JPS58210846A - Method for producing moisture absorbent and adsorbent from slag or slag and coal ash, shale or calcium silicate - Google Patents

Method for producing moisture absorbent and adsorbent from slag or slag and coal ash, shale or calcium silicate

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Publication number
JPS58210846A
JPS58210846A JP57095261A JP9526182A JPS58210846A JP S58210846 A JPS58210846 A JP S58210846A JP 57095261 A JP57095261 A JP 57095261A JP 9526182 A JP9526182 A JP 9526182A JP S58210846 A JPS58210846 A JP S58210846A
Authority
JP
Japan
Prior art keywords
slag
shale
calcium silicate
adsorbent
coal ash
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
JP57095261A
Other languages
Japanese (ja)
Other versions
JPH0417088B2 (en
Inventor
Masao Tomari
泊 正雄
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 JP57095261A priority Critical patent/JPS58210846A/en
Publication of JPS58210846A publication Critical patent/JPS58210846A/en
Publication of JPH0417088B2 publication Critical patent/JPH0417088B2/ja
Granted legal-status Critical Current

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  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PURPOSE:To produce a moisture absorbent and adsorbent from industrial waste, by gelling a raw material consisting essentially of slag with addition of inorg. acids and further adding a basic raw material to make the gel alkaline in pH and subjecting the resulted sediment to filtering, washing and drying. CONSTITUTION:Industrial waste such as blast furnace slag or electric furnace slag alone or under addition of coal ash, shale, calcium silicate, etc. is pulverized. Inorg. acid such as hydrochloric acid, sulfuric acid, nitric acid or the like is added to the same to form a gel. A basic raw material such as an aq. alkaline soln. obtd. by eluting the slag produced when molten iron or the like is desulfurized with soda ash or an aq. NaOH soln. is added to the gel under stirring to regulate the pH to 8.5-10.0. The sediment deposited in this stage is filtered and washed and is then dried, whereby a moisture absorbent and adsorbent is produced.

Description

【発明の詳細な説明】 頁岩,珪酸カルシウム板を有効利用し,吸湿、吸着剤の
製造に関するものであり、詳しくは高炉スラグ(水滓、
除冷スラグ)、転炉スラグ,WL気炉スラグ(酸化期,
還元期)、造塊スラグ等のスラグ単味又は石炭灰、頁岩
、珪酸カルシウムを添加したスラグを無機酸水溶液で溶
解(ゲル化)させ、ソーダ灰脱硫スラグから溶出したア
ルカリ水溶液( Naイオンが主体でStow,鳩OH
, Sイオンを含む)又は水酸化ナトリウム液等の塩基
性物を添加しながら攪拌し、pHを約8.5〜10.0
にあげ析出した沈殿物を濾過水洗し乾燥させ吸湿、吸着
剤を合成することである。
[Detailed description of the invention] This invention relates to the production of moisture absorption and adsorption agents by effectively utilizing shale and calcium silicate plates.
slowly cooled slag), converter slag, WL air furnace slag (oxidation stage,
During the reduction stage), slag alone such as agglomerated slag or slag added with coal ash, shale, or calcium silicate is dissolved (gelled) in an inorganic acid aqueous solution, and an alkaline aqueous solution (mainly Na ions) eluted from the soda ash desulfurization slag is created. Stow, pigeon OH
, containing S ions) or a basic substance such as sodium hydroxide solution, and adjust the pH to approximately 8.5 to 10.0.
The precipitate is filtered, washed with water, and dried to absorb moisture and synthesize an adsorbent.

製鉄所から発生するスラグは莫大な量で、高炉スラグは
水滓(急冷物)と除冷スラグ(畑滓)に大別され、前者
はガラス主体のため潜在水硬性を有するので高炉セメン
トの混和物や人工砂に、後者はメリライト主体のため潜
在水硬性を殆んど有しないので路盤材や骨材に利用され
ている′が未利用で埋立材とされているものも相当鼠で
ある。
A huge amount of slag is generated from steelworks, and blast furnace slag is roughly divided into water slag (quenched slag) and slowly cooled slag (field slag).The former is mainly glass and has latent hydraulic properties, so it cannot be mixed with blast furnace cement. The latter is mainly composed of melilite and has almost no latent hydraulic properties, so it is used for roadbed materials and aggregates, but there are also many unused materials and artificial sands that are used as landfill materials.

