*5m以下に粗砕してヤーゲル錐な作りDIB温
度を測定した。又、同試料を使用してルツボ回転式粘度
測定機(100ボイスまで測定回−な測定機)で結対粘
度を各温度別に測定した。10 of these samples were heated to 110″C triIa@off
Dry for more than 24 hours! 61% i feed - desulfurization slag and slate q addition & 9 quality is only a! send,
Furthermore, the material was crushed to a size of Q*5m or less, and the DIB temperature was measured. Further, using the same sample, the combined viscosity was measured at each temperature using a crucible rotation type viscosity measuring machine (measuring machine capable of measuring up to 100 voices).
なお%8wn以下のN遍尾鉱をsIlマグネシアルツボ
に入れて、 11580’Cに保持したシリクニット電
気炉でIIs分間保持して溶解徨うンス駄のを装入し、
Alt 又は02ガスを吹込んでバブリングを行ない、
粘性低下、固化温度低下材を添加し1更に脱硫スラグを
添加してバブリングを行ない、爲涼スイッチを切り、1
200℃まで約25分間で下げ炉外に取り出し空冷した
。In addition, N tailings with a concentration of %8wn or less were placed in a sIl magnesia crucible and held in a siliknit electric furnace held at 11580'C for 2s minutes to melt.
Bubble by blowing Alt or 02 gas,
Add a viscosity reducing and solidifying temperature reducing agent, 1. Add desulfurization slag, perform bubbling, turn off the cooling switch, 1.
The temperature was lowered to 200° C. in about 25 minutes, and the mixture was taken out of the furnace and cooled in the air.
下、同化温度低下材と脱硼スラグを添加後ランス状Ce
装入してAir 又は02ガスを吹込んでバブリングを
行ないながらfiM (脱硫スラグから口取した1〜2
1のメタル)を添加して回収メタルのR度、回収率等を
調べた。Bottom, lance-shaped Ce after adding assimilation temperature reducing material and deborizing slag
While charging and bubbling with Air or 02 gas, fiM (1 to 2
1 metal) was added to investigate the R degree, recovery rate, etc. of the recovered metal.
g52表にng4温度の測定結果を、湧3衷に粘度測定
結果をそれぐれ示す。Table G52 shows the measurement results of NG4 temperature, and Table 3 shows the measurement results of viscosity.
第2表
以上述べた様に赤泥、粘板岩、マサ土、カラミ、鋳物猫
砂、頁岩、高炉スラグ、脱硫スラグΦ)等をわずか3〜
10重量%添加すると溶例温度、粘度は急激に低下する
。すなわち、製銅スラグ、脱硫スラグ外)単味で紘固化
温度も約1500℃と高(、すでに高温結晶鉱物の20
110・8i0.尋が生成している。As mentioned above in Table 2, only 3~
When 10% by weight is added, the melt temperature and viscosity decrease rapidly. In other words, the solidification temperature of copper slag and desulfurization slag is as high as approximately 1,500℃ (already higher than that of high-temperature crystalline minerals).
110・8i0. Hiro is generated.
しかし、粘゛板岩1頁岩、マサ土、鋳物高砂、カラ1%
脱硫スラグ@、高炉スラグ等の一穆以上を添加すると1
350℃でもほとんど固化せず、高炉スラグとほとんど
変らない様に固化温度、粘度ともに改良される。However, slate 1 shale, masa soil, cast Takasago, Kara 1%
Adding more than one slag of desulfurization slag, blast furnace slag, etc.
It hardly solidifies even at 350°C, and both the solidification temperature and viscosity have been improved so that it is almost the same as blast furnace slag.
節4表に試製スラグの生成鉱物を示す。Table 4 in Section 4 shows the minerals produced in the trial slag.
以上の如(、製鋼スラグ、脱硫スラグ(6)は単味で再
溶解しても2C・0・Si2.を含有し、急冷するとβ
−2CaOeSIO,とガラス主体物であるが徐冷する
と1−2CaO・Is io、を含有し崩壊性を有する
。As shown above, steelmaking slag and desulfurization slag (6) contain 2C・0・Si2. even if they are simply remelted, and when rapidly cooled, β
-2CaOeSIO, which is mainly glass, but when slowly cooled, it contains 1-2CaO•Isio and has disintegrability.
しかし、再溶解した製鋼溶滓に脱硫スラグ15重量九と
粘板岩、頁岩、マサ上等の−II1以上を4〜5重量%
添加し、バブリング処理を行なうと2CIO・F−01
4CaO*ムIJDs・F%On、2Cao*At@O
s* S iO!等を主体とするスラグとなる。However, 15% by weight of desulfurization slag and 4 to 5% by weight of -II1 or higher of slate, shale, masa, etc. are added to the remelted steelmaking slag.
When added and subjected to bubbling treatment, 2CIO・F-01
4CaO*MuIJDs・F%On, 2CaO*At@O
s*SiO! The slag consists mainly of
なお第4表の生成鉱物の略称を次に示す。The abbreviations of the minerals produced in Table 4 are shown below.
