JP2001310175A - Method for insolubilization treatment of boron contained in soil or incineration ash - Google Patents

Method for insolubilization treatment of boron contained in soil or incineration ash

Info

Publication number
JP2001310175A
JP2001310175A JP2000133677A JP2000133677A JP2001310175A JP 2001310175 A JP2001310175 A JP 2001310175A JP 2000133677 A JP2000133677 A JP 2000133677A JP 2000133677 A JP2000133677 A JP 2000133677A JP 2001310175 A JP2001310175 A JP 2001310175A
Authority
JP
Japan
Prior art keywords
soil
boron
ash
incineration ash
incinerated 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.)
Pending
Application number
JP2000133677A
Other languages
Japanese (ja)
Inventor
Shigeru Hayashibara
茂 林原
Fukashi Oguchi
深志 小口
Takeshi Ishiguro
健 石黒
Katsuhiko Hayashi
克彦 林
Toshiyuki Otake
利幸 大竹
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.)
Maeda Corp
Original Assignee
Maeda Corp
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 Maeda Corp filed Critical Maeda Corp
Priority to JP2000133677A priority Critical patent/JP2001310175A/en
Publication of JP2001310175A publication Critical patent/JP2001310175A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/10Production of cement, e.g. improving or optimising the production methods; Cement grinding
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

Abstract

PROBLEM TO BE SOLVED: To provide a method for insolubilization treatment of boron contained in soil or incineration ash, capable of suppressing the elution of boron from soil in the vicinity of farmland or incineration ash. SOLUTION: Soil or incineration ash containing boron, for example, coal ash is solidified with blast furnace slag B cement being a solidifying material or fixed with a fixing material to suppress the elution of boron.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、土壌又は焼却灰
(スラグを含む)に含まれるホウ素の不溶化処理方法に
関し、更に詳細には、雨水などが潅漑用水に流れ込む地
域の土壌、或いは、火力発電所、製鉄所、ゴミ焼却所な
どから排出される焼却灰などに好適なホウ素の不溶化処
理方法に関する。
[0001] The present invention relates to a method for insolubilizing boron contained in soil or incinerated ash (including slag), and more particularly to soil in an area where rainwater or the like flows into irrigation water or thermal power generation. The present invention relates to a method for insolubilizing boron, which is suitable for incineration ash discharged from a steel plant, a steel mill, a garbage incineration plant, or the like.

【0002】[0002]

【従来の技術】ホウ素を含有する土壌からホウ素が溶出
し、潅漑用水に混入するような地域では、植物がホウ素
を多量に摂取して植物の生長を阻害することが知られて
いる。そこで、ホウ素を含有する土壌を後背地に持つ地
域では、ホウ素の不溶化技術が重要な役割を果たすよう
になると考えられる。
2. Description of the Related Art In an area where boron is eluted from boron-containing soil and mixed with irrigation water, it is known that plants ingest a large amount of boron and inhibit the growth of the plants. Therefore, it is thought that boron insolubilization technology will play an important role in areas where the soil containing boron is hinterland.

【0003】一方、火力発電所、製鉄所、ゴミ焼却所な
どでは大量に発生する焼却灰を埋め立てているが、この
焼却灰にもホウ素が含有されており、これが溶出して植
物に悪影響を与えることが心配される。また、焼却灰を
埋め立てる埋め立て処分場は不足しており、処分場を増
やすことによる環境負荷を低減するため、副産物である
焼却灰の有効利用を図ることが望まれている。
On the other hand, in a thermal power plant, a steel mill, a garbage incineration plant and the like, a large amount of incinerated ash is landfilled, and this incinerated ash also contains boron, which elutes and has an adverse effect on plants. I am worried. In addition, there is a shortage of landfill sites for landfilling incineration ash, and it is desired to effectively use incineration ash, a by-product, in order to reduce the environmental impact of increasing the number of disposal sites.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、従来
は、土壌又は焼却灰に含まれるホウ素の不溶化処理は何
ら実施されていなかったので、これらの土壌又は焼却灰
からホウ素が溶出し、潅漑用水などを介して農地にホウ
素が多量に流れ込んでしまい、農産物に被害が出るおそ
れがあった。また、ホウ素を含有したままの焼却灰は、
有効利用も困難であり、廃棄せざるを得なかったため、
埋め立て処分場の制限などによる廃棄処理上の問題も抱
えたままであった。
However, conventionally, no insolubilization treatment of boron contained in soil or incineration ash has been performed, so that boron is eluted from these soils or incineration ash, and irrigation water and the like are removed. A large amount of boron would flow into farmland through the plant, and there was a risk that agricultural products would be damaged. In addition, incineration ash containing boron is
It was difficult to use it effectively, and we had to discard it.
Problems with disposal due to restrictions on landfill sites remained.

