JP7303989B2 - Method for modifying boron-containing substance and method for producing civil engineering and construction material - Google Patents
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Description
本発明は、ホウ素含有物質の改質方法及び土木建築用資材の製造方法に関する。 TECHNICAL FIELD The present invention relates to a method for modifying a boron-containing substance and a method for producing a material for civil engineering and construction.
工業の発展にともない、各種産業において発生する産業副産物の量も増加の一途を辿っている。近年、地球環境保全の観点から、このような産業副産物の有効利用が行われている。例えば、製鉄所から発生する高炉スラグや製鋼スラグなどの鉄鋼スラグ、火力発電所から発生する石炭灰、及び廃棄物や下水汚泥の焼却灰等を高温で溶融し冷却・固化した溶融スラグ等は、適正な粒度調整を施された後、路盤材や地盤改良材などの土木建築用資材として再利用されている。 With the development of industry, the amount of industrial by-products generated in various industries is steadily increasing. In recent years, effective utilization of such industrial by-products has been carried out from the viewpoint of global environment conservation. For example, steel slag such as blast furnace slag and steelmaking slag generated from steel plants, coal ash generated from thermal power plants, and molten slag obtained by melting, cooling, and solidifying waste and sewage sludge incineration ash at high temperatures, After proper particle size adjustment, it is reused as a civil engineering and construction material such as roadbed material and ground improvement material.
産業副産物を再利用する際には、これに含まれる有害物質の環境中への排出を抑制する必要がある。代表的な有害物質としては、カドミウム、水銀、クロム及び鉛等の重金属類が例示できるが、これら重金属類以外に、例えば、フッ素、セレン、ヒ素及びホウ素等についても、環境に悪影響を与える成分として、環境への排出(溶出)が厳しく規制されている。 When reusing industrial by-products, it is necessary to suppress the emission of harmful substances contained therein into the environment. Typical hazardous substances include heavy metals such as cadmium, mercury, chromium and lead. In addition to these heavy metals, for example, fluorine, selenium, arsenic and boron are also harmful to the environment. , the emission (elution) into the environment is strictly regulated.
このような環境に悪影響を及ぼす成分のうち、ホウ素の溶出を抑制する方法としては、例えば、ホウ素が含まれる焼却灰に、酸化マグネシウムを粉末状又はスラリー状で添加、混合する方法(特許文献1)、火力発電所等から排出される石炭灰を所定期間加湿養生する方法(特許文献2)、及びホウ素含有物質の冷却速度を制御すること、具体的には液相を有する温度状態から900℃までの冷却速度を大きくすること(特許文献3)等が知られている。 Among the components that adversely affect the environment, methods for suppressing the elution of boron include, for example, a method of adding and mixing magnesium oxide in the form of powder or slurry to incineration ash containing boron (Patent Document 1 ), a method of humidifying and curing coal ash discharged from a thermal power plant for a predetermined period (Patent Document 2), and controlling the cooling rate of a boron-containing substance, specifically from a temperature state having a liquid phase to 900 ° C. It is known to increase the cooling rate up to (Patent Document 3).
しかし、特許文献1に記載された方法では、ホウ素の溶出抑制材として使用される酸化マグネシウムが高価であること、及び溶出抑制材を添加した混合物(最終生成物)が硬化して比較的高強度の塊状体となるため、これを資材とするための粒度調整に手間がかかることが問題となる。また、特許文献2に記載された方法では、ホウ素の溶出を抑制するために長期間の加湿養生が必要であり、特に、溶出量が多い石炭灰については、所期の溶出量とするためにより長期間の加湿養生を必要とするため、生産性が低いことが問題となる。 However, in the method described in Patent Document 1, the magnesium oxide used as the boron elution inhibitor is expensive, and the mixture (final product) to which the elution inhibitor is added hardens and has a relatively high strength. Since it becomes a lump of this, there is a problem that it takes time and effort to adjust the particle size for using this as a material. In addition, in the method described in Patent Document 2, long-term humidification curing is required in order to suppress the elution of boron. Low productivity is a problem because it requires long-term moisturizing and curing.
特許文献3に記載された方法は、簡便な操作によりホウ素溶出量の低減が可能なものであるが、これを経たホウ素含有物質からのホウ素溶出量が多くなることがあり、より信頼性の高いホウ素溶出量の低減方法が求められていた。 The method described in Patent Document 3 can reduce the amount of boron eluted by a simple operation, but the amount of boron eluted from the boron-containing substance may increase through this method, and is more reliable. A method for reducing the amount of eluted boron has been desired.
そこで、本発明は、前述の問題点を解決し、産業副産物を始めとするホウ素含有物質からのホウ素の溶出を抑制できる、簡便で信頼性の高い処理方法を提供することを目的とする。 Accordingly, an object of the present invention is to solve the above-mentioned problems and to provide a simple and highly reliable treatment method that can suppress the elution of boron from boron-containing substances such as industrial by-products.
