JPH11100242A - Treatment of chromium oxide-containing material - Google Patents
Treatment of chromium oxide-containing materialInfo
- Publication number
- JPH11100242A JPH11100242A JP9265623A JP26562397A JPH11100242A JP H11100242 A JPH11100242 A JP H11100242A JP 9265623 A JP9265623 A JP 9265623A JP 26562397 A JP26562397 A JP 26562397A JP H11100242 A JPH11100242 A JP H11100242A
- Authority
- JP
- Japan
- Prior art keywords
- slag
- chromium oxide
- blast furnace
- steam
- containing material
- 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
Landscapes
- Curing Cements, Concrete, And Artificial Stone (AREA)
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
Abstract
Description
【０００１】[0001]
【発明の属する技術分野】本発明は、ステンレス精錬の
際に発生するステンレス鋼スラグ、重クロム酸ナトリウ
ムなどのクロム化合物の製造の際に発生するクロム鉱
滓、廃棄物溶融スラグなどクロム酸化物含有物質中のCr
6+の還元処理方法に関するものである。The present invention relates to a chromium oxide-containing material such as stainless steel slag generated during refining of stainless steel, chromium slag generated during the production of chromium compounds such as sodium dichromate, and waste slag. Cr inside
It relates to a 6+ reduction treatment method.
【０００２】[0002]
【従来の技術】ステンレス精錬の際に発生するステンレ
ス鋼スラグ、および重クロム酸ナトリウムなどのクロム
化合物の製造の際に発生するクロム鉱滓は、数％のクロ
ム酸化物を含有し、操業条件によっては、過酸化クロ
ム、すなわちCr6+が溶出する場合がある。2. Description of the Related Art Stainless steel slag generated during stainless steel refining and chromium slag generated during the production of chromium compounds such as sodium dichromate contain several percent of chromium oxide, and depending on operating conditions. Chromium peroxide, that is, Cr 6+ may be eluted.
【０００３】このため、ステンレス鋼スラグ、クロム鉱
滓などを路盤材、仮設材、土木埋立材などとして使用す
る場合、スラグからCr6+が溶出しないことが絶対条件で
ある。また、近年、ゴミ焼却灰、汚泥などを溶融処理す
ることによりスラグ化し、生成したスラグを路盤材、タ
イルなどとして有効利用することが検討されているが、
ゴミ焼却灰、汚泥などの種類によっては、生成したスラ
グからCr6+が溶出する場合があり、有効利用を困難にし
ている。For this reason, when stainless steel slag, chromium slag, etc. are used as a roadbed material, a temporary material, a civil engineering landfill material, etc., it is an absolute condition that Cr 6+ does not elute from the slag. In recent years, waste incineration ash, sludge, etc. are melted and converted into slag, and the use of the generated slag as a roadbed material, tile, etc., has been studied.
Depending on the type of garbage incineration ash, sludge, etc., Cr 6+ may be eluted from the generated slag, making effective use difficult.
【０００４】ステンレス鋼スラグからのCr6+の溶出防止
方法として、特開平6-171993号公報において、アルミ灰
およびマグネシア系産業廃棄物を受滓鍋に敷き詰めてお
き、溶融状態にあるスラグを受滓鍋に排滓する方法が提
案されている。しかし、上記ステンレス鋼スラグからの
Cr6+の溶出防止方法は、上記添加剤を精錬炉外で添加し
ているため、撹拌することができず、混合が不十分とな
り、完全にCr6+の溶出を防止することができない場合が
ある。[0004] As a method for preventing elution of Cr 6+ from stainless steel slag, Japanese Unexamined Patent Publication No. Hei 6-171993 discloses a method in which aluminum ash and magnesia-based industrial waste are spread in a slag pan to receive molten slag. A method of discharging the slag in a slag pot has been proposed. However, from the above stainless steel slag
Cr 6+ elution prevention method, because the above additives are added outside the refining furnace, stirring is not possible, mixing is insufficient, and it is not possible to completely prevent Cr 6+ elution There is.
