JPS63139038A - Use of dust, sludge, flue ash and slag - Google Patents

Use of dust, sludge, flue ash and slag

Info

Publication number
JPS63139038A
JPS63139038A JP61285292A JP28529286A JPS63139038A JP S63139038 A JPS63139038 A JP S63139038A JP 61285292 A JP61285292 A JP 61285292A JP 28529286 A JP28529286 A JP 28529286A JP S63139038 A JPS63139038 A JP S63139038A
Authority
JP
Japan
Prior art keywords
sludge
slag
dust
flue ash
generated
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
Application number
JP61285292A
Other languages
Japanese (ja)
Inventor
泊 正雄
松本 勝実
加峯 勝
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.)
Nippon Jiryoku Senko Co Ltd
Original Assignee
Nippon Jiryoku Senko 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 Nippon Jiryoku Senko Co Ltd filed Critical Nippon Jiryoku Senko Co Ltd
Priority to JP61285292A priority Critical patent/JPS63139038A/en
Publication of JPS63139038A publication Critical patent/JPS63139038A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B7/00Hydraulic cements
    • C04B7/24Cements from oil shales, residues or waste other than slag
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/10Production of cement, e.g. improving or optimising the production methods; Cement grinding

Abstract

(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。
(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は製鉄所から発生するダスト、スラッジのうち、
鉄分の含有量の多いものは製鉄原料として利用されてい
るが、鉄分の含有は多いものの油分や水分の付着が多い
、あるいは鉄分の含有が少ないために埋立廃棄処分され
ているダスト、スラッジ又v、 lii、 Co等の有
用金属酸化物の含有が少ないという理由で埋立廃棄処分
されている煙道灰や、木片樹皮を燃料とした乾燥炉、ボ
イラー等から発生した消炭をセメント用鉄、カルシウム
、エネルギー源として利用するものである゛。
[Detailed Description of the Invention] (Industrial Field of Application) The present invention is applicable to dust and sludge generated from steelworks.
Items with a high iron content are used as raw materials for steelmaking, but dust, sludge, and vat are disposed of in landfills because they have a high iron content but have a lot of oil and moisture attached to them, or because they have a low iron content. Flue ash, which is disposed of in landfills because it contains only a small amount of useful metal oxides such as Co, and charcoal generated from drying ovens and boilers that use wood chip bark as fuel, can be used to produce iron for cement, calcium, It is used as an energy source.

(従来の技術) 高炉から排出する高炉ダストは、浮選処理してコークス
粉を回収し他は埋立廃棄処分したり、あるいは湿式サイ
クロン法でZnは少なく鉄分に富む部分と鉄分の少ない
部分に分離し、前者は焼結原料に後者は焼却処理したり
埋立廃棄処分されている。
(Conventional technology) Blast furnace dust discharged from a blast furnace is subjected to flotation treatment to recover coke powder and the rest is disposed of in a landfill, or it is separated into iron-rich parts and iron-poor parts using a wet cyclone method. However, the former is used as raw material for sintering, and the latter is incinerated or disposed of in landfills.

酸洗処理工程で発生するスラッジ、その他の湿式処理工
程で発生する石灰中和スラッジや油分を含有するスラッ
ジのうち、鉄分の含有の多いものはロータリーキルン等
で乾燥後焼結原料にリサイクルしているが他は埋立廃棄
処分されている。
Among the sludge generated in the pickling process, lime-neutralized sludge and oil-containing sludge generated in other wet processing processes, those with high iron content are recycled into sintering raw materials after being dried in a rotary kiln, etc. However, the rest is disposed of in landfills.

オイル専焼火力発電所等で発生する煙道法は、使用する
オイルによりV、 Ni、 Coに冨む場合と殆ど含有
しない場合があり、前者は焼却後濃縮させV、 Ni、
 Co等の回収原料としているが、後者は埋立廃棄処分
されている。
The flue method used in oil-fired thermal power plants, etc. depends on the oil used, and may be rich in V, Ni, and Co, or contain very little, and the former is concentrated after incineration to produce V, Ni, and Co.
Although it is used as a recovered raw material such as Co, the latter is disposed of in a landfill.