本発明者は、前記課題を解決するために種々の検討を行ったところ、高温のホウ素含有物質を冷却する際に、その冷却速度を、より低温に至るまで、より厳密に制御することで、ホウ素溶出量が環境基準を満たすものとなることを見出し、本発明を完成するに至った。 The present inventor conducted various studies to solve the above problems, and found that when cooling a high-temperature boron-containing substance, by more strictly controlling the cooling rate to a lower temperature, The inventors have found that the amount of eluted boron satisfies environmental standards, and have completed the present invention.
前記課題を解決するための実施形態は以下の通りである。
[1]ホウ素含有物質の処理方法であって、液相を含む1100℃以上のホウ素含有物質を、1100℃に達してから750℃に至るまで、25℃/min以上の平均冷却速度にて冷却することを特徴とする、ホウ素含有物質の処理方法。
[2]前記冷却を、薄板状に流し出したホウ素含有物質に対して行う、前記[1]に記載のホウ素含有物質の処理方法。
[3]前記ホウ素含有物質のホウ素含有量が0.1質量%以上である、前記[1]又は[2]に記載のホウ素含有物質の処理方法。
[4]前記冷却に先立って、前記ホウ素含有物質の塩基度((質量%CaO)/(質量%SiO2))を1.20以下に調整する、前記[1]~[3]のいずれかに記載のホウ素含有物質の処理方法。
[5]前記塩基度の調整を、前記ホウ素含有物質の温度が1250℃以上の状態で、該ホウ素含有物質にSiO2を含有する改質材を添加することで行う、前記[4]に記載のホウ素含有物質の処理方法。
[6]前記冷却を、前記ホウ素含有物質の温度が1100℃から750℃に至るまでの全期間又は一部の期間、該ホウ素含有物質を強制冷却することで行う、前記[1]~[5]のいずれかに記載のホウ素含有物質の処理方法。
[7]土木建築用資材の製造方法であって、前記[1]~[6]のいずれかに記載のホウ素含有物質の処理方法によって得られたホウ素含有物質を原料として用いることを特徴とする、土木建築用資材の製造方法。
Embodiments for solving the above problems are as follows.
[1] A method for treating a boron-containing substance, in which a boron-containing substance containing a liquid phase and having a temperature of 1100°C or higher is cooled from 1100°C to 750°C at an average cooling rate of 25°C/min or higher. A method for treating a boron-containing substance, characterized by:
[2] The method for treating a boron-containing substance according to [1], wherein the cooling is performed on the boron-containing substance poured out in the form of a thin plate.
[3] The method for treating a boron-containing substance according to [1] or [2], wherein the boron content of the boron-containing substance is 0.1% by mass or more.
[4] Any one of [1] to [3], wherein the basicity ((% by mass CaO)/(% by mass SiO 2 )) of the boron-containing substance is adjusted to 1.20 or less prior to the cooling. 3. A method for treating a boron-containing substance according to .
[5] The above-mentioned [4], wherein the adjustment of the basicity is performed by adding a modifier containing SiO 2 to the boron-containing substance while the temperature of the boron-containing substance is 1250 ° C. or higher. method of treating boron-containing materials in.
[6] The above [1] to [5], wherein the cooling is performed by forcibly cooling the boron-containing substance during the entire period or part of the period until the temperature of the boron-containing substance reaches 1100 ° C. to 750 ° C. ] The method for treating a boron-containing substance according to any one of the above.
[7] A method for producing a material for civil engineering and construction, characterized in that a boron-containing substance obtained by the method for treating a boron-containing substance according to any one of [1] to [6] is used as a raw material. , a method for manufacturing materials for civil engineering and construction.
本発明によれば、産業副産物を始めとするホウ素含有物質からのホウ素の溶出を抑制できる、簡便で信頼性の高い処理方法を提供することができる。 According to the present invention, it is possible to provide a simple and highly reliable treatment method capable of suppressing elution of boron from boron-containing substances such as industrial by-products.
以下、本発明の各実施形態を詳細に説明するが、本発明は該各実施形態に限定されるものではない。また、以下に述べる作用機構については推定を含んでおり、その正否は、本発明を制限するものではない。なお、数値範囲の記載(2つの数値を「~」でつないだ記載)については、下限及び上限として記載された数値をも含む意味である。 Hereinafter, each embodiment of the present invention will be described in detail, but the present invention is not limited to each embodiment. In addition, the mechanism of action described below includes presumptions, and its correctness does not limit the present invention. It should be noted that the description of a numerical range (a description in which two numerical values are connected by "-") is meant to include numerical values described as lower and upper limits.
