JPH03249984A - Method for regenerating used cr6+-containing basic brick - Google Patents
Method for regenerating used cr6+-containing basic brickInfo
- Publication number
- JPH03249984A JPH03249984A JP4558490A JP4558490A JPH03249984A JP H03249984 A JPH03249984 A JP H03249984A JP 4558490 A JP4558490 A JP 4558490A JP 4558490 A JP4558490 A JP 4558490A JP H03249984 A JPH03249984 A JP H03249984A
- Authority
- JP
- Japan
- Prior art keywords
- water
- bricks
- brick
- maguro
- basic brick
- 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
Links
- 239000011449 brick Substances 0.000 title claims abstract description 38
- 238000000034 method Methods 0.000 title claims abstract description 19
- 230000001172 regenerating effect Effects 0.000 title abstract 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 17
- 150000001875 compounds Chemical class 0.000 claims description 6
- 238000004064 recycling Methods 0.000 claims description 5
- 239000000126 substance Substances 0.000 claims description 3
- 238000009835 boiling Methods 0.000 claims description 2
- 239000002994 raw material Substances 0.000 abstract description 8
- 238000010828 elution Methods 0.000 abstract description 4
- 238000003756 stirring Methods 0.000 abstract description 3
- 238000001035 drying Methods 0.000 abstract description 2
- 238000010438 heat treatment Methods 0.000 abstract description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 abstract 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 abstract 1
- OTYBMLCTZGSZBG-UHFFFAOYSA-L potassium sulfate Chemical compound [K+].[K+].[O-]S([O-])(=O)=O OTYBMLCTZGSZBG-UHFFFAOYSA-L 0.000 abstract 1
- 229910052939 potassium sulfate Inorganic materials 0.000 abstract 1
- 239000011651 chromium Substances 0.000 description 18
- 239000002245 particle Substances 0.000 description 7
- 239000004568 cement Substances 0.000 description 4
- 239000000463 material Substances 0.000 description 3
- 239000002244 precipitate Substances 0.000 description 3
- 239000002893 slag Substances 0.000 description 3
- 239000003513 alkali Substances 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- ZCDOYSPFYFSLEW-UHFFFAOYSA-N chromate(2-) Chemical class [O-][Cr]([O-])(=O)=O ZCDOYSPFYFSLEW-UHFFFAOYSA-N 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 150000001805 chlorine compounds Chemical class 0.000 description 1
- JOPOVCBBYLSVDA-UHFFFAOYSA-N chromium(6+) Chemical class [Cr+6] JOPOVCBBYLSVDA-UHFFFAOYSA-N 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 238000011437 continuous method Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 238000010304 firing Methods 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 238000007654 immersion Methods 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 238000005325 percolation Methods 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 239000011819 refractory material Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 238000009628 steelmaking Methods 0.000 description 1
- 150000003467 sulfuric acid derivatives Chemical class 0.000 description 1
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
Description
【発明の詳細な説明】
[産業上の利用分野]
本発明は実炉に使用された塩基性れんが、特にマグクロ
れんがまたはクロマグれんがの再生利用法に関する。DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention relates to a method for recycling basic bricks used in actual furnaces, particularly maguro bricks or chroma bricks.
[従来の技術]
マグクロれんがあるいはクロマグれんがは使用される窯
炉においてアルカリないしカルシウム成分が存在し、且
つ酸素分圧が高い場合には、れんが中のタロマイトCr
ho 、(Cr”)が次の反応を生じ、有害なCr”の
化合物を生ずる:
2 Cr 20! + 4 K 20 + 302 =
4 K 2 Cr O+2cr20z+ 4CaO+
302=4CaCrO。[Prior Art] When maguro bricks or chroma bricks are used in a kiln in which alkaline or calcium components are present and the partial pressure of oxygen is high, the talomite Cr in the bricks is
ho, (Cr”) undergoes the following reaction to produce the harmful Cr” compound: 2 Cr 20! + 4 K 20 + 302 =
4 K 2 Cr O+2cr20z+ 4CaO+
302=4CaCrO.
これらの反応はセメント焼成炉において特に生じ易い。These reactions are particularly likely to occur in cement kilns.