又製鋼の過程で発生する転炉スラグはγ−2Cso・S
in、、F@CaO(遊離石灰)を主体に2caO,F
e、03.4CaO”A%0.−Fe、O,、F、Mg
0(遊離マグネ、シア)を含有しているので膨張崩壊性
を有するので改質しなければ路盤材等に有効利用されず
、ごく一部珪鉄肥料、セメント原料に利用されているの
みで大部分は埋立廃棄されている。
In addition, converter slag generated during the steelmaking process is γ-2Cso・S.
in,, F@CaO (free lime) as the main component, 2caO,F
e, 03.4CaO"A%0.-Fe, O,, F, Mg
Since it contains 0 (free magne, shea), it has expansion and disintegration properties, so it cannot be used effectively for roadbed materials, etc. unless it is modified, and only a small portion is used as silica fertilizer and cement raw material. Parts are being disposed of in landfills.

同様に電気炉から発生する酸化期スラグは2CaO・A
z、o、、sio、、2Ca O* F 62 o、、
4CaO−A40.− Fe、O8主体でr−2CaO
@SiO,、F−Cooは少なイ+7)テ大部分は路盤
材として利用されているが他は埋立廃棄されている。
Similarly, the oxidation stage slag generated from the electric furnace is 2CaO・A
z, o,, sio,, 2Ca O* F 62 o,,
4CaO-A40. - Mainly Fe, O8 and r-2CaO
@SiO,, F-Coo is small A+7) Most of it is used as roadbed material, but the rest is disposed of in landfills.

還元期スラグは2CaO・S * 02又は3CaO・
2 S * OH主体あため冷却の過程でダスティング
を起し殆んど全部崩壊し埋立廃棄されている。
The reduction stage slag is 2CaO・S*02 or 3CaO・
2 S * OH mainly causes dusting during the cooling process, and almost all of it disintegrates and is disposed of in a landfill.

造塊スラグも還元期スラグと同様にγ−2CaO・Si
n。
Like the reduction stage slag, the agglomerated slag also contains γ-2CaO・Si.
n.

主体でp’@caoに富むので冷却の過程でダスティン
グを起して崩壊する場合が多いので埋立廃棄されている
Since it is mainly rich in p'@cao, it often causes dusting and collapses during the cooling process, so it is disposed of in landfills.

石炭灰は石炭火力発電所からフライアッシュ。Coal ash is fly ash from coal-fired power plants.

ボトム7ツシユ、シンダーアッシュとの名称で発生し、
フライアッシーは殆んどセメント混和材に利用されてい
るが、ボトムアッシュ等は肥料や軽蓋骨材、路盤材等へ
の有効利用の研究も行なわれているが大部分は埋立廃棄
されている。
It occurs under the name Bottom 7 Tsushiyu, Cinder Ash,
Most fly assemblies are used as cement admixtures, but research is being conducted on the effective use of bottom ash as fertilizer, light aggregate, roadbed material, etc., but most of it is disposed of in landfills. .

頁岩は日本各地に広く賦存し、粘土鉱物のカオリナイト
やモンモリロナイト等を含有した未利用資源である。
Shale is an unused resource that exists widely throughout Japan and contains clay minerals such as kaolinite and montmorillonite.

本発明で珪酸カルシウム原として使う珪酸カルシウム板
は珪石、石灰を徽粉砕して配合しオートクレーブ処理し
て製造されているが、その製造過程で破損したりした不
合格品で主成分鉱物はゾノライト、トベルiライト等か
らなっている産業廃棄物である。
The calcium silicate plate used as the calcium silicate raw material in the present invention is manufactured by crushing and blending silica stone and lime and treating it in an autoclave.However, it is a rejected product that was damaged during the manufacturing process and the main minerals are zonolite, This is industrial waste consisting of Tobel i-light and other materials.

なお、ソーダ灰脱硫スラグは溶銑中に含有する8分を取
り除くため炭酸ソーダを投入しなからN。
Note that soda ash desulfurization slag does not require adding soda carbonate to remove the 8% content in the hot metal.

ガス等を吹き込んでバブリングを行ないNa、 Sとし
てスラグに移行させたスラグでNanoに富み(Nat
O約12〜601に量S)時には未反応のNaff1C
OBも含まれているので、水に接するとNmイオンの他
Sin、。
The slag is rich in Nano (Nat
Sometimes unreacted Naff1C
Since it also contains OB, when it comes into contact with water, it produces Nm ions as well as Sin.