本発明者は、上述の課題を解決するための検討の過程で、ホウ素含有物質中のホウ素の分布を確認するため、ホウ素含有物質について、X線回折(XRD)測定結果に基づくガラス相比率の算出、電子線マイクロアナライザ(EPMA)によるホウ素の偏在状態の確認、及び透過型電子顕微鏡付属の電子エネルギー損失分光(TEM-EELS)装置によるガラス相へのホウ素の分配観察を実施した。その結果、ホウ素含有物質中のホウ素は、主としてガラス相領域に濃化していることが明らかとなった。 In the process of studying to solve the above-mentioned problems, the present inventors, in order to confirm the distribution of boron in the boron-containing substance, determined the glass phase ratio based on the X-ray diffraction (XRD) measurement results for the boron-containing substance. Calculation, confirmation of uneven distribution of boron with an electron probe microanalyzer (EPMA), and observation of boron distribution in the glass phase with an electron energy loss spectrometer (TEM-EELS) attached to a transmission electron microscope were carried out. As a result, it was found that boron in the boron-containing material was mainly concentrated in the glass phase region.
また、本発明者は、液相を有する状態のホウ素含有物質を高速冷却することで生成するガラス相が、900℃未満の温度域での徐冷によって結晶化することも確認した。 The inventors also confirmed that the glass phase produced by rapid cooling of the boron-containing substance in a liquid phase crystallizes by slow cooling in a temperature range of less than 900°C.
これらの結果によれば、液相を有する状態のホウ素含有物質を冷却する際に、900℃以下の温度域での冷却速度が遅いと、ガラス相が結晶化してその量が減少することで、ガラス相中のホウ素濃度が相対的に上昇し、冷却後のホウ素含有物質からのホウ素溶出量が増加するといえる。そうであれば、900℃未満の低温に至るまで高速冷却を継続することで、ガラス相の結晶化を抑制してホウ素溶出量の少ないホウ素含有物質が得られることになる。
後述する本発明の各実施形態は、こうした技術思想に基づくものである。
According to these results, when cooling the boron-containing substance in the state of having a liquid phase, if the cooling rate in the temperature range of 900 ° C. or less is slow, the glass phase will crystallize and the amount will decrease. It can be said that the boron concentration in the glass phase relatively increases, and the amount of boron eluted from the boron-containing substance after cooling increases. If so, by continuing high-speed cooling down to a low temperature of less than 900° C., crystallization of the glass phase is suppressed, and a boron-containing substance with a small amount of eluted boron can be obtained.
Each embodiment of the present invention to be described later is based on such a technical idea.
[ホウ素含有物質の処理方法]
本発明の一実施形態に係るホウ素含有物質の処理方法は、液相を含む1100℃以上のホウ素含有物質を、1100℃に達してから750℃に至るまで、25℃/min以上の平均冷却速度にて冷却することを特徴とする。
[Method for treating boron-containing substances]
A method for treating a boron-containing substance according to one embodiment of the present invention is a boron-containing substance containing a liquid phase of 1100 ° C. or higher, from 1100 ° C. to 750 ° C., at an average cooling rate of 25 ° C./min or more. It is characterized by cooling at
ホウ素含有物質は、ホウ素を含有するとともに、ホウ素の溶出が問題となる環境下に置かれ得るものであれば特に限定されない。ホウ素含有物質の例としては、製鉄所から発生する高炉スラグや製鋼スラグなどの鉄鋼スラグ、火力発電所から発生する石炭灰、廃棄物や下水汚泥の焼却灰等を高温で溶融し冷却・固化したスラグ等の各種スラグ、及びペーパースラッジ焼却灰等が挙げられる。 The boron-containing substance is not particularly limited as long as it contains boron and can be placed in an environment where elution of boron poses a problem. Examples of boron-containing substances include steel slag such as blast furnace slag and steelmaking slag generated from steel plants, coal ash generated from thermal power plants, and incinerated ash of waste and sewage sludge, etc., which are melted at high temperatures, cooled, and solidified. Various slags such as slag, and paper sludge incineration ash, etc., can be mentioned.
ホウ素含有物質は、1100℃以上の温度にあり、かつ液相を含む状態から冷却される。この状態のホウ素含有物質は、常温にあるものを加熱して得てもよく、溶融状態で生成したものをそのまま用いてもよい。ホウ素含有物質がスラグである場合には、一旦冷却され、凝固したものを再加熱して溶融状態としてもよい。 The boron-containing material is cooled from a temperature above 1100° C. and containing a liquid phase. The boron-containing substance in this state may be obtained by heating a substance at normal temperature, or may be used as it is produced in a molten state. If the boron-containing material is slag, it may be cooled and solidified and reheated to a molten state.