【０００５】上記方法において、混合を十分に行うため
に、精錬炉内で添加すれば、添加物が溶鋼を汚染する問
題が生じる。一方、重クロム酸ナトリウムなどのクロム
化合物の製造の際に発生するクロム鉱滓からのCr6+の溶
出防止方法として、一般に、スラグを還元焙焼して、Cr
6+をCr3+に還元して無害化している。[0005] In the above method, if added in a refining furnace in order to sufficiently mix, there is a problem that the additive contaminates molten steel. On the other hand, as a method for preventing the elution of Cr 6+ from chromium slag generated during the production of chromium compounds such as sodium dichromate, slag is generally reduced and roasted,
6+ is reduced to Cr 3+ to render it harmless.
【０００６】しかし、上記クロム化合物の製造の際に発
生するクロム鉱滓からのCr6+の溶出防止方法および汚泥
の焼却処理による安定化方法は、熱処理法のため多量の
エネルギーを要し、経済的に極めて高価な処理方法であ
る。本発明者らは、前記した従来技術の問題点を解決す
るために鋭意検討した結果、ステンレス鋼スラグ、クロ
ム鉱滓などからのCr6+の溶出防止方法として、これらの
スラグに高炉徐冷スラグ冷却水を散水する方法、高炉徐
冷スラグ冷却水に浸漬する方法、高炉徐冷スラグと混合
し水蒸気を吹き込む方法を提案し、クロム酸化物含有物
質からのCr6+の溶出を完全に防止することを可能とした
（特願平９−75588号）。However, the method for preventing the elution of Cr 6+ from the chromium slag generated during the production of the chromium compound and the method for stabilizing the sludge by incineration require a large amount of energy due to the heat treatment method, and are economical. This is an extremely expensive processing method. The present inventors have conducted intensive studies to solve the above-mentioned problems of the prior art, and as a method of preventing the elution of Cr 6+ from stainless steel slag, chromium slag, etc., these slags were cooled by blast furnace gradual cooling slag cooling. Propose a method of spraying water, a method of immersing in blast furnace slow cooling slag cooling water, a method of mixing with blast furnace slow cooling slag and blowing steam to completely prevent the elution of Cr 6+ from chromium oxide-containing substances (Japanese Patent Application No. 9-75588).
【０００７】一方、上記した高炉徐冷スラグ冷却水を散
水する方法および高炉徐冷スラグ冷却水に浸漬する方法
の場合、環境庁告示46号法による溶出試験において10mg
/l以上のCr6+が溶出するスラグまたは気孔率が低いスラ
グの場合、完全に安定化するためには長時間の処理が必
要であった。また、高炉徐冷スラグと混合し水蒸気を吹
き込む方法の場合、上記したスラグの場合でも短時間で
安定化することが可能であるが、高炉徐冷スラグを添加
する必要があることから、体積が増加するという問題が
あり、改善すべき余地があった。On the other hand, in the above-mentioned method of sprinkling the blast furnace slow cooling slag cooling water and the method of immersing in the blast furnace slow cooling slag cooling water, 10 mg was obtained in a dissolution test according to the Environment Agency Notification No. 46 method.
In the case of a slag in which Cr 6+ of / l or more is eluted or a slag having a low porosity, a long time treatment was required for complete stabilization. Further, in the case of a method of mixing with the blast furnace slow cooling slag and blowing steam, it is possible to stabilize the above-mentioned slag in a short time, but since the blast furnace slow cooling slag needs to be added, the volume is reduced. There was a problem of increase, and there was room for improvement.
【０００８】[0008]
【発明が解決しようとする課題】本発明は、前記した従
来技術の問題点を解決し、ステンレス鋼スラグ、クロム
鉱滓、廃棄物溶融スラグなどクロム酸化物含有物質を、
短時間かつ被処理材の体積を増加することなく、工業的
に簡易で経済性に優れた方法で処理し、これらクロム酸
化物含有物質からのCr6+の溶出を完全に防止することが
可能なクロム酸化物含有物質の処理方法を提供すること
を課題とする。SUMMARY OF THE INVENTION The present invention solves the above-mentioned problems of the prior art, and reduces the chromium oxide-containing substance such as stainless steel slag, chromium slag, and waste slag.
In a short time and without increasing the volume of the material to be treated, it is possible to treat it industrially with a simple and economical method to completely prevent the elution of Cr 6+ from these chromium oxide-containing substances. It is an object to provide a method for treating a chromium oxide-containing substance.