A/、0.、Sイオン等を溶出しpHも高くメタル回収
後の尾鉱処理も大変である。
A/, 0. , S ions, etc. are eluted and the pH is high, making it difficult to treat the tailings after metal recovery.

そCで仁れ等のスラグ、石炭灰1頁岩、珪酸カルシウム
板を有効利用することを研究し吸湿、吸着剤の製造に成
功した。
At SoC, we researched the effective use of slag, coal ash 1 shale, and calcium silicate plates, and succeeded in producing a moisture absorbent and adsorbent.

高炉スラグ(水滓)、電気炉スラグ(還元期) 1.t
Sin、 、Cab、 At、0. 等に富みアルカリ
溶液で約60〜100℃で6〜6時間処理するとゲル化
するが、他の高炉除冷スラグ、転炉スラグ、造塊スラグ
、酸化期スラグ、石炭灰1頁岩、珪酸カルシウム板はカ
シなり長時間アルカリ液で処理してもゲル化しなtl)
Blast furnace slag (water slag), electric furnace slag (reduction stage) 1. t
Sin, ,Cab, At, 0. etc., and gels when treated with an alkaline solution at about 60 to 100°C for 6 to 6 hours, but other cooled blast furnace slag, converter slag, agglomerated slag, oxidation stage slag, coal ash 1 shale, calcium silicate plate It is hard and does not gel even if treated with alkaline solution for a long time)
.

前述のスラグを約2−以下に粗砕(ダスティングを起し
たスラグ、高炉水滓はそのまま)シ、磁選処理を行ない
、その尾鉱を更に1−以下に粉砕し、塩酸、硫酸、硝酸
等の無89酸を添加すると高炉水滓、電気炉スラグ(還
元期)は激しく Co、ガスを発生しながら反応し瞬間
的にゲル化して膨潤し約100℃に達しpHは約1〜2
となる。
The above-mentioned slag is crushed to a size of about 2 or less (dusting slag and blast furnace water slag are left as is), subjected to magnetic separation treatment, and the tailings are further crushed to a size of about 1 or less and treated with hydrochloric acid, sulfuric acid, nitric acid, etc. When 89 acid-free is added, blast furnace water slag and electric furnace slag (in the reduction stage) react violently while generating Co and gas, instantaneously gel and swell, reaching a temperature of about 100°C and a pH of about 1 to 2.
becomes.

又他のスラグ、石炭灰、頁岩、珪酸カルシウム板は上記
の反応は殆んど生起しないので反応促進剤的に高炉水滓
又は還元期スラグを10%以上配上記塩酸、硫酸、硝酸
等の無機酸を添加すると激しく反応し瞬間的にゲル化し
て膨潤し約、100℃優ζ達しpHは約1〜2となる。
In addition, since the above reaction hardly occurs with other slags, coal ash, shale, and calcium silicate plates, 10% or more of blast furnace water slag or reduction phase slag is used as a reaction accelerator. When an acid is added, it reacts violently and instantaneously gels and swells, reaching approximately 100°C and a pH of approximately 1 to 2.

これらにソーダ灰脱硫スラグからの溶出液(Nail溶
液でもよい)を攪拌しながら添加しpHを約85〜10
まで上昇させ加水分解反応を起させ、生成した沈殿物を
一過、水洗し乾燥させると高炉スラグ。
The eluate from the soda ash desulfurization slag (Nail solution may also be used) is added to these with stirring to adjust the pH to approximately 85-10.
The resulting precipitate is temporarily washed with water and dried to produce blast furnace slag.

還元期スラグ、造塊スラグ、石炭灰、頁岩、珪酸カルシ
ウム主体物からは白色の、転炉スラグ、酸死期スラグか
らは渋茶褐色の吸湿、吸着剤が生成する。
White hygroscopic and adsorbent substances are produced from reduction phase slag, agglomeration slag, coal ash, shale, and calcium silicate substances, and dark brown moisture absorption and adsorption agents are produced from converter slag and acid death phase slag.

以下本願方法の作用効果を確認するために行なった試験
及びその結果を示す。
Tests conducted to confirm the effects of the present method and their results are shown below.

〈試験方法〉 転炉スラグ、酸化期スラグ、高炉除冷スラグ。<Test method> Converter slag, oxidation stage slag, blast furnace slow cooling slag.