木片樹皮を燃焼とした乾燥炉、ボイラー等から発生する
消炭も埋立廃棄処分されている。
Coal generated from drying furnaces and boilers that burn wood chip bark is also disposed of in landfills.

製鋼スラグ、脱珪スラグ、脱P−Sスラグ等は、破砕、
磁選処理して鉄粒を回収し製鉄原料にリサイクルしてい
るが、残りのスラグは膨張崩壊性を有することが多いの
で、エージング後路盤材、肥料、セメント原料等に一部
利用されているのみで大部分は埋立廃棄処分されている
Steelmaking slag, desiliconization slag, desiliconization slag, etc. are crushed,
Iron grains are collected through magnetic separation and recycled as a raw material for steelmaking, but the remaining slag often expands and disintegrates, so after aging it is only partially used for roadbed materials, fertilizers, cement raw materials, etc. The majority of waste is disposed of in landfills.

(発明が解決しようとする問題点) 上述の通り製鉄、製鋼産業から発生するダスト。(Problem that the invention attempts to solve) As mentioned above, dust generated from iron and steel manufacturing industries.

スラッジ、含油スラッジ等は、鉄分が低く  (T、F
e約50%以下) CI、 Cd、 Pb、 Zn等を
成る程度含有しているため焼結原料にリサイクルしたり
、セメントの鉄源等に利用するには問題がある。
Sludge, oil-impregnated sludge, etc. have low iron content (T, F
Since it contains a certain amount of CI, Cd, Pb, Zn, etc., it is problematic to recycle it as a sintering raw material or use it as an iron source for cement.

煙道法についても使用する燃料の種類によりV。Regarding the flue method, V depends on the type of fuel used.

Ni、 Co等の含有量は多いがSも多い場合、V、L
+Go等の含有量が少なくSが多い場合等があり、有効
利用できないという問題がある。
When the content of Ni, Co, etc. is high but S is also high, V, L
There are cases where the content of +Go etc. is small and the S content is large, so there is a problem that it cannot be used effectively.

本発明はこれらの事情に鑑みさせれたもので、ダスト、
スラッジ等は水洗、熱湯、酸処理によって不要含有物を
除去することができるし、煙道法は水洗や鉱酸々性液で
処理するとSは0.5〜0.8%と少なくなり、固定炭
素は90〜95%で約8.000KcaI/Kgの発生
量を有しており、また木片樹皮を燃料とした乾燥炉等か
ら発生する消炭は、(:d、 Pb、 7n。
The present invention was made in view of these circumstances, and it
Unnecessary substances such as sludge can be removed by washing with water, boiling water, or acid treatment, and in the flue method, when washing with water or treating with mineral acid solution, the S content is reduced to 0.5 to 0.8%, and it is fixed. Carbon is 90-95% and has a generation amount of about 8,000 KcaI/Kg, and the slaked carbon generated from a drying furnace using wood chip bark as fuel is (:d, Pb, 7n.

C1,S、 Na、O等の含有は殆どなく、固定炭素は
75〜80%で発熱量は約4,0OOKcal/Kgあ
るのでセメント原料やセメントのエネルギー源として有
効に利用できろと考えて研究を重ね本発明を完成したも
のである。
It contains almost no C1, S, Na, O, etc., has a fixed carbon content of 75-80%, and has a calorific value of approximately 4,0OOKcal/Kg, so we conducted research with the idea that it could be used effectively as a cement raw material and an energy source for cement. The present invention has been completed by repeating the above steps.

セメント原料の鉄源、 Cab、5ift源として考え
る場合、NaxOやC1の含有が多い原料でセメントを
製造、コンクリートとして使用した場合にアルカリ骨材
反応や鉄筋腐食の問題が発生したり、アンザ7ツリング
の生成等があり好ましくない。
When considering the iron source, cab, and 5ift source for cement raw materials, when cement is manufactured from raw materials containing a large amount of NaxO and C1 and used as concrete, problems such as alkali aggregate reaction and reinforcing steel corrosion may occur, and This is not preferable as it may cause the formation of

しかし、前記のダスト スラ7ジ、スラグや煙道法の場
合はNaア0に富むののは非常に少なく、上述の通り水
洗や鉱酸々性液で処理すると簡単にCI等が除去できて
セメント原料の鉄源+ Ca O+ S iOt +エ
ネルギー源として使用可能である。
However, in the case of the above-mentioned dust sludge, slag, and flue method, there is very little Na0 richness, and as mentioned above, CI etc. can be easily removed by washing with water or treating with mineral acid solution. It can be used as an iron source + Ca O + SiOt + energy source for cement raw materials.