β−2CsO・・β−2CsO−S ! 0tC1F−
zcaoeF*、O。β-2CsO・・β-2CsO-S! 0tC1F-
zcaoeF*, O.
・C4AF−4CaOeA40.@Fe1o1G@
= 2CaOsA40.−8i0゜H・ ・−、Fす0
s
AK = 2CaO−MgO−28i%次に第5表に
溶出試験結果を示す。・C4AF-4CaOeA40. @Fe1o1G@
= 2CaOsA40. -8i0゜H・・−,Fs0
s AK = 2CaO-MgO-28i% Next, Table 5 shows the elution test results.
以上の結果を見ると、脱硫スラグ単味を再溶融させたの
みではB”、80j−イオンも溶出して、黄水の溶出は
防止できないが、赤泥、粘板岩、頁岩、マサ土%力う電
等の添加量を4〜5重量Sと脱硫スラグを約15重量X
添加して溶融反応を生起さ昔るとが一、 SO,t−イ
オンもほとんど溶出しなくなり背水の溶出防止ができる
。Looking at the above results, it can be seen that if only the desulfurization slag is remelted, B" and 80j- ions will also be eluted, and the elution of yellow water cannot be prevented. The amount of electricity added is 4 to 5 weight S and the desulfurization slag is about 15 weight
Once added to cause a melting reaction, almost no SO and t-ions will be eluted, making it possible to prevent the elution of backwater.
次−ζ第6表に回収メタ慶の粒度とその割合について示
す。Table 6 shows the particle size and proportion of the recovered meta-kei.
なお%仁の基礎実験に使用した粒銑(1〜2m)は脱硫
スラグから破砕、磁選後、回収した溶解歩留72重IN
の鉄粒を使用した。The granular pig iron (1 to 2 m) used in the basic experiment of percent iron was recovered from desulfurization slag after crushing and magnetic separation, and had a melting yield of 72 times IN.
iron grains were used.
以上の結果、製鋼スラグ単味の溶滓に粒銑を添加して、
も溶湯は凝集せず大きいメタル粒とならない、又、脱硫
スラグ■と粒銑を添加しても粘性が高いスラグで溶湯の
凝集はあまり行なわれていない。As a result of the above, by adding granular pig iron to the slag of steelmaking slag,
However, the molten metal does not coagulate and does not form large metal grains, and even if desulfurization slag (2) and granular pig iron are added, the molten metal does not coagulate much due to the slag being highly viscous.
しかし、脱硫スラグ■及び脱硫スラグ(ム、B)と粘板
岩1頁岩、マサ土、カラミ等と粒銑を添加すると*Sは
凝集し、大きいメタル粒となる。However, when desulfurization slag ■ and desulfurization slag (mu, B), slate 1 shale, masa soil, karami, etc., and granular pig iron are added, *S aggregates and becomes large metal grains.
次第7表に試製スラグの骨材試験結果を示す。Table 7 shows the aggregate test results for the trial slag.
備考 次に本願処理方法の一実施例について述べる。remarks Next, an embodiment of the present application processing method will be described.
図面に示す如く脱硫スラグ(1)をのろ鍋(2)に(約
1200kp)受滓し約30分後(まだかなり熱い)に
、製銅溶滓(3)を受け(受滓後、約20分、約750
% ) 、スラグ処理室(4) (ダストが飛散しない
様に三方を鉄板溶接し、他の一方はのる鍋が入ると、下
部に若干、冷却空気導入の為に空間を有したトビラを閉
じ)に入れ、天井クレーン(5)醤ζ吊した鉄製のおも
り(6)(先端を尖し重量的2oookf)によって、
表面硬化環を4ケ所割ってランスバイブ())に酸素を
送りながら溶滓に装入(酸素圧、[17−1okid、
酸累量2m’/win ) l、 、 t<ブリングを
行ないながら、ホッパー(8)の電動パイブレイク−を
動かし、ベビーコンベア(9)を経てシーート鵠から融
点低下材等の粘板岩、鋳物真砂、カラ鵞、高炉スラグ等
の混合物を約370 kfを約4分間で投入し、更に酸
素のみで約3分間後吹きを行なった。As shown in the drawing, the desulfurization slag (1) is received in the ladle (2) (approximately 1200 kp), and after approximately 30 minutes (still quite hot), the copper slag (3) is received (after receiving the slag, approximately 1200 kp) is received. 20 minutes, about 750
%), slag processing chamber (4) (Three sides are welded with iron plates to prevent dust from scattering, and the other side is closed with a door that has a small space at the bottom to introduce cooling air when a pot is placed on it. ) and suspended by an overhead crane (5) and an iron weight (6) (with a sharp tip and weighing 2OOOKF).