造塊スラグは約2!1m以下に粗砕して、磁選処理を行
ない、尾鉱のみを約1m以下に粉砕した。
The agglomerated slag was coarsely crushed to about 2!1 m or less and subjected to magnetic separation treatment, and only the tailings were crushed to about 1 m or less.

高炉水滓、還元期スラグはそのままの粒層で磁選処理を
行ない、尾鉱のみを約1m以下に粉砕した。
Blast furnace water slag and reduction phase slag were subjected to magnetic separation treatment using the grain layer as they were, and only the tailings were pulverized to a size of approximately 1 m or less.

石炭灰、頁岩、珪酸カルシウム($1!造過程で破損し
たりした珪酸カルシウム板の不合格品)はそのまま1−
以下に粉砕して試料とした。
Coal ash, shale, calcium silicate ($1! Rejected calcium silicate plates that were damaged during the manufacturing process) are 1-
It was pulverized and used as a sample.

又、ソーダ灰説硫スラグを約2−以下に粗砕機磁選処理
を行ない1尾鉱をバルブ濃度50九で溶出して得た溶出
水に更に新しい尾鉱をバルブ濃度50Sとなるべく添加
し溶出するという事を3回繰返を中和用に使用した。使
用したスラグ、石炭灰、頁岩、珪酸カルシウムの化学分
析値を11表に、性状を第2表に、ソーダ灰説硫スラグ
の溶出水を第3表にそれぞれ示す。
In addition, the soda ash theory sulfur slag is subjected to a coarse crusher magnetic separation treatment to reduce the sulfur slag to about 2 - or less, and 1 tailings are eluted at a bulb concentration of 509. To the eluted water obtained, new tailings are added to the bulb concentration of 50 S as much as possible and eluted. This was repeated three times and used for neutralization. The chemical analysis values of the slag, coal ash, shale, and calcium silicate used are shown in Table 11, the properties are shown in Table 2, and the leached water of the soda ash theory sulfur slag is shown in Table 3.

前述のスラグ試料を2000CCのビーカーに200 
f秤り取って、純水300 CCを添加して攪拌しなが
らHCt(30九濃度)を250−300CC、E、8
04(1: 1 )を200〜250ccあるいはHN
O,(1: 1 )を250CC添加すると炭酸ガスを
発生しながら発熱し約1oo℃となり、瞬間的にゲル化
して膨潤しpHは約1〜2となる。
The slag sample mentioned above was placed in a 2000CC beaker.
Weigh out f, add 300 cc of pure water, and add 250-300 cc of HCt (309 concentration), E, 8 while stirring.
04 (1: 1) to 200-250cc or HN
When 250 cc of O, (1:1) is added, heat is generated while generating carbon dioxide gas, and the temperature reaches about 100° C., which instantly gels and swells, and the pH becomes about 1 to 2.

この溶液にソーダ灰脱硫スラグから溶出した溶液を約5
00cc、あるいは水酸化ナトリウム溶[(AN)を約
、500 CC添加すると白色沈殿物が生成し、ゲル物
と一緒に濾過後水洗し恒温乾燥器(105〜110℃)
で乾燥′すると軽量の粉体物となる。
Add about 50% of the solution eluted from the soda ash desulfurization slag to this solution.
When approximately 500 cc of sodium hydroxide solution (AN) is added, a white precipitate is formed, which is filtered together with the gel, washed with water, and dried in a constant temperature dryer (105-110°C).
When dried, it becomes a lightweight powder.

この場合、前述した通り転炉スラグ、酸化期スラグ、造
塊スラグ、頁岩、石炭灰、珪酸カルシウム板は単味で酸
処理しても瞬間的にゲル化しないが、反応促進剤的に高
炉水滓又は還元期スラグを10九以上混合し酸処理を行
なうと瞬間的にゲル化する。
In this case, as mentioned above, converter slag, oxidation stage slag, agglomeration slag, shale, coal ash, and calcium silicate plates do not gel instantly even if they are treated with acid alone, but blast furnace water is a reaction accelerator. When 10 or more slags or reducing stage slags are mixed and treated with acid, they instantly gel.