更に製鋼、脱珪、脱P−3過程で発生するスラグは、C
ab、 FezO*+ 5i02. AIzO*tl!
lが主体であるので石灰石、粘土、珪石等と配合し、水
硬率=2.10.珪酸率=2.75.鉄率= 1.70
等と一定になるように配合しセメントを製造すると石灰
石の配合量は減少し、脱炭酸反応に要するエネルギーが
少なくなる。
Furthermore, the slag generated during the steelmaking, desiliconization, and P-3 processes is C
ab, FezO*+ 5i02. AIzO*tl!
Since l is the main component, it is mixed with limestone, clay, silica stone, etc., and the hydraulic ratio is 2.10. Silicic acid rate=2.75. Iron rate = 1.70
If cement is manufactured by mixing limestone at a constant level, the amount of limestone added will decrease, and the energy required for the decarboxylation reaction will decrease.

上記のダスト、スラッジ、煙道灰、消炭、スラグを適当
に混合すると乾燥微粉の飛散防止となり、又水分が多過
ぎるものは適量となり、スラグから溶出するCaイオン
はCa (OH) zとなり、更に空気中からCOzを
吸収してCaCO5が生成し固化し取り扱いやすくなり
、産業廃棄物をセメントのCab、 FetOs+Si
Oア、Altos、エネルギー源として有効に利用でき
る。
Properly mixing the above dust, sludge, flue ash, charcoal, and slag will prevent the dry fine powder from scattering, and if there is too much moisture, the amount of moisture will be adjusted to the appropriate amount, and Ca ions eluted from the slag will become Ca (OH) z, and further It absorbs COz from the air and produces CaCO5, which solidifies and becomes easier to handle.
Altos can be effectively used as an energy source.

(問題を解決するための手段) 本発明は上記の問題点を解決しダスト、スラッジ、煙道
灰、消炭、スラグ等の有効利用の道を拓くものでその要
旨とするところは、製鉄所から発生する集じんダスト、
スラ7ジ、オイル燃焼炉から発生する煙道灰、木片樹皮
を燃料とした炉から発生する消炭、含油スラッジ、酸洗
スラッジ、製鋼スラグの二種以上を混合しセメント原料
として利用することを特徴とするダスト、スラッジ、煙
道圧、スラグの利用方法である。
(Means for Solving the Problems) The present invention solves the above problems and opens the way to the effective use of dust, sludge, flue ash, charcoal, slag, etc. generated dust,
It is characterized by mixing two or more types of sludge, flue ash generated from an oil-burning furnace, charcoal generated from a furnace using wood chip bark as fuel, oil-containing sludge, pickling sludge, and steelmaking slag and using it as a raw material for cement. This is how dust, sludge, flue pressure, and slag are used.

上記の発明において、集じんダスト、スラッジ。In the above invention, collected dust and sludge.

煙道灰が水洗又は鉱酸々性液で洗浄処理を行ったもので
あり、スラグは製鋼スラグ、脱P−Sスラグであること
を特徴としており、又集じんダスト。
The flue ash is washed with water or a mineral acid solution, and the slag is steelmaking slag or P-S-free slag, and the dust is collected.

スラッジに硫酸第1鉄または塩化第1鉄を添加して使用
することもある。
Ferrous sulfate or ferrous chloride may also be added to the sludge.

(実施例及び作用) 以下、本発明の作用効果をbv t=するために行った
実施例及び結果を示す。実験に用いたダスト。
(Examples and Effects) Examples and results carried out in order to demonstrate the effects of the present invention to bv t will be shown below. Dust used in the experiment.