【０００９】[0009]
【課題を解決するための手段】本発明者らは、前記した
従来技術の問題点について種々検討、実験を行った結
果、スラグに水蒸気を吹き込むことによって、予めスラ
グ中のCr6+を還元しやすい形態にした後、未エージング
高炉徐冷スラグ溶出水により還元処理することによっ
て、スラグを、短時間かつ工業的に簡易で経済性に優れ
た方法で安定化し、Cr6+の溶出を完全に防止することが
可能であることを新規に見出し、本発明に到った。Means for Solving the Problems The present inventors have conducted various studies and experiments on the above-mentioned problems of the prior art, and as a result, by blowing steam into the slag, the Cr 6+ in the slag was reduced in advance. After the slag is made into an easy-to-use form, it is subjected to reduction treatment with unaged blast furnace slow-cooled slag leaching water to stabilize the slag in a short time, industrially simple and economical method, and to completely elute Cr 6+. The inventors have newly found that it is possible to prevent this, and have arrived at the present invention.
【００１０】すなわち、第１の発明は、クロム酸化物含
有物質に水蒸気を吹き込んだ後、得られたクロム酸化物
含有物質に、高炉スラグの散水冷却時に発生する高炉ス
ラグ溶出水を散水することを特徴とするクロム酸化物含
有物質の処理方法である。また、第２の発明は、クロム
酸化物含有物質に水蒸気を吹き込んだ後、得られたクロ
ム酸化物含有物質を、高炉スラグの散水冷却時に発生す
る高炉スラグ溶出水中に浸漬することを特徴とするクロ
ム酸化物含有物質の処理方法である。That is, a first aspect of the present invention is to spray water-blasted blast furnace slag generated at the time of water-cooling of blast furnace slag into the obtained chromium oxide-containing material after blowing steam into the chromium oxide-containing material. This is a method for treating a chromium oxide-containing material. Further, the second invention is characterized in that after the steam is blown into the chromium oxide-containing substance, the obtained chromium oxide-containing substance is immersed in blast furnace slag elution water generated during sprinkling cooling of the blast furnace slag. This is a method for treating a chromium oxide-containing substance.
【００１１】[0011]
【発明の実施の形態】以下、本発明をさらに詳細に説明
する。本発明者らは、環境庁告示46号法による溶出試験
におけるCr6+の溶出量が10mg/l以上のスラグまたは気孔
率が低いスラグを、短時間かつ被処理材の体積を増加す
ることなく、工業的に簡易で経済性に優れた方法で処理
し、これらのスラグからのCr6+の溶出を完全に防止する
ことが可能なクロム酸化物含有物質の処理方法につい
て、鋭意検討、実験を重ねた。BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in more detail. The present inventors have found that the amount of Cr 6+ dissolved in a dissolution test according to the Environment Agency Notification No. 46 method is 10 mg / l or more slag or a low porosity slag, in a short time without increasing the volume of the material to be treated. Investigating and experimenting on a method for treating chromium oxide-containing substances that can be industrially simple and economically efficient, and that can completely prevent the elution of Cr 6+ from these slags. Stacked.
【００１２】その結果、スラグに高温度の水蒸気を吹き
込むことにより、Cr6+が溶出しやすい形態にした後、得
られたスラグに高炉徐冷スラグ溶出水を散水するか、ま
たは、得られたスラグを高炉徐冷スラグ溶出水中に浸漬
することにより、短時間かつ体積を増やすことなく、経
済性に優れた方法でCr6+を還元し、完全に安定化できる
ことを見い出した。As a result, the slag was blown with high-temperature steam to form a form in which Cr 6+ was easily eluted, and then the slag was sprinkled with blast-furnace gradually cooled slag elution water or obtained. By immersing the slag in the blast furnace slowly cooled slag elution water, it was found that Cr 6+ can be reduced and completely stabilized in a short time and without increasing the volume in an economical manner.
【００１３】すなわち、本発明によれば、(1) 過酸化ク
ロムを含むスラグに水蒸気を吹き込んだ後、未エージン
グ高炉徐冷スラグ溶出水を散水するか、もしくは、(2)
過酸化クロムを含むスラグに水蒸気を吹き込んだ後、未
エージング高炉徐冷スラグ溶出水中に浸漬することによ
って、短時間かつ体積の増加を伴わずに、経済性に優れ
た方法でスラグ中のCr6+を還元処理することが可能とな
った。That is, according to the present invention, (1) water vapor is blown into a slag containing chromium peroxide, and then the unaged blast furnace slowly cooled slag elution water is sprinkled, or (2)
After blowing steam into slag containing peroxide chromium, by immersion in non-aging slowly cooled blast furnace slag dissolution in water, quickly and without the increase in volume, in the slag by the method excellent in economical Cr 6 + Can be reduced.