ホウ素含有物質の冷却は、これが1100℃に達してから750℃に至るまで、25℃/min以上の平均冷却速度にて行う。ここで、平均冷却速度とは、1100℃と750℃との温度差である350℃を、ホウ素含有物質が1100℃に達してから750℃になるまでの所要時間t(min)で割った値(350/t(℃/min))を意味する。平均冷却速度を25℃/min以上とすることで、結晶相の晶出を抑制し、冷却後のガラス相の比率を高めることができる。結晶相の晶出抑制効果を高める点からは、前記平均冷却速度は30℃/min以上とすることが好ましく、35℃/min以上とすることがより好ましい。前記平均冷却速度は、工業的に実現できる範囲で速いほど好ましいため、その上限値は限定されない。前記平均冷却速度が25℃/min未満では、結晶相の晶出抑制効果が小さいため、冷却後のガラス相の比率が低くなることで、ホウ素の溶出量が多くなる。高速冷却を行う温度範囲については、1100℃を超える温度にあるホウ素含有物質の冷却速度を高めても、結晶相の晶出抑制効果は限定的である。他方、750℃未満の温度では、晶出しうる結晶相が少量である上、高速冷却を実現するために、高価な装置を導入したり、大量の冷媒を使用したりする必要があるため、高速冷却の費用対効果が小さくなる。 Cooling of the boron-containing substance is carried out at an average cooling rate of 25°C/min or more from when it reaches 1100°C to 750°C. Here, the average cooling rate is a value obtained by dividing 350°C, which is the temperature difference between 1100°C and 750°C, by the required time t (min) for the boron-containing substance to reach 1100°C and reach 750°C. (350/t (°C/min)). By setting the average cooling rate to 25° C./min or higher, crystallization of the crystal phase can be suppressed and the ratio of the glass phase after cooling can be increased. The average cooling rate is preferably 30° C./min or higher, more preferably 35° C./min or higher, in order to enhance the effect of suppressing crystallization of the crystal phase. The average cooling rate is preferably as fast as possible within an industrially achievable range, so the upper limit is not limited. If the average cooling rate is less than 25° C./min, the effect of suppressing the crystallization of the crystal phase is small, so the ratio of the glass phase after cooling is low, and the elution amount of boron increases. Regarding the temperature range in which high-speed cooling is performed, even if the cooling rate of the boron-containing substance at a temperature exceeding 1100°C is increased, the effect of suppressing the crystallization of the crystal phase is limited. On the other hand, at temperatures below 750°C, the amount of crystalline phase that can be crystallized is small, and in order to achieve high-speed cooling, it is necessary to introduce expensive equipment or use a large amount of refrigerant, so the high-speed Cooling becomes less cost effective.
平均冷却速度を算出するための、ホウ素含有物質の測温位置は、冷却速度が最も遅く、冷却期間中最も高温となる箇所とする。該箇所を特定すると共に、前述の平均冷却速度を得るための冷却条件を決定するために、あらかじめ、冷却時のホウ素含有物質の形状及び寸法を測定すると共に、溶融状態のホウ素含有物質の初期温度、及び冷却中のホウ素含有物質における各位置での温度の経時変化を、熱電対等の測温手段により測定・記録し、温度が最も高い箇所が750℃以下になるまでの時間を把握しておくとよい。また、あらかじめ伝熱計算を行って、最も冷却速度が遅いと予想される箇所、及び該箇所における温度の経時変化を予測してもよい。温度が最も高い部分が750℃以下になるまでの時間、冷却手段にてホウ素含有物質を冷却し、ホウ素含有物質中のいずれの箇所においても25℃/min以上の平均冷却速度が確保されるようにする。例えば、ホウ素含有物質を溶融状態から冷却用容器に流し込んで冷却する際には、所期の平均冷却速度が得られるよう、ホウ素含有物質の厚みを薄くして流し込むとよい。 The temperature measurement position of the boron-containing substance for calculating the average cooling rate is the point where the cooling rate is the slowest and the temperature is the highest during the cooling period. In order to identify the location and determine the cooling conditions for obtaining the above-mentioned average cooling rate, the shape and dimensions of the boron-containing material during cooling are measured in advance, and the initial temperature of the boron-containing material in the molten state , and the temperature change over time at each position in the boron-containing substance during cooling is measured and recorded by temperature measuring means such as a thermocouple, and the time until the highest temperature point reaches 750 ° C. or less is grasped. Good. Alternatively, a heat transfer calculation may be performed in advance to predict a location where the cooling rate is expected to be the slowest and a time-dependent change in temperature at that location. The boron-containing material is cooled by a cooling means until the highest temperature part reaches 750 ° C. or less, and an average cooling rate of 25 ° C./min or more is secured at any point in the boron-containing material. to For example, when pouring a boron-containing substance from a molten state into a cooling vessel for cooling, the thickness of the boron-containing substance should be reduced so as to obtain a desired average cooling rate.