スラッジ、煙道灰、消炭、スラグの化学分析値を第1表
に、水洗、鉱酸ケ性液等でパルプ濃度30%にてスター
ラーで15.30分間と処理時間を変えて処理し、ブフ
ナーロートで脱水した。しかし、鉱酸々性液で処理した
場合は、更にサンプル量と同重量の水で洗浄した。これ
等は時間を変えても殆ど差がないので、15分間処理し
た分析値を第2表に示す。
The chemical analysis values of sludge, flue ash, slaked coal, and slag are shown in Table 1. They were washed with water, treated with a mineral acidic solution, etc. at a pulp concentration of 30%, and treated with a stirrer for 15.30 minutes for different treatment times. Dehydrated using a funnel. However, when treated with mineral acidic solution, the sample was further washed with water of the same weight as the sample amount. Since there is almost no difference in these values even if the time is changed, Table 2 shows the analytical values obtained after processing for 15 minutes.

以上の結果、CI、 Zn、 Pb、 Cd等をかなり
の量含有しセメント原料として好ましくない場合は、水
洗、熱湯洗浄あるいは鉱酸?8液で約15分間処理する
と簡単に除去できる。
As a result of the above, if the material contains a considerable amount of CI, Zn, Pb, Cd, etc. and is undesirable as a cement raw material, it should be washed with water, hot water, or mineral acid. It can be easily removed by treating with 8 liquids for about 15 minutes.

しかし、これらのダスト、スラッジ等は非常に微細なこ
とが多く乾燥すると粉塵の発生源となって飛散するのが
、スラグと混合するとスラグから溶出するCaイオンか
らCa (01り !となり、更に空気中からCO2を
吸収しCaC0*となるので硬化し粉塵の発生を防止で
きる。これらの混合原料を石灰石。
However, these dusts, sludges, etc. are often very fine and when dried, they become a source of dust and scatter.When mixed with slag, Ca ions eluted from the slag become Ca(01ri!), which further releases air into the air. It absorbs CO2 from inside and becomes CaCO*, which hardens and prevents the generation of dust.The mixed raw material is limestone.

珪石、粘土等と混合し試験ボールミルでプレーン値約3
,0OOcd/gに粉砕し水を加えて練り約10〜15
φ1のペレットとし、1,450℃に保持したエレマ電
気炉で白金皿に入れて30分間焼成し、炉外で空冷後試
作タリンカーとし、三水石膏を4%添加し試験用ボール
ミルでプレーン値約3,150−/gに粉砕しJIS法
に沿ってJISモルタル(4X 4 X16mm)を作
りセメント強度を測定した結果を第3表に示す。
Mixed with silica stone, clay, etc., the plain value was approximately 3 in a test ball mill.
,000cd/g, add water and knead about 10-15
Pellets of φ1 were made into pellets, placed in a platinum plate in an Elema electric furnace maintained at 1,450°C, fired for 30 minutes, cooled in air outside the furnace, and then made into a prototype Talinker. 4% gypsum trihydrate was added, and a test ball mill was used to reduce the plain value to approx. Table 3 shows the results of pulverizing to 3,150-/g, making JIS mortar (4 x 4 x 16 mm) according to the JIS method, and measuring the cement strength.

なお、セメント原料の計算は水硬率−2,10,珪酸率
=2.75.鉄率=1.75.門go=2.0となる様
に、通常のセメント原料である石灰石、珪石、粘土。
In addition, the calculation of the cement raw material is as follows: hydraulic ratio -2.10, silicic acid ratio = 2.75. Iron rate = 1.75. Limestone, silica stone, and clay, which are normal cement raw materials, have a gate go of 2.0.

カラミ、蛇紋岩を使用した場合をNo、1、石灰石。No. 1, limestone when using karami and serpentine.

珪石、粘土と製鋼スラグ(スラグ■)、ダスト■1ダス
ト■を使用した場合をNo、2、石灰石、珪石。
No. 2, limestone, silica stone when using silica stone, clay, steelmaking slag (slag ■), dust ■1 dust ■.