【００１４】図１に、ステンレス鋼スラグに対する水蒸
気吹き込み時間とスラグからのCr6+溶出量との関係を示
す。図１は、Cr6+が溶出するステンレス鋼スラグに100
℃の水蒸気を所定時間吹き込んだ後、環境庁告示46号法
による溶出試験を行い、Cr6+溶出量と水蒸気吹き込み時
間との関係をプロットしたものである。FIG. 1 shows the relationship between the steam blowing time for stainless steel slag and the amount of Cr 6+ eluted from the slag. Figure 1 shows that 100% of stainless steel slag in which Cr 6+ elutes
In this figure , a relationship between the Cr 6+ elution amount and the steam blowing time is plotted by performing a dissolution test in accordance with the notification method of the Environment Agency No. 46 after blowing steam at ℃ for a predetermined time.
【００１５】なお、本試験におけるスラグの粒度は26.5
〜13.2mmで、溶出試験を行う際の粒度も26.5〜13.2mmで
あり、破砕は行っていない。図１に示すように、Cr6+溶
出量は、100 ℃の水蒸気を吹き込む前よりも、100℃の
水蒸気を24時間吹き込んだ後の方が多い。本試験結果
は、水蒸気にはクロムを酸化する作用がないことから、
100 ℃の水蒸気を吹き込むことにより、Cr6+が溶出しや
すい、すなわち還元しやすい形態になることを示竣して
いる。The slag particle size in this test was 26.5.
The particle size at the time of performing the dissolution test was 26.5 to 13.2 mm, and no crushing was performed. As shown in FIG. 1, the amount of Cr 6+ eluted is greater after blowing 100 ° C. water vapor for 24 hours than before blowing 100 ° C. water vapor. This test result shows that water vapor does not have the effect of oxidizing chromium,
It has been shown that by blowing steam at 100 ° C., Cr 6+ can be easily eluted, that is, reduced.
【００１６】これは、水蒸気による毛細管現象により、
スラグ内部のCr6+がスラグの表面層に移動・濃縮するた
めと考えられる。100 ℃の水蒸気を24時間よりも長時間
吹き込むとCr6+溶出量は低くなるが、これは溶出しやす
い形態になったCr6+が、水蒸気を吹き込むことにより発
生したドレンに溶解し、除去されているためである。This is due to the capillary action caused by water vapor.
This is probably because Cr 6+ inside the slag migrates and concentrates on the surface layer of the slag. When the steam at 100 ° C is blown for longer than 24 hours, the amount of Cr 6+ eluted decreases, but this is because the easily eluted Cr 6+ dissolves in the drain generated by blowing the steam and is removed. That is because.
【００１７】したがって、極めて長時間水蒸気を吹き込
めば、Cr6+を完全に除去することができるが、現実的な
方法ではない。そこで、本発明者らは、上記した新たな
知見に基づき、水蒸気を吹き込むことにより、スラグ中
のCr6+を溶出しやすい形態にした後、還元剤、すなわち
未エージング高炉徐冷スラグ溶出水を用いて還元処理す
る処理方法を見い出した。Therefore, if steam is blown for an extremely long time, Cr 6+ can be completely removed, but this is not a practical method. Therefore, the present inventors, based on the above-mentioned new knowledge, by blowing steam, to form a form in which the slag is easy to elute Cr6 + , then the reducing agent, i.e., the non-aged blast furnace gradually cooled slag leaching water. A treatment method for performing a reduction treatment using the same has been found.
【００１８】なお、本発明において用いる水蒸気は高温
度の水蒸気であることが好ましいが、その温度は特に限
定されるものではない。これは、大気中で水蒸気を吹き
込む場合、水蒸気の温度は通常100 ℃であるが、密閉容
器中に高圧力の水蒸気を吹き込む場合、内部が高圧とな
ることから、水の沸点が100 ℃よりも高くなり、水蒸気
の温度も圧力に応じて高くなるためである。The steam used in the present invention is preferably high-temperature steam, but the temperature is not particularly limited. This is because when steam is blown in the atmosphere, the temperature of the steam is usually 100 ° C. However, when steam with high pressure is blown into a closed container, the internal pressure becomes high, so the boiling point of water is higher than 100 ° C. This is because the temperature increases, and the temperature of the steam also increases according to the pressure.