【0005】そこで、本発明は、潅漑用水路付近の土壌
や、火力発電所などから排出される焼却灰からホウ素が
溶出するのを抑制でき、これにより、ホウ素による農産
物の生育障害を未然に防止できると共に、焼却灰の有効
利用が可能な土壌又は焼却灰に含まれるホウ素の不溶化
処理方法を提供することを目的とする。
[0005] Therefore, the present invention can suppress the elution of boron from soil near the irrigation canal or incineration ash discharged from a thermal power plant or the like, thereby preventing the growth failure of agricultural products due to boron. In addition, an object of the present invention is to provide a method for insolubilizing boron contained in soil or incinerated ash in which incinerated ash can be effectively used.

【0006】[0006]

【課題を解決するための手段】本発明は土壌又は焼却灰
に含まれるホウ素の不溶化処理方法であり、前述の技術
的課題を解決するために以下のように構成されている。
すなわち、本発明は、ホウ素を含む土壌又は焼却灰を固
化材料によって固化するか、或いは固着材料によって固
着することにより、前記ホウ素の溶出を抑制することを
特徴とする。
SUMMARY OF THE INVENTION The present invention relates to a method for insolubilizing boron contained in soil or incinerated ash, and is constituted as follows in order to solve the above-mentioned technical problems.
That is, the present invention is characterized in that the elution of the boron is suppressed by solidifying the soil or incinerated ash containing boron with a solidifying material or fixing with a fixing material.

【0007】固化材料としては、カルシウム系材料、ア
ルカリ材料、非晶質アルミナ、又は活性アルミナのうち
少なくとも何れか1つを用いることができる。また、固
着材料としては、ゼオライト、アロフエン、又はベント
ナイトのうち少なくとも何れか1つを用いることができ
る。土壌又は焼却灰に固化材料又は固着材料が含まれて
いるときは、加熱することにより固化又は固着すること
ができる。
As the solidifying material, at least one of a calcium-based material, an alkali material, amorphous alumina, and activated alumina can be used. Further, as the fixing material, at least one of zeolite, allophane, and bentonite can be used. When the soil or the incineration ash contains a solidified material or a fixing material, it can be solidified or fixed by heating.

【0008】[0008]

【発明の実施の形態】以下、本発明に係る土壌又は焼却
灰に含まれるホウ素の不溶化処理方法の実施の形態につ
いて、図面を参照して詳細に説明する。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments of the method for insolubilizing boron contained in soil or incinerated ash according to the present invention will be described below in detail with reference to the drawings.

【0009】本発明は、ホウ素による汚染土壌、又は火
力発電所、製鉄所、ゴミ焼却所などから排出されるホウ
素を含む焼却灰を、固化材料によって固化することによ
り、或いは固着材料によって固着することにより、ホウ
素の溶出を抑制するものである。ここでは、焼却灰には
スラグも含むものとする。
According to the present invention, there is provided a method of solidifying boron-contaminated soil or incinerated ash containing boron discharged from a thermal power plant, a steel mill, a garbage incinerator, or the like with a solidifying material, or fixing with a fixing material. This suppresses the elution of boron. Here, the incinerated ash includes slag.

【0010】固化材料又は固着材料は、通常は土壌又は
焼却灰に別に添加して混合させるが、土壌又は焼却灰に
もともと含まれている場合もあり、この場合には、別に
添加する必要はなく、土壌又は焼却灰に水を加えて加熱
するだけで固化することができる。
[0010] The solidified material or the fixing material is usually added separately to the soil or incinerated ash and mixed therewith, but it may be originally contained in the soil or incinerated ash. In this case, it is not necessary to add it separately. It can be solidified simply by adding water to soil or incinerated ash and heating.

【0011】固化材料としては、カルシウム系材料、ア
ルカリ材料、非晶質アルミナ、又は活性アルミナを含む
材料などを使用できる。このうち、カルシウム系材料と
しては、セメント、石灰、石膏、炭酸カルシウムなどが
あり、これらの材料はそれ自体の固化作用を期待するも
のである。
As the solidified material, a calcium-based material, an alkali material, a material containing amorphous alumina or activated alumina can be used. Among them, calcium-based materials include cement, lime, gypsum, calcium carbonate, and the like, and these materials are expected to have their own solidifying action.