これはセメント原料の一部である粘土にアルカリ化合物
が数%含まれていること、及び主原料がCaOであるこ
とに加えて酸素分圧の高い部位すなわちロータリーキル
ンの焼成帯にはマグクロれんがが使用されているためで
ある。以下、本明細書ではセメントロータリーキルンで
の例を挙げて説明する。This is because clay, which is part of the raw material for cement, contains a few percent of alkali compounds, and the main raw material is CaO. In addition, maguro bricks are used in areas with high oxygen partial pressure, that is, in the firing zone of the rotary kiln. This is because it has been Hereinafter, this specification will be explained using an example of a cement rotary kiln.
セメントロータリーキルンに内張すされたマグクロれん
がは全呼の約1/2〜2/3を使用するだけで、元の厚
さ(150〜250IIIIm)の2分の1から3分の
1を残して取り外され、新しいれんかに取り替えられる
。取り外されたマグクロれんがすなわち使用後のマグク
ロれんがは先に述べたようにアルカリ及びCaOの存在
下にさらされて6価のクロム化合物をクロマイトの周辺
に生ずる。Maguro bricks lined in a cement rotary kiln require only about 1/2 to 2/3 of the total thickness, leaving 1/2 to 1/3 of the original thickness (150 to 250 III m). It will be removed and replaced with a new brick. The removed Maguro brick, that is, the Maguro brick after use, is exposed to the presence of alkali and CaO, as described above, to produce hexavalent chromium compounds around the chromite.
Cr”の生成量はその使用条件によって異なり定かでは
ないが、500〜3000ppmに達する場合もある。The amount of Cr" produced varies depending on the conditions of use and is not certain, but it may reach 500 to 3000 ppm in some cases.
[発明が解決しようとする課M]
これらの使用済マグクロれんがは大力製鋼用電気炉ある
いは転炉の吹付補修材ないしスラグコーチング材として
使用される。この場合、使用済マグクロれんが中のCr
”はスラグに拡散され且つその後も冷却によりスラグが
固化するためCr”としての実害は実質上生じ得ない。[Problem M to be Solved by the Invention] These used maguro bricks are used as a spray repair material or slag coating material for electric furnaces or converters for large-scale steelmaking. In this case, Cr in used Maguro bricks
Since "Cr" is diffused into the slag and the slag is solidified by cooling thereafter, there is virtually no actual damage caused by "Cr".
一方、マグクロれんが等の主成分であるクロム鉱(クロ
マイト)は極めて重要な耐火物原料であり、省資源の観
点からも使用済マグクロれんがの再生、利用は重要な課
題である。また、鉄鋼での吹付補修材等として需給バラ
ンスが崩れ、使用済マグクロれんが量が過剰となった場
合は、その取り扱い如何によっては重大な環境汚染問題
を生じかねない。On the other hand, chromite (chromite), which is the main component of maguro bricks, is an extremely important raw material for refractories, and the recycling and utilization of used maguro bricks is an important issue from the perspective of resource conservation. Furthermore, if the supply and demand balance is disrupted and the amount of used maguro bricks becomes excessive as a spray repair material for steel, etc., depending on how they are handled, serious environmental pollution problems may occur.
[課題を解決するための手段]
即ち、本発明はCr”含有使用済塩基性れんがを水、温
水ないし熱湯に浸漬することによりCr”を含む化合物
の他の水溶性物質を溶出処理し、溶出処°理済れんがを
水切り、乾燥することを特徴とする使用済塩基性れんが
の再生方法に係る。[Means for Solving the Problems] That is, the present invention processes a Cr"-containing used basic brick by immersing it in water, warm water, or boiling water to elute other water-soluble substances of the Cr"-containing compound. The present invention relates to a method for recycling used basic bricks, which comprises draining and drying the treated bricks.
[作 用コ
本発明者らは前記K 2Cro 、、Ca Cr O*
等のクロム酸塩類の水への溶解度が高い〈特にK 2
Cr O−)ことに着目し、使用済マグクロれんがを水
中に浸漬し、振盪、撹拌、加熱等を与えることによって
容易にCr”化合物を溶出するばかりでなく、再生原料
として含まれては好ましくない使用済れんが中に沈積し
たに2SO,、K(lといった硫酸塩、塩化物を同時に
溶出できるため、より清浄な再生原料が得られることに
なる。[Function] The present inventors used the above-mentioned K 2Cro , Ca Cr O *
Chromates such as chromates have high solubility in water (especially K 2
Focusing on CrO-), by immersing used Maguro bricks in water and applying shaking, stirring, heating, etc., Cr'' compounds are not only easily eluted, but also undesirable if they are included as recycled raw materials. Since sulfates and chlorides such as SO, K(l) deposited in used bricks can be eluted at the same time, a cleaner recycled raw material can be obtained.