【００１９】なお、本発明における水蒸気を吹き込む方
法としては、水蒸気を単独で吹き込む方法に限定され
ず、空気、N2などの他のガスを含有する水蒸気を吹き込
んでもよい。また、水蒸気を吹き込む時間についても特
に限定はされない。これは、対象とするスラグの粒度、
気孔率などによって、Cr6+が溶出しやすい形態となる時
間が異なるためである。The method of blowing steam in the present invention is not limited to the method of blowing steam alone, and steam containing other gas such as air and N 2 may be blown. Also, the time for blowing steam is not particularly limited. This is the slag granularity of interest,
This is because the time during which Cr 6+ is easily eluted varies depending on the porosity and the like.
【００２０】本発明における高炉スラグは、JIS A 5015
付属書１の呈色判定試験方法において呈色がある未エー
ジング高炉徐冷スラグであることが好ましく、高炉スラ
グ溶出水としては、概ね、自然エージング３ヶ月未満の
未エージング高炉徐冷スラグに水を散水して生じた溶出
水を用いることが好ましい。例えば、高温状態の高炉ス
ラグに水を散水して生じた溶出水が適する。The blast furnace slag in the present invention is JIS A 5015
In the color determination test method of Annex 1, it is preferable to use an unaged blast furnace slowly cooled slag having a color. As the blast furnace slag elution water, water is generally added to an unaged blast furnace slowly cooled slag of less than 3 months in natural aging. It is preferable to use elution water generated by water spraying. For example, elution water generated by spraying water on a blast furnace slag in a high temperature state is suitable.
【００２１】未エージング高炉徐冷スラグ溶出水によっ
てCr6+をCr3+に還元する機構は、未エージング高炉徐冷
スラグ溶出水中の還元性の硫黄（S2- ,S0, S203 2- ）が
酸化することによるものである。また、本発明において
は、未エージング高炉徐冷スラグ溶出水とCr6+を還元す
る作用のある他の還元剤を併用してもよい。The mechanism for reducing Cr 6+ to Cr 3+ by the unaged blast furnace slow-cooled slag leaching water is based on the reducing sulfur (S 2− , S 0 , S 2 0 3) in the unaged blast furnace slow-cooled slag leaching water. 2- ) is due to oxidation. In the present invention, the unaged blast furnace slowly cooled slag leaching water and another reducing agent having an action of reducing Cr 6+ may be used in combination.
【００２２】すなわち、例えば、硫酸第一鉄を未エージ
ング高炉徐冷スラグ溶出水中に溶解して使用してもよ
い。スラグに対する未エージング高炉徐冷スラグ溶出水
の散水量、浸漬時の浸漬時間、スラグと浸漬液の量比
は、特に限定しない。これは、対象とするスラグの粒
度、気孔率、Cr6+含有量により上記に係わる好適条件が
異なるためである。That is, for example, ferrous sulfate may be used by dissolving it in unaged blast furnace slowly cooled slag elution water. The sprinkling amount of the unaged blast furnace slowly cooled slag elution water to the slag, the immersion time during immersion, and the ratio of the slag to the immersion liquid are not particularly limited. This is because the suitable conditions relating to the above vary depending on the particle size, porosity, and Cr 6+ content of the target slag.
【００２３】本発明は、高濃度、おおよそ10mg/l以上の
Cr6+が溶出するスラグに適用すると特に効果的である
が、もちろん低濃度のCr6+が溶出するスラグに適用して
も効果的である。なお、本発明をCr6+を含むステンレス
鋼スラグ、クロム鉱滓、産業廃棄物、廃棄物溶融スラグ
などのスラグだけでなく、Cr6+を生成し得る可能性のあ
る他の物質に適用することにより、Cr6+の生成を防止す
ることが可能である。The present invention provides a high-concentration, approximately 10 mg / l or more
It is particularly effective when applied to a slag in which Cr 6+ elutes, but of course, it is also effective when applied to a slag in which a low concentration of Cr 6+ elutes. The present invention is applicable not only to slag such as stainless steel slag containing Cr 6+ , chromium slag, industrial waste and waste molten slag, but also to other substances that may generate Cr 6+. Thereby, generation of Cr 6+ can be prevented.