ホウ素含有物質の冷却方法は、上記平均冷却速度を満たすものであれば限定されず、自然冷却であってもよい。ただし、ホウ素含有物質の温度が低下するにつれ、冷却速度は低下する傾向にあるため、上記平均冷却速度を得るために、ホウ素含有物質を、これよりも十分に熱容量の大きな他の固体物質と接触させ、この固体物質を冷媒として自然冷却するとよい。例えば、ホウ素含有物質を鉄板上に流し込んで冷却する場合、スラグが有する熱量に対して鉄板が十分な冷却能を有するよう、鉄板の温度が低い状態でホウ素含有物質を流し込むようにしたり、厚い鉄板を使用したりするなどの対応をするとよい。また、上記の対応がとりにくい場合は、風冷・水冷等の強制冷却を行ってもよい。強制冷却の具体的な手法としては、流し込んだホウ素含有物質の表面に向けてロータリークーラー等の送風機で送風して冷却する方法、ミストノズルから水ミストを噴霧する方法、及びホウ素含有物質を流し込む容器を水冷する方法が例示される。これらの方法は、併用してもよい。なお、上記の強制冷却は、ホウ素含有物質の温度が750℃に至るまでの冷却中の全期間又は一部の期間に行うことができる。特に、ホウ素含有物質の温度が750℃に近い低温側で強制冷却を実施すると、ホウ素含有物質の温度が低下しても高い冷却速度を保持することができるため、より効果的である。 The method for cooling the boron-containing substance is not limited as long as it satisfies the above average cooling rate, and natural cooling may be used. However, as the temperature of the boron-containing substance decreases, the cooling rate tends to decrease. It is preferable to allow the solid substance to cool naturally as a coolant. For example, when pouring a boron-containing substance onto an iron plate to cool it, the boron-containing substance is poured into the iron plate while the temperature of the iron plate is low so that the iron plate has sufficient cooling power for the heat of the slag, or the iron plate is thick. It is better to take measures such as using In addition, if the above measures are difficult to take, forced cooling such as air cooling or water cooling may be performed. Specific methods of forced cooling include a method of cooling the surface of the poured boron-containing substance by blowing air with a blower such as a rotary cooler, a method of spraying water mist from a mist nozzle, and a container into which the boron-containing substance is poured. is exemplified by water cooling. These methods may be used in combination. The forced cooling described above can be performed during the entire period or part of the cooling period until the temperature of the boron-containing substance reaches 750°C. In particular, it is more effective to perform forced cooling at a low temperature side where the temperature of the boron-containing substance is close to 750° C., because a high cooling rate can be maintained even if the temperature of the boron-containing substance drops.
冷却を行う際のホウ素含有物質の形状も特に限定されないが、大量のホウ素含有物質を効率的にかつ低コストで冷却できると共に、冷却後の破砕及び粒度調整が容易である点で、薄板状とすることが好ましい。薄板状のホウ素含有物質は、液相を含むホウ素含有物質を、鉄板を始めとする金属板や、アルミナを始めとする耐火物上に流し出すことで形成できる。薄板状のホウ素含有物質の厚さとしては、冷却速度を高める点からは、100mm以下が例示される。該厚さは、80mm以下が好ましく、60mm以下がより好ましい。 The shape of the boron-containing substance during cooling is not particularly limited, either. preferably. A thin plate-like boron-containing substance can be formed by pouring a boron-containing substance containing a liquid phase onto a metal plate such as an iron plate or a refractory such as alumina. The thickness of the thin plate-like boron-containing substance is exemplified by 100 mm or less from the viewpoint of increasing the cooling rate. The thickness is preferably 80 mm or less, more preferably 60 mm or less.
本発明の一実施形態に係るホウ素含有物質の処理方法は、ホウ素含有量が0.1質量%以上のホウ素含有物質に適用すると、より大きな効果が得られる。このようなホウ素含有物質は、ガラス相の結晶化が起こった場合に、ホウ素溶出量が顕著に増加し、環境基準を超える虞が高いためである。ホウ素含有量の上限は限定されないが、産業副産物として生じるホウ素含有物質においては、通常、多くて0.5質量%である。 The method for treating a boron-containing substance according to one embodiment of the present invention is more effective when applied to a boron-containing substance having a boron content of 0.1% by mass or more. This is because such a boron-containing substance has a high possibility of exceeding the environmental standard because the amount of elution of boron increases remarkably when crystallization of the glass phase occurs. The upper limit of the boron content is not limited, but is usually at most 0.5% by weight in boron-containing substances occurring as industrial by-products.
本発明の一実施形態に係るホウ素含有物質の処理方法では、ホウ素含有物質の冷却に先立って、その塩基度を1.20以下に調整することが好ましい。これにより、冷却後のホウ素含有物質からのホウ素の溶出をさらに抑制することができる。ここで、ホウ素含有物質の塩基度は、質量%で表したSiO2含有量に対する、質量%で表したCaO含有量の比((質量%CaO)/(質量%SiO2))を意味する。塩基度の下限値については特に限定されない。このため、CaOをほとんど含まず、塩基度がほぼゼロとなるホウ素含有物質も処理対象とすることができる。 In the method for treating a boron-containing substance according to one embodiment of the present invention, it is preferable to adjust the basicity to 1.20 or less prior to cooling the boron-containing substance. Thereby, the elution of boron from the boron-containing substance after cooling can be further suppressed. Here, the basicity of the boron-containing material means the ratio of the CaO content in mass % to the SiO 2 content in mass % ((mass % CaO)/(mass % SiO 2 )). The lower limit of basicity is not particularly limited. Therefore, a boron-containing substance that contains almost no CaO and has a basicity of almost zero can also be treated.