【0012】また、固化材料の中には、アルカリ刺激を
与えないと固化しないものが比較的多いが、このような
材料にアルカリ刺激を加える材料、すなわち、固化作用
の助剤となりうるアルカリ材料としては、ソーダ灰、苛
性ソーダ、苛性カリウム、ケイ酸ソーダなどがある。
In addition, although there are relatively many solidifying materials which do not solidify unless an alkali stimulus is applied, such materials are those which apply an alkali stimulus to such a material, that is, alkali materials which can serve as an auxiliary for the solidification action. Examples include soda ash, caustic soda, caustic potassium, and sodium silicate.

【0013】また、非晶質アルミナ若しくは活性アルミ
ナを含む材料としては、アルミン酸ソーダ、アルミン酸
カリウム、高炉スラグ、製紙焼却灰、都市ゴミ焼却灰、
下水汚泥焼却灰、石炭灰、ゼオライト、アロフェン、ベ
ントナイトなどがある。
Materials containing amorphous alumina or activated alumina include sodium aluminate, potassium aluminate, blast furnace slag, paper incineration ash, municipal waste incineration ash,
There are sewage sludge incineration ash, coal ash, zeolite, allophane, bentonite and the like.

【0014】このうち、アルミン酸ソーダ,アルミン酸
カリウムは、固化作用の助剤としての効果があるといわ
れている。また、高炉スラグ,製紙焼却灰,都市ゴミ焼
却灰,下水汚泥焼却灰,石炭灰は、ホウ素を内在するが
それ自体で固化作用がある。更に、ゼオライト、アロフ
ェン、ベントナイトは、固着作用がある。
Of these, sodium aluminate and potassium aluminate are said to have an effect as a solidification aid. Blast furnace slag, papermaking incineration ash, municipal garbage incineration ash, sewage sludge incineration ash, and coal ash contain boron but have a solidifying action by itself. Furthermore, zeolites, allophane and bentonite have a sticking action.

【0015】これらの固化材料及び固着材料は、それぞ
れ単独で使用することができるが、土壌又は焼却灰の特
性に応じて複数種類を複合させて使用することもでき
る。これらの固化材料又は固着材料は、通常、固化すべ
き土壌又は焼却灰に水と一緒に添加して混合させる。そ
して、常温又は加熱による高温で一定期間養生すること
により、固化させる。また、固化すべき土壌又は焼却灰
に、上記の固化材料が含まれている場合には、土壌又は
焼却灰に水を加えて、常温又は加熱による高温で一定期
間養生することにより、固化又は固着することができ
る。
These solidifying materials and fixing materials can be used alone, but a plurality of types can be used in combination according to the characteristics of soil or incinerated ash. These solidifying or fixing materials are usually added to the soil or incineration ash to be solidified together with water and mixed. Then, it is cured by curing at a room temperature or a high temperature by heating for a certain period. If the above-mentioned solidified material is contained in the soil or incineration ash to be solidified, water is added to the soil or incineration ash and the mixture is cured at room temperature or high temperature by heating for a certain period of time to solidify or fix. can do.

【0016】一方、焼却灰には生石灰が含まれている
が、これ以外にも、水と反応して固化するポゾラン物質
を含むことがある。この場合には、焼却灰を水に溶かし
た状態で、常温から200℃で加熱することにより、別
に固化材料を加えることなく、固化反応を促進させて固
化することができる。
On the other hand, incinerated ash contains quicklime, but may also contain pozzolanic substances which solidify by reacting with water. In this case, by heating the incinerated ash in a state of being dissolved in water from room temperature to 200 ° C., the solidification reaction can be accelerated and solidified without adding a solidified material separately.

【0017】このホウ素の不溶化処理方法を、潅漑用水
の付近にある土壌に適用する場合には、浅層安定処理に
よって実施することができる。この浅層安定処理とは、
一般的に地表面下数m程度までを対象として行うもので
あり、例えばトラクターなどを利用して、上述の固化材
料を土壌に混合させることができる。
When this boron insolubilization method is applied to soil near irrigation water, it can be implemented by shallow layer stabilization. This shallow layer stabilization processing
Generally, the process is performed for a few meters below the ground surface. For example, the above-mentioned solidified material can be mixed with the soil using a tractor or the like.