【００２４】[0024]
【実施例】以下、本発明を実施例に基づき具体的に説明
する。Cr6+を含有するクロム酸化物含有物質、すなわち
還元処理対象材として、ステンレス鋼スラグ、重クロム
酸ナトリウム製造の際に発生したクロム鉱滓、下水汚泥
溶融スラグを用いた。DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be specifically described below based on embodiments. Stainless steel slag, chromium slag generated during the production of sodium bichromate, and sewage sludge molten slag were used as the chromium oxide-containing material containing Cr 6+ , that is, the material to be subjected to the reduction treatment.
【００２５】なお、ステンレス鋼スラグのサンプルとし
ては、Cr6+が溶出するスラグが生成する操業条件下で製
造したサンプルを用いた。表１に、本実施例の実験に供
したステンレス鋼スラグ、クロム鉱滓、下水汚泥溶融ス
ラグの化学組成、気孔率、Cr6+溶出量を示す。Cr6+の溶
出量は、ステンレス鋼スラグが10.5mg/l、クロム鉱滓が
25.3mg/l、下水汚泥溶融スラグ−Ａ（気孔率：８％）が
0.8mg/l 、下水汚泥溶融スラグ−Ｂ（気孔率：２％）が
0.27mg/lである。As a sample of stainless steel slag, a sample manufactured under operating conditions in which slag in which Cr 6+ is eluted was used. Table 1 shows the chemical composition, porosity, and Cr 6+ elution amount of the stainless steel slag, chromium slag, and sewage sludge molten slag used in the experiment of this example. The elution amount of Cr 6+ was 10.5 mg / l for stainless steel slag and
25.3mg / l, sewage sludge molten slag-A (porosity: 8%)
0.8mg / l, sewage sludge molten slag-B (porosity: 2%)
It is 0.27 mg / l.
【００２６】これらの還元処理対象スラグを、表２に示
す条件下で処理し、処理後のスラグのCr6+の溶出量を測
定した。得られた結果を表２に併せて示す。なお、スラ
グの処理量は100t／バッチであり、未エージング高炉徐
冷スラグ溶出水としては、高温状態の高炉スラグに水を
散水して生じた溶出水(TotalＳ濃度：0.50wt％）を用い
た。The slag to be subjected to the reduction treatment was treated under the conditions shown in Table 2, and the slag after the treatment was measured for the amount of Cr 6+ eluted. Table 2 also shows the obtained results. The processing amount of the slag was 100 t / batch, and the eluent water (Total S concentration: 0.50 wt%) generated by spraying water on the blast furnace slag in a high temperature state was used as the unaged blast furnace slow cooling slag elution water. .
【００２７】また、水蒸気の吹き込み温度は100 ℃で、
スラグの底部から吹き込んだ。比較例１に示すように、
Cr6+溶出量が10.5mg/lのステンレス鋼スラグに未エージ
ング高炉徐冷スラグ溶出水を散水してもCr6+の溶出量
は、環境基準値である0.05mg/l以下にはならない。ま
た、比較例２〜５に示すように、ステンレス鋼スラグ、
クロム鉱滓、下水汚泥溶融スラグを未エージング高炉徐
冷スラグ溶出水中に７日間浸漬してもCr6+の溶出量は0.
05mg/l以下にはならない。The steam injection temperature is 100 ° C.
Inhaled from the bottom of the slag. As shown in Comparative Example 1,
Even if the unaged blast furnace slowly cooled slag elution water is sprinkled onto stainless steel slag with a Cr 6+ elution amount of 10.5 mg / l, the elution amount of Cr 6+ does not fall below the environmental standard value of 0.05 mg / l. Further, as shown in Comparative Examples 2 to 5, stainless steel slag,
The leaching amount of Cr 6+ is 0.
It does not fall below 05mg / l.