粘土と製鋼スラグ(スラグ■)、脱P−Sスラグ(スラ
グ■)、ダスト■の水洗物、スラフジ■、ダスト■、煙
道灰■を使用した場合をNo、3とし、試作原料及び試
作タリンカーとした。
Cases using clay, steelmaking slag (slag ■), de-P-S slag (slag ■), washing of dust ■, sloughji ■, dust ■, and flue ash ■ are designated as No. 3, and prototype raw materials and prototype tallincar. And so.

なお、ダスト■は環境庁公示方法による溶出試験方法に
よればCr’°イオンを0.0I P、P、M?8出す
るが、硫酸第1鉄又は塩化第1鉄を0.1%添加し散水
後混合すると溶出防止を行い得る。そこで、石灰石、珪
石、粘土と脱P−Sスラグ(スラグ■)。
According to the elution test method published by the Environment Agency, dust ■ contains 0.0I P, P, M? of Cr'° ions. However, if 0.1% of ferrous sulfate or ferrous chloride is added and mixed after watering, elution can be prevented. Therefore, limestone, silica stone, clay and P-S-free slag (slag ■).

ダスト■の硫酸第1鉄0.1%添加処理物、スラッジ■
、ダスト■を使用した場合をNo、4とし試作原料及び
試作タリンカーとした。
Dust■ treated with 0.1% ferrous sulfate, sludge■
, the case where Dust ■ was used was designated as No. 4, and was used as a trial raw material and a trial production Talinker.

以上述べた如く、産業廃棄物として埋立廃棄処分されて
いたダスト スラッジ等をスラグと混合使用することに
より、セメントの強度は殆ど変わらずセメント原料とし
て有効に利用できることがわかる。
As mentioned above, it can be seen that by mixing dust sludge, etc., which had been disposed of as industrial waste in a landfill, with slag, it can be effectively used as a raw material for cement, with almost no change in the strength of cement.

又、煙道灰、高炉ダスト、消炭等Cを含有するものを配
合したが発熱量としては約3+500〜8,000Kc
al/Kgを有しているにもかかわらず、実験用電気炉
であるため熱量の減少は! 認されなかった。
In addition, materials containing C such as flue ash, blast furnace dust, and slaked coal were mixed, but the calorific value was approximately 3+500 to 8,000 Kc.
Although it has al/Kg, the amount of heat decreases because it is an experimental electric furnace! Not approved.

しかし、セメント製造会社に於いてはエネルギーの削減
を目的に炭質頁岩や廃タイヤ等も利用されているし、そ
の効果は実際のロータリーキルンで行うと有効であると
思う。なお、煙道灰、消炭等はセメント原料に混合して
使用するのみでなく、サスペンションプレヒーター装置
の最下段付近に於いて微粉炭やオイル等を燃焼として吹
き込んでいる装置から吹き込んで(供給)もその効果が
あるのでどちらで使用しても良い。
However, carbonaceous shale and waste tires are also used by cement manufacturing companies to reduce energy consumption, and I think this would be effective if done in an actual rotary kiln. In addition, flue ash, extinguished coal, etc. are not only mixed with cement raw materials and used, but also blown (supplied) from a device near the bottom of the suspension preheater device that blows pulverized coal, oil, etc. as combustion. Both have the same effect, so you can use either one.

(発明の効果) 以上の如く製鉄産業等から発生し、製鉄原料としてリサ
イクルするには鉄分の含有が少なかったり油分を含有し
ていて問題があり、産業廃棄物として埋立廃棄処分され
ているダスト、スラッジ。
(Effects of the invention) As described above, dust generated from the steel industry, etc., has problems because it contains too little iron or contains oil to be recycled as a raw material for steel production, and is disposed of in landfills as industrial waste. Sludge.

スラグ或いは発電所等から発生する煙道灰で有価金属の
酸化物等の含有が少ないため埋立廃棄処分されているも
のをエネルギー源として、そのまま或いは水洗又は鉱酸
々性液等で洗浄処理を行うことで、セメントに対して好
ましくないC1,Pb、 Zn等を除去し、かつZn、
 Pb、 Cd等を用物は水酸化物等として回収し、残
渣はセメント原料として有効利用することで有限の石灰
石、珪石等の資源の延命利用ができる。
Slag or flue ash generated from power plants, etc., which is disposed of in landfills due to its low content of valuable metal oxides, can be used as an energy source, or it can be washed with water or cleaned with mineral acid solution. By doing this, C1, Pb, Zn, etc. which are undesirable for cement are removed, and Zn,
By recovering Pb, Cd, etc. as hydroxides, etc., and effectively using the residue as a raw material for cement, it is possible to extend the life of limited resources such as limestone and silica stone.