前述の塩基度調整は、ホウ素含有物質の温度が1250℃以上の状態で、該ホウ素含有物質にSiO2を含有する改質材を添加することで行ってもよい。ホウ素含有物質の温度が1250℃以上の状態で改質材を添加することにより、改質材がホウ素含有物質の液相に充分溶解し、ホウ素含有物質の塩基度が均一に低下する。SiO2を含有する改質材を添加する際には、これを加熱溶融してから添加してもよい。これにより、SiO2を含有する改質材の添加に起因するホウ素含有物質の温度低下を抑制することができる。SiO2を含有する改質材としては、SiO2含有量が30質量%以上であり、ホウ素含有物質の液相に溶解するものを用いることが好ましい。これにより、処理後のホウ素含有物質からのホウ素の溶出を効果的に抑制できる。改質材中のSiO2含有量は、50質量%以上であることがより好ましく、70質量%以上であることがさらに好ましい。具体的な改質材としては、珪砂、廃ガラス及びろう石等が例示される。 The aforementioned basicity adjustment may be performed by adding a modifier containing SiO 2 to the boron-containing substance while the temperature of the boron-containing substance is 1250° C. or higher. By adding the modifier while the temperature of the boron-containing substance is 1250° C. or higher, the modifier is sufficiently dissolved in the liquid phase of the boron-containing substance, and the basicity of the boron-containing substance is uniformly lowered. When adding the modifier containing SiO 2 , it may be added after heating and melting. Thereby, it is possible to suppress the temperature drop of the boron-containing substance due to the addition of the modifier containing SiO 2 . As the modifier containing SiO 2 , it is preferable to use a material having a SiO 2 content of 30% by mass or more and being dissolved in the liquid phase of the boron-containing substance. This can effectively suppress the elution of boron from the boron-containing substance after treatment. The SiO 2 content in the modifier is more preferably 50% by mass or more, and even more preferably 70% by mass or more. Examples of specific modifiers include silica sand, waste glass, and pyrophyllite.
上記のように処理したホウ素含有物質は、常温まで冷却した後、常法による破砕及び篩分けで粒径2mm以下とし、環境庁告示46号試験によってホウ素の溶出を評価する。 The boron-containing substance treated as described above is cooled to room temperature, crushed and sieved by a conventional method to a particle size of 2 mm or less, and the elution of boron is evaluated by the Environment Agency Notification No. 46 test.
[土木建築用資材の製造方法]
本発明の他の形態に係る土木建築用資材の製造方法は、前述したホウ素含有物質の処理方法により得られた改質スラグを材料として使用することを特徴とする。
[Manufacturing method for civil engineering and construction materials]
A method for producing a material for civil engineering and construction according to another aspect of the present invention is characterized by using, as a material, the modified slag obtained by the above-described method for treating a boron-containing substance.
この実施形態では、ホウ素溶出が環境基準を満たすホウ素含有物質の粒度を、路盤材や地盤改良材等の土木建築用資材の用途に応じて調整することが好ましい。粒度調整の例として、ホウ素含有物質を路盤材に用いる場合に、ホウ素含有物質を40mm以下となるように破砕ないし篩い分けすることが挙げられる。 In this embodiment, it is preferable to adjust the particle size of the boron-containing substance whose boron elution satisfies the environmental standard according to the use of the civil engineering and construction materials such as roadbed materials and soil improvement materials. An example of particle size adjustment is crushing or sieving the boron-containing material to a size of 40 mm or less when the boron-containing material is used as a roadbed material.
以下、実施例により本発明をさらに具体的に説明するが、本発明は該実施例に限定されるものではない。 EXAMPLES The present invention will be described in more detail with reference to examples below, but the present invention is not limited to the examples.
[実施例1~4]
ホウ素含有物質として、表1に示す組成を有する4種類のスラグ(A~D)を準備した。これらのスラグは、金属製錬工程で常態的に発生するものである。なお、表1に示すスラグの組成は、普段の操業条件から推定したものである。
[Examples 1 to 4]
Four types of slag (A to D) having the compositions shown in Table 1 were prepared as boron-containing substances. These slags are normally generated in metal smelting processes. The composition of slag shown in Table 1 is estimated from normal operating conditions.