又、用いる塩基性物は例えばNaOH溶液を使用しても
良いが、前述した如くソーダ灰脱硫スラグの溶出水はN
lイオンのはかSin、 、 Al40.イオンも溶出
し、一種の水ガラス状物も含有しているので、Na1l
溶液を使用するより生成物が多量に生成するし、産業廃
棄物を有効利用できるので特許請求の範囲第2項記載の
発明の方が有効である。
In addition, the basic substance used may be, for example, NaOH solution, but as mentioned above, the eluted water of soda ash desulfurization slag is N
The weight of l ions is Sin, , Al40. Ions are also eluted and it also contains a kind of water glass, so Na1L
The invention recited in claim 2 is more effective because a larger amount of product is produced than when a solution is used, and industrial waste can be used more effectively.

又、ソーダ灰脱硫スラグからの溶出水、NaOH溶液、
HC/−%H,804、HNO3の溶液は濃度が濃いと
少量で良く、淡いと多量使用する必要がある。
In addition, elution water from soda ash desulfurization slag, NaOH solution,
When the concentration of HC/-%H, 804, HNO3 solution is high, a small amount is required, and when the concentration is low, a large amount needs to be used.

使用原料と鉱酸、アルカリ溶液の使用製と生成物lを第
4表に、生成物の性状を第5表にそれぞれ示す。
Table 4 shows the raw materials used, mineral acids and alkali solutions used, and the product l, and Table 5 shows the properties of the product.

なおこの処理方法での生成物は非晶質でX線回折でも結
晶鉱物のピークが現われないのが合成ゼオライトと異な
っている。
The product produced by this treatment method is different from synthetic zeolite in that it is amorphous and no crystalline mineral peaks appear in X-ray diffraction.

又、比表面積は非常に大きく合成ゼオライトの4A型と
同等か若干大きいし、吸湿能力(その物の重量に対する
吸湿物のllmN)も合成ゼオライト4A型と同等か若
干大きい。その結果の一部を第6表に示す。
In addition, the specific surface area is very large, the same as or slightly larger than that of synthetic zeolite type 4A, and the moisture absorption capacity (llmN of the hygroscopic material relative to the weight of the material) is also equal to or slightly larger than that of synthetic zeolite type 4A. Some of the results are shown in Table 6.

又、スラグ等を鉱酸処理後アルカリ溶液で処理した生成
物の数例の化学分析錬を第7表に示す。
Further, Table 7 shows chemical analyzes of several examples of products obtained by treating slag and the like with mineral acids and then treating them with alkaline solutions.

第    5    表 以上述べて釆た如く、現状ではまだまだ未利用資源であ
ったり産業廃棄物であるスラグ、石炭灰、頁岩や珪酸カ
ルシウム析を原料として容易に吸湿剤や段着剤を製造出
来るし、その製品は1合成ゼオライトの代替品として例
えば石鹸原料その他の吸着剤や吸湿剤として広く利用可
能である。
Table 5 As stated above, moisture absorbents and tiering agents can be easily manufactured using raw materials such as slag, coal ash, shale, and calcium silicate, which are currently still unused resources or industrial waste. The product can be widely used as a substitute for 1 synthetic zeolite, for example as an adsorbent or moisture absorbent for soap raw materials, etc.

特許出願人  日本磁力選鉱株式会社 代  理  人   有  吉  教  晴231−Patent applicant: Japan Magnetic Separation Co., Ltd. 231 Yoshi Kyo Haru who has a background

Claims (1)

【特許請求の範囲】 1、 スラグ又はスラグに石炭灰、頁岩、珪酸カルシウ
ムを混合したものを無機酸水溶液にてゲル化したゲル状
物に、塩基性物を上記ゲル状物がアルカリ性となる量添
加し、この際の析出沈殿物を濾過水洗後乾燥することを
特徴とするスラグ又はスラグに石炭灰1頁岩、珪酸カル
シウムを混合したものから吸湿、吸着剤を製造する方法
。 2、特許請求の範囲第1項記載の方法において塩基性物
がソーダ灰脱硫スラグから溶出したアルカリ性溶液であ
ること゛を特徴とするスラグ又はスラグに石炭灰、頁岩
、珪酸カルシウムを混合したものから吸湿、吸着剤を製
造する方法。
[Claims] 1. Adding a basic substance to a gel-like substance obtained by gelling slag or a mixture of slag with coal ash, shale, and calcium silicate with an aqueous inorganic acid solution in an amount that makes the gel-like substance alkaline. A method for producing a moisture absorbent and adsorbent from slag or a mixture of coal ash, shale, and calcium silicate, characterized by adding the precipitate at this time, filtering and washing with water, and then drying. 2. Moisture absorption from slag or a mixture of slag and coal ash, shale, and calcium silicate, characterized in that the basic substance is an alkaline solution eluted from soda ash desulfurization slag in the method described in claim 1. , a method of producing an adsorbent.
JP57095261A 1982-06-02 1982-06-02 Method for producing moisture absorbent and adsorbent from slag or slag and coal ash, shale or calcium silicate Granted JPS58210846A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57095261A JPS58210846A (en) 1982-06-02 1982-06-02 Method for producing moisture absorbent and adsorbent from slag or slag and coal ash, shale or calcium silicate