【0018】また、火力発電所などから海中投棄された
焼却灰などに本発明を適用する場合には、深層混合工法
によって実施することができる。深層混合工法は、地盤
改良などを目的として地盤の深部を固結する方法であ
り、例えば海中の焼却灰にノズルを差し込み、このノズ
ルから水平方向に固化材料、例えばセメントミルクなど
を噴射することにより焼却灰を固化することができる。
Further, when the present invention is applied to incinerated ash discarded in the sea from a thermal power plant or the like, it can be implemented by a deep mixing method. The deep mixing method is a method of solidifying the deep part of the ground for the purpose of ground improvement, etc., for example, by inserting a nozzle into incinerated ash in the sea, and spraying a solidified material, such as cement milk, etc. horizontally from this nozzle. The incineration ash can be solidified.

【0019】土壌又は焼却灰を加熱する場合には、ヒー
タ自体を土壌又は焼却灰に打ち込んで直接加熱するか、
或いはH型鋼などを土壌又は焼却灰に打ち込んで、H型
鋼をヒータで加熱することにより間接的に加熱すること
ができる。
When heating the soil or incinerated ash, the heater itself is driven into the soil or incinerated ash,
Alternatively, it is possible to indirectly heat the H-shaped steel by driving the H-shaped steel into a soil or incineration ash and heating the H-shaped steel with a heater.

【0020】[0020]

【実施例1】図1に示すように、ミキサー10に、火力
発電所から排出されたホウ素を含有する石炭灰11を投
入し、更に固化材料として高炉スラグBセメント12を
添加後、水13を加えて撹拌翼14を回転させ、7日間
の養生を行った。そして、環境庁告示46号に基づくホ
ウ素の溶出試験を行った結果、図2に示すような結果を
得た。
EXAMPLE 1 As shown in FIG. 1, a coal ash 11 containing boron discharged from a thermal power plant is put into a mixer 10, and a blast furnace slag B cement 12 is added as a solidifying material. In addition, the stirring blade 14 was rotated to perform curing for 7 days. Then, as a result of performing a boron elution test based on the notification of the Environment Agency No. 46, a result as shown in FIG. 2 was obtained.

【0021】図2から分かるように、固化材料として高
炉スラグBセメント12を配合しなかったときには、石
炭灰11のホウ素溶出量が7.81mg/lであった
が、高炉スラグBセメント12の配合比率が増加するに
つれて、ホウ素溶出量が減少し、ここでは最大95%低
減することができた。また、高炉スラグBセメント12
の配合比率が高くなるほど一軸圧縮強度も増加している
ことが分かる。このように、保管中の石炭灰の地盤修復
やホウ素を含む発生灰の不溶化を図ることによる発生灰
の有効利用ができる。
As can be seen from FIG. 2, when the blast furnace slag B cement 12 was not blended as a solidifying material, the amount of boron eluted from the coal ash 11 was 7.81 mg / l. As the ratio increased, the boron elution amount decreased, where it could be reduced by up to 95%. In addition, blast furnace slag B cement 12
It can be seen that the uniaxial compressive strength increases as the blending ratio of becomes higher. As described above, the generated ash can be effectively used by repairing the ground of the coal ash during storage and insolubilizing the generated ash containing boron.

【0022】[0022]

【実施例2】図3に示すように、ポゾラン物質を含む石
炭灰15に飽和する程度に加水後、モールド(型枠)1
6に投入し、これを乾燥炉17内に入れて、約80℃で
28日間に亘って加熱した。その後、環境庁告示46号
に基づくホウ素の溶出試験を行った結果、図4に示すよ
うに、ホウ素の溶出が抑制されることを確認した。本実
施例では、ホウ素の溶出量を約77%低減できた。
Embodiment 2 As shown in FIG. 3, after adding water to such an extent that coal ash 15 containing a pozzolanic substance is saturated, a mold (form) 1
6 and placed in a drying oven 17 and heated at about 80 ° C. for 28 days. Thereafter, as a result of a boron elution test based on the Environment Agency Notification No. 46, it was confirmed that boron elution was suppressed as shown in FIG. In this example, the elution amount of boron was reduced by about 77%.

【0023】[0023]

【発明の効果】以上説明したように、本発明によれば、
火力発電所などから排出される焼却灰や、農地の後背地
の土壌などに含有されるホウ素の溶出を抑制できるの
で、ホウ素が潅漑用水を介して農産物に過剰に摂取され
るのを防止でき、これによって、農業被害を未然に防止
できる。
As described above, according to the present invention,
Since the incineration ash discharged from thermal power plants and the elution of boron contained in the soil behind the farmland can be suppressed, it is possible to prevent boron from being excessively taken into agricultural products via irrigation water, This can prevent agricultural damage.