精錬工程で発生した直後で、1450℃程度の溶融状態にあったスラグA~Dを、鉄板の上に流し出して、その厚みが50mm以下になるよう薄く広げて冷却し、実施例1~4に係るスラグの処理を行った。鉄板は、(鉄板の熱容量)>{1.5×(流し出すスラグの熱容量)}となるよう選定し、冷却能を確保した。また、スラグを受ける前の鉄板の温度は500℃以下とした。スラグを流し出す際には、薄く広げたスラグの厚み方向の中央部分に熱電対を設置して、温度の経時変化を測定・記録し、その結果に基づいて平均冷却速度を算出した。その結果、いずれの実施例においても、1100~750℃における平均冷却速度が25℃/min以上となった。 Immediately after being generated in the refining process, the slag A to D in a molten state of about 1450 ° C. was poured onto an iron plate, spread thinly so that the thickness was 50 mm or less, and cooled, Examples 1 to 4. We processed the slag related to. The iron plate was selected so that (the heat capacity of the iron plate)>{1.5×(the heat capacity of the slag to be poured out)} to ensure the cooling performance. Also, the temperature of the iron plate before receiving the slag was 500° C. or lower. When pouring out the slag, a thermocouple was placed in the central portion of the thinly spread slag in the thickness direction to measure and record changes in temperature over time, and the average cooling rate was calculated based on the results. As a result, the average cooling rate at 1100 to 750° C. was 25° C./min or higher in any of the examples.
冷却後の各スラグについて、環境庁告示46号試験によってホウ素の溶出量を評価した。その結果、いずれのスラグについても、ホウ素の溶出量が自主基準値以下となり、合格(○)と判定された。 For each slag after cooling, the elution amount of boron was evaluated by the Environment Agency Notification No. 46 test. As a result, the amount of eluted boron in all slags was below the voluntary standard value, and the slag was determined to be acceptable (○).
[実施例5~7]
精錬工程で発生した直後で、1450℃程度の溶融状態にあったスラグA及びBに対して、珪砂をそれぞれ数質量%添加した以外は、前述の実施例1及び2と同様の方法で、実施例5及び6に係るスラグの処理を行った。また、精錬工程で発生した直後で、1450℃の溶融状態にあったスラグCに対しては、廃ガラスをあらかじめ加熱溶解してからスラグCに添加した以外は実施例3と同様の方法で、実施例7に係るスラグの処理を行った。珪砂または廃ガラスの添加により、スラグ中のSiO2含有量が増加し、スラグの塩基度が低下した。各実施例における1100~750℃における平均冷却速度は、いずれも25℃/min以上となった。
[Examples 5-7]
Executed in the same manner as in Examples 1 and 2 above, except that several mass % of silica sand was added to each of slags A and B that were in a molten state of about 1450 ° C. immediately after being generated in the refining process. Slag treatments according to Examples 5 and 6 were performed. In addition, for the slag C which was in a molten state of 1450° C. immediately after being generated in the refining process, the waste glass was heated and melted in advance and then added to the slag C in the same manner as in Example 3. The slag according to Example 7 was treated. The addition of silica sand or waste glass increased the SiO2 content in the slag and decreased the basicity of the slag. The average cooling rate at 1100 to 750°C in each example was 25°C/min or more.
処理後の各スラグについて、前述の実施例1~4と同様の方法で、ホウ素の溶出の合否を判定した。その結果、いずれのスラグについても、ホウ素の溶出量が自主基準値以下となり、合格(○)と判定された。 For each slag after the treatment, the elution of boron was determined in the same manner as in Examples 1 to 4 described above. As a result, the amount of eluted boron in all slags was below the voluntary standard value, and the slag was determined to be acceptable (○).
[比較例1~4]
鉄板上に流し出された各スラグを、冷却途中で鉄板から取り外し、同様に鉄板上で冷却されているスラグ上に堆積させ、さらにその上に冷却途中のスラグを堆積させて挟み込んだ以外は、前述の実施例1~4と同様の方法で、比較例1~4に係る処理を行った。なお、スラグで挟み込んだ後も、鉄板上に流し出した当初の厚み方向中央部での測温は継続した。各比較例では、1100~750℃における平均冷却速度が25℃/min未満となることが確認された。
[Comparative Examples 1 to 4]
Each slag poured out on the iron plate was removed from the iron plate during cooling, deposited on the slag that was similarly cooled on the iron plate, and further the slag during cooling was deposited on it and sandwiched. Treatments according to Comparative Examples 1 to 4 were performed in the same manner as in Examples 1 to 4 described above. In addition, even after sandwiching with slag, the temperature measurement was continued at the central portion in the thickness direction when it was first poured onto the iron plate. In each comparative example, it was confirmed that the average cooling rate at 1100 to 750°C was less than 25°C/min.
処理後の各スラグについて、前述の実施例1~4と同様の方法で、ホウ素の溶出の合否を判定した。その結果、いずれのスラグについても、ホウ素の溶出量が自主基準値を上回り、不合格(×)と判定された。 For each slag after the treatment, the elution of boron was determined in the same manner as in Examples 1 to 4 described above. As a result, the amount of eluted boron exceeded the voluntary standard value for all slags, and they were judged to be unacceptable (x).