【００２８】一方、実施例１〜９に示すように、還元処
理対象スラグに水蒸気を吹き込んだ後、得られたスラグ
に未エージング高炉徐冷スラグ溶出水を散水するか、ま
たは、得られたスラグを未エージング高炉徐冷スラグ溶
出水中に浸漬することにより、Cr6+の溶出量を環境基準
値である0.05mg/l以下にすることができる。なお、実施
例１〜９のステンレス鋼スラグ、クロム鉱滓、下水汚泥
溶融スラグは、還元処理後、大気中に１年間放置しても
Cr6+の溶出は認められなかった。On the other hand, as shown in Examples 1 to 9, after steam was blown into the slag to be subjected to the reduction treatment, the obtained slag was sprinkled with eluate of unaged blast furnace slowly cooled slag, or the obtained slag was sprayed. Is immersed in an unaged blast-furnace slowly cooled slag elution water, whereby the elution amount of Cr 6+ can be reduced to 0.05 mg / l or less, which is the environmental standard value. The stainless steel slag, chromium slag, and sewage sludge molten slag of Examples 1 to 9 were allowed to stand in the air for one year after the reduction treatment.
No elution of Cr 6+ was observed.
【００２９】[0029]
【表１】 [Table 1]
【００３０】[0030]
【表２】 [Table 2]
【００３１】[0031]
【発明の効果】本発明によれば、ステンレス鋼スラグ、
クロム鉱滓、廃棄物溶融スラグなどクロム酸化物含有物
質を、短時間かつ被処理材の体積を増加することなく、
工業的に簡易で経済性に優れた方法で処理し、これらの
クロム酸化物含有物質からのCr 6+の溶出を完全に防止す
ることが可能となり、路盤材、仮設材、土木埋立材など
への再利用を容易に行うことが可能となった。According to the present invention, stainless steel slag,
Chromium oxide-containing substances such as chromium slag and waste molten slag
Quality, in a short time and without increasing the volume of the material to be treated,
Processed in an industrially simple and economical manner,
Cr from chromium oxide containing material 6+Completely prevent elution of
Roadbed materials, temporary materials, civil engineering landfill materials, etc.
It can be easily reused.
【図１】ステンレス鋼スラグに対する水蒸気吹き込み時
間とスラグからのCr6+溶出量との関係を示すグラフであ
る。FIG. 1 is a graph showing the relationship between the steam blowing time for stainless steel slag and the amount of Cr 6+ eluted from the slag.
───────────────────────────────────────────────────── フロントページの続き (72)発明者 當房 博幸 千葉県千葉市中央区川崎町１番地 川崎製 鉄株式会社技術研究所内 (72)発明者 岸本 康夫 千葉県千葉市中央区川崎町１番地 川崎製 鉄株式会社技術研究所内 (72)発明者 櫻谷 敏和 東京都千代田区内幸町２丁目２番３号 川 崎製鉄株式会社内 ──────────────────────────────────────────────────の Continuing on the front page (72) Inventor Hiroyuki Tobo 1 Kawasaki-cho, Chuo-ku, Chiba City, Chiba Prefecture Inside the Technical Research Institute of Kawasaki Steel Corporation (72) Inventor Yasuo Kishimoto 1-Kawasaki-cho, Chuo-ku, Chiba City, Chiba Prefecture (72) Inventor Toshikazu Sakuraya 2-3-2 Uchisaiwaicho, Chiyoda-ku, Tokyo Inside Kawasaki Steel Corporation
Claims (2)
んだ後、得られたクロム酸化物含有物質に、高炉スラグ
の散水冷却時に発生する高炉スラグ溶出水を散水するこ
とを特徴とするクロム酸化物含有物質の処理方法。1. A chromium oxide, characterized in that after blowing steam into the chromium oxide-containing substance, blast furnace slag eluate generated during blast furnace slag sprinkling cooling is sprinkled into the obtained chromium oxide-containing substance. How to treat contained substances.
んだ後、得られたクロム酸化物含有物質を、高炉スラグ
の散水冷却時に発生する高炉スラグ溶出水中に浸漬する
ことを特徴とするクロム酸化物含有物質の処理方法。2. A chromium oxide characterized in that after steam is blown into the chromium oxide-containing substance, the obtained chromium oxide-containing substance is immersed in blast furnace slag elution water generated during sprinkling cooling of blast furnace slag. How to treat contained substances.