【0024】また、本発明によれば、保管中の石炭灰の
地盤修復やホウ素を含む発生灰の不溶化を図ることによ
る発生灰の有効利用ができ、従来のように、焼却灰の廃
棄処理費用が不要となるため、経費節減が可能になると
共に、焼却場の増大を抑制でき、環境的にも有利にな
る。
Further, according to the present invention, it is possible to effectively utilize generated ash by repairing the ground of coal ash during storage and insolubilizing generated ash containing boron. This eliminates the need for smelting, so that costs can be reduced and the increase in incineration plants can be suppressed, which is environmentally advantageous.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の第1実施例を説明する図である。FIG. 1 is a diagram illustrating a first embodiment of the present invention.

【図2】本発明の第1実施例の試験結果を示す図であ
る。
FIG. 2 is a diagram showing test results of the first embodiment of the present invention.

【図3】本発明の第2実施例を説明する図である。FIG. 3 is a diagram illustrating a second embodiment of the present invention.

【図4】本発明の第2実施例の試験結果を示す図であ
る。
FIG. 4 is a diagram showing test results of a second example of the present invention.

【符号の説明】[Explanation of symbols]

11 石炭灰(焼却灰) 12 高炉スラグBセメント(固化材料) 15 ポゾラン物質を含む石炭灰(焼却灰) 11 Coal ash (incineration ash) 12 Blast furnace slag B cement (solidified material) 15 Coal ash containing pozzolanic substances (incineration ash)

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) //(C04B 28/00 C04B 7:14 7:14 22:08 A 22:08 Z 22:06 Z 22:06 14:10 Z 14:10 14:04 Z 14:04 14:30) 14:30) 103:60 103:60 111:20 111:20 B09B 3/00 ZAB (72)発明者 石黒 健 東京都千代田区富士見二丁目10番26号前田 建設工業株式会社内 (72)発明者 林 克彦 東京都千代田区富士見二丁目10番26号前田 建設工業株式会社内 (72)発明者 大竹 利幸 東京都千代田区富士見二丁目10番26号前田 建設工業株式会社内 Fターム(参考) 4D004 AA36 AA41 AA43 AB05 AC07 CA15 CA22 CA45 CB27 CB32 CC03 CC11 CC13 4G012 PA01 PA26 PA35 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) // (C04B 28/00 C04B 7:14 7:14 22:08 A 22:08 Z 22:06 Z 22 : 06 14:10 Z 14:10 14:04 Z 14:04 14:30) 14:30) 103: 60 103: 60 111: 20 111: 20 B09B 3/00 ZAB (72) Inventor Takeshi Ishiguro Tokyo (10) Maeda Construction Industry Co., Ltd., 2-10-26 Fujimi, Chiyoda-ku (72) Inventor Katsuhiko Hayashi Inside (2) Maeda Construction Industry Co., Ltd. 2-10-26, Fujimi, Chiyoda-ku, Tokyo 2-10-10 Fujimi Maeda Construction Industry Co., Ltd. F-term (reference) 4D004 AA36 AA41 AA43 AB05 AC07 CA15 CA22 CA45 CB27 CB32 CC03 CC11 CC13 4G012 PA01 PA26 PA35