実施例1~7及び比較例1~4に係るスラグの処理について、その条件及びホウ素溶出判定結果を、まとめて表2に示す。 Table 2 summarizes the conditions and boron elution determination results for the treatment of slag according to Examples 1 to 7 and Comparative Examples 1 to 4.
表2から、スラグを冷却する際に、1100℃に達してから750℃に至るまで、25℃/min以上の平均冷却速度にて冷却を行った実施例では、ホウ素の溶出量が自主基準値以下に抑えられることが判る。他方、冷却時に、1100℃~750℃での平均冷却速度が25℃/min未満となる比較例では、ホウ素の溶出量が自主基準値を超えることが判る。 From Table 2, in the example in which the slag was cooled from 1100 ° C. to 750 ° C. at an average cooling rate of 25 ° C./min or more, the elution amount of boron was the voluntary standard value. It turns out that it can be suppressed as follows. On the other hand, in the comparative examples in which the average cooling rate at 1100° C. to 750° C. is less than 25° C./min during cooling, the boron elution amount exceeds the voluntary standard value.
[実施例8~11]
ホウ素含有物質として、精錬工程で発生して放冷された後、電気炉で再加熱して1450℃の溶融状態としたスラグA~Dを用いた以外は上述の実施例1~4と同様の方法で、実施例8~11に係るスラグの処理を行った。
[Examples 8 to 11]
As the boron-containing substance, the same as in Examples 1 to 4 above except that slag A to D that was generated in the refining process and left to cool and then reheated in an electric furnace to a molten state of 1450 ° C. was used. The method was used to treat the slag according to Examples 8-11.
処理後の各スラグについて、上述の実施例1~4と同様の方法で、ホウ素の溶出量を評価した。その結果、同じ組成のスラグであれば、精錬工程から発生した直後の溶融スラグを処理した場合とホウ素の溶出量に差異はないことが確認された。 For each slag after treatment, the amount of eluted boron was evaluated in the same manner as in Examples 1 to 4 described above. As a result, it was confirmed that if the slag had the same composition, there was no difference in the amount of eluted boron from the molten slag immediately after being generated from the refining process.
本発明によれば、従来の処理方法ではホウ素の溶出量が環境基準を超えるホウ素含有物質について、ホウ素の溶出量を低減できる簡便で信頼性の高い方法が提供される。このため、ホウ素の溶出量が環境基準を超えることのみを理由として再利用ができなかったホウ素含有物質の再利用が可能となる点、及び同じ理由により最終処分時に別途処置が必要であったホウ素含有物質について、該処置を省略して簡便に最終処分が可能となる点で、本発明は有用なものである。 According to the present invention, there is provided a simple and highly reliable method capable of reducing the amount of elution of boron from a boron-containing substance for which the amount of elution of boron exceeds the environmental standard by a conventional treatment method. For this reason, it is possible to reuse boron-containing substances that could not be reused only because the amount of eluted boron exceeds environmental standards, and for the same reason, boron that had to be treated separately at the time of final disposal. The present invention is useful in that the contained substance can be simply disposed of by omitting the treatment.
Claims (7)
液相を含む1100℃以上のホウ素含有物質を、1100℃に達してから750℃に至るまで、25℃/min以上(ただし、100℃/min以上を除く)の平均冷却速度にて冷却することを特徴とする、
ホウ素含有物質の処理方法。 A method for treating a boron-containing material, comprising:
Cooling a boron-containing substance containing a liquid phase of 1100° C. or higher from 1100° C. to 750° C. at an average cooling rate of 25° C./min or more (excluding 100° C./min or more) characterized by
A method for treating boron-containing substances.
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| JP2004255233A (en) | 2003-02-24 | 2004-09-16 | Dowa Mining Co Ltd | Method of treating boron-containing waste |
| JP2004315296A (en) | 2003-04-16 | 2004-11-11 | Jfe Steel Kk | Prevention method of powdered Cr-containing alloyed steel slag |
| JP2006334502A (en) | 2005-06-01 | 2006-12-14 | Sanbic:Kk | Method and apparatus for purification of contaminated soil |
| JP2020132485A (en) | 2019-02-21 | 2020-08-31 | Jfeスチール株式会社 | Slug, production method of slug, and civil engineering material |
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| JP2004255233A (en) | 2003-02-24 | 2004-09-16 | Dowa Mining Co Ltd | Method of treating boron-containing waste |
| JP2004315296A (en) | 2003-04-16 | 2004-11-11 | Jfe Steel Kk | Prevention method of powdered Cr-containing alloyed steel slag |
| JP2006334502A (en) | 2005-06-01 | 2006-12-14 | Sanbic:Kk | Method and apparatus for purification of contaminated soil |
| JP2020132485A (en) | 2019-02-21 | 2020-08-31 | Jfeスチール株式会社 | Slug, production method of slug, and civil engineering material |
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