Priority Applications (14)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP26562397A JP3221564B2 (en) | 1997-09-30 | 1997-09-30 | Method for treating chromium oxide-containing material |
| TW87104091A TW477818B (en) | 1997-03-27 | 1998-03-19 | Method for processing chromium oxide-containing substances in large quantities, method for utilizing the processed substances, and products comprising the processed substances |
| US09/047,411 US6336967B1 (en) | 1997-03-27 | 1998-03-25 | Method for processing chromium oxide-containing substances in large quantities, method for utilizing the processed substances, and products comprising the processed substances |
| DE1998638267 DE69838267T2 (en) | 1997-03-27 | 1998-03-26 | Process for Cr (VI) reduction in waste materials containing chromium oxide |
| DE1998624775 DE69824775T2 (en) | 1997-03-27 | 1998-03-26 | Process for the treatment of substances containing chromium oxide in large quantities |
| EP20040000464 EP1413635B1 (en) | 1997-03-27 | 1998-03-26 | Method for reducing Cr(VI) in chromium oxide-containing waste materials |
| KR1019980010559A KR100318792B1 (en) | 1997-03-27 | 1998-03-26 | Method for processing chromium oxide-containing substances in large quantities, method for utilizing the processed substances, and products comprising the processed substances |
| EP19980105535 EP0869193B1 (en) | 1997-03-27 | 1998-03-26 | Method for processing chromium oxide-containing substances in large quantities |
| ES98105535T ES2223092T3 (en) | 1997-03-27 | 1998-03-26 | TREATMENT PROCEDURE IN LARGE AMOUNTS OF SUBSTANCES CONTAINING CHROME OXIDE. |
| CA 2233388 CA2233388C (en) | 1997-03-27 | 1998-03-26 | Method for processing chromium oxide containing substances in large quantities, method for utilizing the processed substances, and products comprising the processed substances |
| ES04000464T ES2293102T3 (en) | 1997-03-27 | 1998-03-26 | CR (6+) REDUCTION PROCEDURE IN WASTE CONTAINING CHROME OXIDES. |
| BR9801203A BR9801203A (en) | 1997-03-27 | 1998-03-27 | Method for processing, in large quantities, substances containing chromium oxide, method for using processed substances, and products comprising processed substances. |
| CN98108899A CN1112975C (en) | 1997-03-27 | 1998-03-27 | Method for treating matter contg. chromium oxides in large scale, and method for utilizing after-treatment matter |
| US09/984,038 US6521040B2 (en) | 1997-03-27 | 2001-10-26 | Method for processing chromium oxide-containing substances in large quantities, method for utilizing the processed substances, and products comprising the processed substances |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP26562397A JP3221564B2 (en) | 1997-09-30 | 1997-09-30 | Method for treating chromium oxide-containing material |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH11100242A true JPH11100242A (en) | 1999-04-13 |
| JP3221564B2 JP3221564B2 (en) | 2001-10-22 |
Family
ID=17419711
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP26562397A Expired - Fee Related JP3221564B2 (en) | 1997-03-27 | 1997-09-30 | Method for treating chromium oxide-containing material |
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| Country | Link |
|---|---|
| JP (1) | JP3221564B2 (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2005201479A (en) * | 2004-01-13 | 2005-07-28 | Nippon Steel Corp | Method of treating slag containing chromium oxide |
| US7459020B2 (en) | 2001-10-23 | 2008-12-02 | Denki Kagaku Kogyo Kabushiki Kaisha | Cement admixture, cement composition, and cement concrete made therefrom |
| JP2011036827A (en) * | 2009-08-18 | 2011-02-24 | Jfe Steel Corp | Method for treating substance containing chromium oxide |
| JP2014024713A (en) * | 2012-07-26 | 2014-02-06 | Kobe Steel Ltd | Steel slag hydration product, and production method of the same |
-
1997
- 1997-09-30 JP JP26562397A patent/JP3221564B2/en not_active Expired - Fee Related
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7459020B2 (en) | 2001-10-23 | 2008-12-02 | Denki Kagaku Kogyo Kabushiki Kaisha | Cement admixture, cement composition, and cement concrete made therefrom |
| JP2005201479A (en) * | 2004-01-13 | 2005-07-28 | Nippon Steel Corp | Method of treating slag containing chromium oxide |
| JP2011036827A (en) * | 2009-08-18 | 2011-02-24 | Jfe Steel Corp | Method for treating substance containing chromium oxide |
| JP2014024713A (en) * | 2012-07-26 | 2014-02-06 | Kobe Steel Ltd | Steel slag hydration product, and production method of the same |
Also Published As
| Publication number | Publication date |
|---|---|
| JP3221564B2 (en) | 2001-10-22 |
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