Break the surface hardening ring in 4 places and charge it to the slag while sending oxygen to the lance vibe () (oxygen pressure, [17-1okid,
Accumulated acid amount: 2 m'/win) l, , t < While performing the buffing, the electric pie break of the hopper (8) is moved, and the melting point reducing materials such as slate, foundry sand, etc. are transferred from the sheet to the baby conveyor (9). A mixture of slag, blast furnace slag, etc. was introduced at a pressure of about 370 kf for about 4 minutes, and after-blowing was performed for about 3 minutes using only oxygen.
バブリング中に発生するダストは集塵機軸で回収した。The dust generated during bubbling was collected by the dust collector shaft.
このスラグを放流場まで運搬し、破砕、aia処理を行
ない、溶出試験、路盤材試験を行ない第8表に示す。This slag was transported to a discharge field, crushed, treated with AIA, and subjected to an elution test and a roadbed material test, which are shown in Table 8.
なおバブリング中に発生するダストは集塵機0で回収し
、多量になれば造粒又は製回して、ホッパー(8)に戻
したり、敷滓の代用り1)として単独に使用したり、混
合して使用してもさしつかえない。The dust generated during bubbling is collected by the dust collector 0, and if it becomes large, it is granulated or recycled and returned to the hopper (8), used alone as a substitute for slag 1), or mixed. It is safe to use.
この実施例についての溶出試験結果を第8表に、路盤材
試験結果を第9表に、又破砕、磁選処理後の尾鉱中の残
留メタル割合を第10表にそれぞれ示す。The results of the elution test for this example are shown in Table 8, the results of the roadbed material test are shown in Table 9, and the percentage of residual metal in the tailings after crushing and magnetic separation is shown in Table 10.
図面は本願方法の実施例を示す説明図。 特許出願人 日本磁力選鉱株式会社 The drawings are explanatory diagrams showing an example of the method of the present application. Patent applicant: Japan Magnetic Separation Co., Ltd.
Claims (1)
泥、粘板岩、頁岩、n槍廃砂、カラミ1マサ±1高炉ス
ラグの一環以上を4〜5重量%敷滓し、溶融状a!!鯛
スラスラグれた後ランス状物により空気、Wi票あるい
は酸素を吹込み、脱硫スラグを敷滓した部会は赤泥、粘
板岩、頁岩、#物廃砂1カラミ、マサ土、高炉スラグの
一環以上を4〜5重量%、逆の場合はaWスラグを10
〜20′IR量%添加し有用地金を回収し易くすると共
にスラグの改質を行なう方法・1 to 20% by weight of desulfurization slag or 4 to 5% by weight of red mud, slate, shale, waste sand, 1 mass ± 1 part or more of blast furnace slag is poured into the casting, and the slag is melted. a! ! After the sea bream slag is slaged, air, Wi-slip or oxygen is blown in with a lance-like object, and the subcommittee that laid down the desulfurization slag is red mud, slate, shale, #waste sand, masa soil, and part or more of blast furnace slag. 4 to 5% by weight, or vice versa, 10% aW slag
A method for improving slag while making it easier to recover useful metal by adding ~20'IR amount%.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP14201181A JPS5842713A (en) | 1981-09-08 | 1981-09-08 | Treatment of desulfurized slag |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP14201181A JPS5842713A (en) | 1981-09-08 | 1981-09-08 | Treatment of desulfurized slag |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS5842713A true JPS5842713A (en) | 1983-03-12 |
Family
ID=15305295
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP14201181A Pending JPS5842713A (en) | 1981-09-08 | 1981-09-08 | Treatment of desulfurized slag |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5842713A (en) |
-
1981
- 1981-09-08 JP JP14201181A patent/JPS5842713A/en active Pending
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JPH082949A (en) | Method for modifying steelmaking slag | |
US4778523A (en) | Process for using steelmaking slag | |
KR870001567B1 (en) | Method for use steel manufacture slag | |
JPS5842713A (en) | Treatment of desulfurized slag | |
JPS625220B2 (en) | ||
Pribulová et al. | Utilization of slags from foundry process | |
JPS5842712A (en) | Treatment of desulfurizing slag | |
JPS6287443A (en) | Treatment of steel slag | |
Sviridova et al. | Development of steelmaking slag processing scheme for environmental stress reduction | |
JPS6148475A (en) | Use of steel slag | |
JPS60215704A (en) | Treatment of steel making slag | |
JPS6183876A (en) | Method of treating steel-making dephosphorized slag | |
RU2031875C1 (en) | Method of building material making | |
JPS6183877A (en) | Method of treating steel-making dephosphorized slag | |
JPS6148468A (en) | Use of steel slag | |
JPS62162657A (en) | Reformation of steel slag | |
JPS6148478A (en) | Use of steel slag | |
JPS6148471A (en) | Use of steel slag | |
JP2001151540A (en) | Production process of hard artificial aggregate | |
JPS60231445A (en) | Use of highly basic steel slag | |
JPS6148472A (en) | Use of steel slag | |
JPS61275148A (en) | Treatment of steel slag | |
JPS6136143A (en) | Treatment of steel slag | |
JPS6240325A (en) | Manufacture of binder | |
JPS6148470A (en) | Use of steel slag |