Claims (1)

【特許請求の範囲】 1、製鉄所から発生する集じんダスト、スラッジ、オイ
ル燃焼炉から発生する煙道灰、木片樹皮を燃料とした炉
から発生する消炭、含油スラッジ、酸洗スラッジ、製鋼
スラグの二種以上を混合しセメント原料として利用する
ことを特徴とするダスト、スラッジ、煙道灰、スラグの
利用方法。 2、特許請求の範囲第1項において、集じんダスト、ス
ラッジ、煙道灰が水洗又は鉱酸々性液で洗浄処理を行っ
たものであることを特徴とするダスト、スラッジ、煙道
灰、スラグの利用方法。 3、特許請求の範囲第1項において、含油スラッジが鉄
分を含有するものであることを特徴とするダスト、スラ
ッジ、煙道灰、スラグの利用方法。 4、特許請求の範囲第1項において、スラグが製鋼スラ
グ又は脱P・Sスラグであることを特徴とするダスト、
スラッジ、煙道灰、スラグの利用方法。 5、特許請求の範囲第1項において、集じんダスト、ス
ラッジが硫酸第1鉄又は塩化第1鉄を添加したものであ
ることを特徴とするダスト、スラッジ、煙道灰、スラグ
の利用方法。
[Claims] 1. Dust and sludge generated from steel mills, flue ash generated from oil-burning furnaces, charcoal generated from furnaces using wood chip bark as fuel, oil-impregnated sludge, pickling sludge, and steelmaking slag A method of utilizing dust, sludge, flue ash, and slag, characterized by mixing two or more of the following and using the mixture as a raw material for cement. 2. The dust, sludge, and flue ash set forth in claim 1, characterized in that the collected dust, sludge, and flue ash have been washed with water or washed with a mineral acid solution; How to use slag. 3. A method of utilizing dust, sludge, flue ash, and slag according to claim 1, wherein the oil-impregnated sludge contains iron. 4. The dust according to claim 1, wherein the slag is steelmaking slag or P/S-free slag;
How to use sludge, flue ash and slag. 5. A method of utilizing dust, sludge, flue ash, and slag according to claim 1, characterized in that the collected dust and sludge contain ferrous sulfate or ferrous chloride.
JP61285292A 1986-11-28 1986-11-28 Use of dust, sludge, flue ash and slag Pending JPS63139038A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61285292A JPS63139038A (en) 1986-11-28 1986-11-28 Use of dust, sludge, flue ash and slag

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61285292A JPS63139038A (en) 1986-11-28 1986-11-28 Use of dust, sludge, flue ash and slag

Publications (1)

Publication Number Publication Date
JPS63139038A true JPS63139038A (en) 1988-06-10

Family

ID=17689633

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61285292A Pending JPS63139038A (en) 1986-11-28 1986-11-28 Use of dust, sludge, flue ash and slag

Country Status (1)

Country Link
JP (1) JPS63139038A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001302293A (en) * 2000-04-18 2001-10-31 Tsukishima Kikai Co Ltd Method of treating waste
WO2003045868A1 (en) * 2001-11-29 2003-06-05 Duna-Dráva Cement Kft. Additive mixture for cement clinker production and its use
JPWO2006098202A1 (en) * 2005-03-16 2008-08-21 太平洋セメント株式会社 Fired product

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001302293A (en) * 2000-04-18 2001-10-31 Tsukishima Kikai Co Ltd Method of treating waste
WO2003045868A1 (en) * 2001-11-29 2003-06-05 Duna-Dráva Cement Kft. Additive mixture for cement clinker production and its use
JPWO2006098202A1 (en) * 2005-03-16 2008-08-21 太平洋セメント株式会社 Fired product

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