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57095261A JPS58210846A (en) 1982-06-02 1982-06-02 Method for producing moisture absorbent and adsorbent from slag or slag and coal ash, shale or calcium silicate

Publications (2)

Publication Number Publication Date
JPS58210846A true JPS58210846A (en) 1983-12-08
JPH0417088B2 JPH0417088B2 (en) 1992-03-25

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JP57095261A Granted JPS58210846A (en) 1982-06-02 1982-06-02 Method for producing moisture absorbent and adsorbent from slag or slag and coal ash, shale or calcium silicate

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02293045A (en) * 1989-05-09 1990-12-04 Nippon Steel Corp Production of deodorant
US6132594A (en) * 1998-04-15 2000-10-17 Nippon Mitsubishi Oil Corp. Hydrocracking catalyst and hydrocracking method for hydrocarbon oils
KR20110061558A (en) * 2008-08-28 2011-06-09 오리카 익스플로시브스 테크놀로지 피티와이 리미티드 Improved integrated chemical process
CN109364872A (en) * 2018-11-19 2019-02-22 常熟理工学院 A kind of preparation method of sulfenyl cover type basic clinker adsorbent

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114014423A (en) * 2015-06-11 2022-02-08 大竹久夫 System for recovering phosphorus in water to be treated, method for recovering phosphorus in water to be treated, fertilizer raw material, and yellow phosphorus raw material

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS49122889A (en) * 1973-03-29 1974-11-25
JPS5096485A (en) * 1973-12-27 1975-07-31
JPS5278687A (en) * 1975-12-25 1977-07-02 Nagasaki Prefecture Manufacture of heavy metal collecting agents as main material of fly ash
JPS5318194B2 (en) * 1973-07-10 1978-06-13
JPS5531401A (en) * 1978-07-26 1980-03-05 Agency Of Ind Science & Technol Preparing adsorbent
JPS55116616A (en) * 1979-01-19 1980-09-08 Effem Gmbh Method of using grain or powder of calcium silicate

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5318194A (en) * 1976-08-02 1978-02-20 Nippon Air Brake Co Method of cargo stowage

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS49122889A (en) * 1973-03-29 1974-11-25
JPS5318194B2 (en) * 1973-07-10 1978-06-13
JPS5096485A (en) * 1973-12-27 1975-07-31
JPS5278687A (en) * 1975-12-25 1977-07-02 Nagasaki Prefecture Manufacture of heavy metal collecting agents as main material of fly ash
JPS5531401A (en) * 1978-07-26 1980-03-05 Agency Of Ind Science & Technol Preparing adsorbent
JPS55116616A (en) * 1979-01-19 1980-09-08 Effem Gmbh Method of using grain or powder of calcium silicate

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02293045A (en) * 1989-05-09 1990-12-04 Nippon Steel Corp Production of deodorant
US6132594A (en) * 1998-04-15 2000-10-17 Nippon Mitsubishi Oil Corp. Hydrocracking catalyst and hydrocracking method for hydrocarbon oils
KR20110061558A (en) * 2008-08-28 2011-06-09 오리카 익스플로시브스 테크놀로지 피티와이 리미티드 Improved integrated chemical process
JP2012500718A (en) * 2008-08-28 2012-01-12 オリカ エクスプロージブズ テクノロジー プロプライアタリー リミティド Improved integrated chemistry
CN109364872A (en) * 2018-11-19 2019-02-22 常熟理工学院 A kind of preparation method of sulfenyl cover type basic clinker adsorbent
CN109364872B (en) * 2018-11-19 2021-06-01 常熟理工学院 Preparation method of sulfur-based covering type alkaline ash adsorbent

Also Published As

Publication number Publication date
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