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 ホウ素を含む土壌又は焼却灰を、固化材
料によって固化するか、或いは固着材料によって固着す
ることにより、前記ホウ素の溶出を抑制することを特徴
とする土壌又は焼却灰に含まれるホウ素の不溶化処理方
法。
1. Boron contained in soil or incinerated ash, characterized in that the soil or incinerated ash containing boron is solidified by a solidifying material or fixed by a fixing material to suppress the elution of the boron. Insolubilization treatment method.
【請求項2】 前記固化材料は、カルシウム系材料、ア
ルカリ材料、非晶質アルミナ、又は活性アルミナのうち
少なくとも何れか1つを含み、前記固着材料は、ゼオラ
イト、アロフエン、又はベントナイトのうち少なくとも
何れか1つを含むことを特徴とする請求項1に記載の土
壌又は焼却灰に含まれるホウ素の不溶化処理方法。
2. The solidifying material includes at least one of a calcium-based material, an alkali material, amorphous alumina, and activated alumina, and the fixing material includes at least one of zeolite, allophane, and bentonite. The method for insolubilizing boron contained in soil or incinerated ash according to claim 1, comprising:
【請求項3】 前記土壌又は焼却灰に前記固化材料又は
前記固着材料が含まれている場合には、前記土壌又は焼
却灰を加熱することにより固化又は固着することを特徴
とする請求項1または2に記載の土壌又は焼却灰に含ま
れるホウ素の不溶化処理方法。
3. The method according to claim 1, wherein when the solidified material or the fixing material is contained in the soil or the incinerated ash, the soil or the incinerated ash is solidified or fixed by heating the soil or the incinerated ash. 3. The method for insolubilizing boron contained in soil or incinerated ash according to 2.
【請求項4】 前記焼却灰は、火力発電所、製鉄所、又
はゴミ焼却所から排出される焼却灰であることを特徴と
する請求項1〜3の何れかに記載の土壌又は焼却灰に含
まれるホウ素の不溶化処理方法。
4. The soil or incineration ash according to claim 1, wherein the incineration ash is incineration ash discharged from a thermal power plant, a steel mill, or a garbage incineration plant. A method for insolubilizing boron contained.
JP2000133677A 2000-05-02 2000-05-02 Method for insolubilization treatment of boron contained in soil or incineration ash Pending JP2001310175A (en)

Priority Applications (1)

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JP2000133677A JP2001310175A (en) 2000-05-02 2000-05-02 Method for insolubilization treatment of boron contained in soil or incineration ash

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000133677A JP2001310175A (en) 2000-05-02 2000-05-02 Method for insolubilization treatment of boron contained in soil or incineration ash

Publications (1)

Publication Number Publication Date
JP2001310175A true JP2001310175A (en) 2001-11-06

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Country Link
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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005270790A (en) * 2004-03-24 2005-10-06 Toda Kogyo Corp Adsorbent adsorbing fluorine and/or boron
JP2006026511A (en) * 2004-07-15 2006-02-02 Oji Paper Co Ltd Method for treating boron-containing combustion ash
JP2006305543A (en) * 2005-03-29 2006-11-09 Kurita Water Ind Ltd In-situ confining method
JP2007090155A (en) * 2005-09-27 2007-04-12 Shimizu Corp Method of controlling leaching out of boron from coal ash
JP2008273997A (en) * 2007-01-12 2008-11-13 Chugoku Electric Power Co Inc:The Elution inhibitor for controlling elution of harmful trace element, method for controlling elution and method for combustion of dust coal
JP2015178098A (en) * 2014-02-27 2015-10-08 Jfeスチール株式会社 Method of suppressing boron elution from boron-containing substance and boron elution reformation treated material

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6351520B2 (en) * 1982-07-22 1988-10-14 Jgc Corp
JPH02164488A (en) * 1988-12-20 1990-06-25 Mitsubishi Heavy Ind Ltd Treatment of waste water containing boron
JPH11118990A (en) * 1997-10-14 1999-04-30 Hitachi Ltd Method for treating radioactive liquid waste

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6351520B2 (en) * 1982-07-22 1988-10-14 Jgc Corp
JPH02164488A (en) * 1988-12-20 1990-06-25 Mitsubishi Heavy Ind Ltd Treatment of waste water containing boron
JPH11118990A (en) * 1997-10-14 1999-04-30 Hitachi Ltd Method for treating radioactive liquid waste

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005270790A (en) * 2004-03-24 2005-10-06 Toda Kogyo Corp Adsorbent adsorbing fluorine and/or boron
JP4715991B2 (en) * 2004-03-24 2011-07-06 戸田工業株式会社 Adsorbent that adsorbs fluorine and / or boron
JP2006026511A (en) * 2004-07-15 2006-02-02 Oji Paper Co Ltd Method for treating boron-containing combustion ash
JP2006305543A (en) * 2005-03-29 2006-11-09 Kurita Water Ind Ltd In-situ confining method
JP4572761B2 (en) * 2005-03-29 2010-11-04 栗田工業株式会社 In-situ containment method and in-situ containment device
JP2007090155A (en) * 2005-09-27 2007-04-12 Shimizu Corp Method of controlling leaching out of boron from coal ash
JP2008273997A (en) * 2007-01-12 2008-11-13 Chugoku Electric Power Co Inc:The Elution inhibitor for controlling elution of harmful trace element, method for controlling elution and method for combustion of dust coal
JP2015178098A (en) * 2014-02-27 2015-10-08 Jfeスチール株式会社 Method of suppressing boron elution from boron-containing substance and boron elution reformation treated material

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