ちなみに、これらの化合物の0℃の水100I?に対す
る溶解度は次の通りである:
K 2 Cr O458、0g
CaCrO< 22.0IF
K 2 S O47、35Li
KCl 27.6g
これらの溶出の速度を増すについては使用済れんがを粉
砕して粒径を減少させ、表面積を多くすることが有効で
あるが、粒径が小さすぎると固液の分離性が低下する。By the way, 100 I of water at 0°C for these compounds? The solubility for K 2 Cr O 458, 0 g CaCrO < 22.0 IF K 2 S O 47, 35 Li KCl 27.6 g To increase the rate of these elutions, reduce the particle size by crushing the used bricks. It is effective to increase the surface area by increasing the particle size, but if the particle size is too small, the solid-liquid separability will decrease.
処理済のれんがを再生使用する際の粒度はおよそ5II
I*から11であるが、当初からこの粒度に粉砕して処
理することは先に述べた問題から好ましくはないが、粉
状のものは粉砕過程において必然的に生ずるものであり
、実質的には50〜5mmの塊ないし粒状のものと5I
II*m以下の粉状に分けてする方法が良い。The particle size when reusing treated bricks is approximately 5II.
From I* to 11, it is not preferable to grind the particles to this particle size from the beginning due to the problems mentioned above, but since powdered particles are inevitably produced during the grinding process, are 50-5mm lumps or granules and 5I
It is best to divide it into powders of II*m or less.
溶出に際しての具体的な装置は一般にはいわゆる固体抽
出装置として非連続法(固定式)としてパーコレーショ
ンタンク法、撹拌槽式等、連続法では、Rotocel
器法、K ennedy法等があるが、ここではこの方
法については限定しない。The specific equipment for elution is generally a so-called solid extraction equipment, such as a discontinuous method (fixed type) such as a percolation tank method or a stirring tank method, and a continuous method such as a Rotocel.
Although there are methods such as the German method and the Kennedy method, this method is not limited here.
溶出処理後のいわば清浄された使用済マグクロれんがは
水切り後、乾燥して耐火原料として再生、利用され、C
r”等を含む溶出液は公知の手法に従ってpH調整後、
F e S O4等の還元剤の投入によってCr″°に
還元され、次に、中和するとCr(OH)s等となって
沈澱し、以後、沈澱物と溶液に分離され、凝集剤を添加
することによって溶液との分離が容易となる。The used Maguro bricks that have been cleaned after the elution process are drained, dried, and recycled and used as a refractory raw material.
After adjusting the pH of the eluate containing r'' etc. according to a known method,
It is reduced to Cr″° by adding a reducing agent such as F e S O4, and then, when neutralized, it precipitates as Cr(OH)s, etc. After that, it is separated into a precipitate and a solution, and a flocculant is added. This facilitates separation from the solution.
なお、C「60等を含む溶出液の処理におけるp H調
整、還元処理、中和処理、沈澱物の分離、溶液の排出に
ついての操作は既に確立されている任意の技術を使用す
ることができる。In addition, any already established techniques can be used for the operations for pH adjustment, reduction treatment, neutralization treatment, separation of precipitates, and solution discharge in the treatment of eluate containing C60 etc. .
[実 施 例コ 以下に実施例を挙げて本発明を更に説明する。[Implementation example] The present invention will be further explained with reference to Examples below.
実施例
に202.08%、NazO0,25%及び11060
ppのCr’°を含む使用済マグクロれんが100gを
振動を加えつつ、循環する温水(50℃)30(H!に
1時間浸漬し、水切りを行い、乾燥することによりマグ
クロれんがを清浄化処理した。Examples include 202.08%, NazO0.25% and 11060
100 g of used Maguro bricks containing pp Cr'° were immersed in circulating warm water (50°C) 30 (H!) for 1 hour while being vibrated, drained, and dried to clean the Maguro bricks. .
処理済マグクロれんがのCr”を測定したところ、Cr
@+は8pp3 K2Oは0.02%、また、N a
20は0.005%と大幅な低減を見た。これらの値は
再生使用上何ら悪影響を及ぼす値ではないが、処理方法
の工夫例えば浸漬時間の延長、温水の循環速度を早める
こと等によって一層の低減化が可能である。When the Cr” of treated Maguro bricks was measured, it was found that Cr
@+ is 8pp3 K2O is 0.02%, and Na
20 saw a significant reduction of 0.005%. Although these values do not have any adverse effects on recycling, they can be further reduced by improving the treatment method, such as extending the immersion time and increasing the circulation speed of hot water.
[発明の効果]
上述のように、本発明方法は工業化も極めて容易であり
、使用済マグクロれんがからCr”含有物質等の水溶性
不純物を溶出せしめるのに極めて適性且つ経済的な手段
といえる。[Effects of the Invention] As described above, the method of the present invention is extremely easy to industrialize, and can be said to be an extremely suitable and economical means for eluting water-soluble impurities such as Cr''-containing substances from used maguro bricks.
また、処理済のれんがは不純物が溶出除去されているこ
とから再生原料として充分活用できるのみならず、省資
源化にもなり、また、環境保全にも寄与するところが大
である。In addition, since impurities have been eluted and removed from treated bricks, they can not only be fully utilized as recycled raw materials, but also save resources and greatly contribute to environmental conservation.
Claims (1)
熱湯に浸漬することによりCr^6^+を含む化合物の
他の水溶性物質溶出処理し、溶出処理済れんがを水切り
、乾燥することを特徴とする使用済塩基性れんがの再生
方法。A used basic brick containing Cr^6^+ is immersed in water, warm water, or boiling water to elute other water-soluble substances of compounds containing Cr^6^+, and the eluted brick is drained and dried. A method for recycling used basic bricks, characterized by:
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2045584A JPH0673660B2 (en) | 1990-02-28 | 1990-02-28 | Cr ▲ 6 ▼ ▲ + + ▼ Recycled used basic brick containing |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2045584A JPH0673660B2 (en) | 1990-02-28 | 1990-02-28 | Cr ▲ 6 ▼ ▲ + + ▼ Recycled used basic brick containing |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH03249984A true JPH03249984A (en) | 1991-11-07 |
JPH0673660B2 JPH0673660B2 (en) | 1994-09-21 |
Family
ID=12723399
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2045584A Expired - Fee Related JPH0673660B2 (en) | 1990-02-28 | 1990-02-28 | Cr ▲ 6 ▼ ▲ + + ▼ Recycled used basic brick containing |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH0673660B2 (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH07328585A (en) * | 1994-06-10 | 1995-12-19 | Shinagawa Refract Co Ltd | Regeneration of alkali metal component-containing used brick |
JP2005201479A (en) * | 2004-01-13 | 2005-07-28 | Nippon Steel Corp | Method of treating slag containing chromium oxide |
JP2006281069A (en) * | 2005-03-31 | 2006-10-19 | Taiheiyo Cement Corp | Treating method of fired material containing chromic oxide |
JP2008168289A (en) * | 2006-12-11 | 2008-07-24 | Sumitomo Metal Ind Ltd | Detoxification method of heavy metal-containing basic waste |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5433294A (en) * | 1977-08-18 | 1979-03-10 | Asahi Glass Co Ltd | Treating method for hexavalent chromium containing substance |
JPS58174280A (en) * | 1982-04-07 | 1983-10-13 | Babcock Hitachi Kk | Treatment of waste containing chromium (6) |
-
1990
- 1990-02-28 JP JP2045584A patent/JPH0673660B2/en not_active Expired - Fee Related
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5433294A (en) * | 1977-08-18 | 1979-03-10 | Asahi Glass Co Ltd | Treating method for hexavalent chromium containing substance |
JPS58174280A (en) * | 1982-04-07 | 1983-10-13 | Babcock Hitachi Kk | Treatment of waste containing chromium (6) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH07328585A (en) * | 1994-06-10 | 1995-12-19 | Shinagawa Refract Co Ltd | Regeneration of alkali metal component-containing used brick |
JP2005201479A (en) * | 2004-01-13 | 2005-07-28 | Nippon Steel Corp | Method of treating slag containing chromium oxide |
JP2006281069A (en) * | 2005-03-31 | 2006-10-19 | Taiheiyo Cement Corp | Treating method of fired material containing chromic oxide |
JP2008168289A (en) * | 2006-12-11 | 2008-07-24 | Sumitomo Metal Ind Ltd | Detoxification method of heavy metal-containing basic waste |
Also Published As
Publication number | Publication date |
---|---|
JPH0673660B2 (en) | 1994-09-21 |
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