JP2006116389A - Fixing method for boron and fluorine and fixing agent composition - Google Patents

Fixing method for boron and fluorine and fixing agent composition Download PDF

Info

Publication number
JP2006116389A
JP2006116389A JP2004305006A JP2004305006A JP2006116389A JP 2006116389 A JP2006116389 A JP 2006116389A JP 2004305006 A JP2004305006 A JP 2004305006A JP 2004305006 A JP2004305006 A JP 2004305006A JP 2006116389 A JP2006116389 A JP 2006116389A
Authority
JP
Japan
Prior art keywords
group
boron
fluorine
compound
chloride
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
JP2004305006A
Other languages
Japanese (ja)
Inventor
Shiyuuichi Niue
修一 仁上
Kazuo Hosoda
和夫 細田
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.)
Miyoshi Yushi KK
Miyoshi Oil and Fat Co Ltd
Original Assignee
Miyoshi Yushi KK
Miyoshi Oil and Fat Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Miyoshi Yushi KK, Miyoshi Oil and Fat Co Ltd filed Critical Miyoshi Yushi KK
Priority to JP2004305006A priority Critical patent/JP2006116389A/en
Publication of JP2006116389A publication Critical patent/JP2006116389A/en
Pending legal-status Critical Current

Links

Abstract

<P>PROBLEM TO BE SOLVED: To provide a fixing method for boron and fluorine capable of certainly capturing and fixing boron and fluorine, and to obtain a fixing agent composition. <P>SOLUTION: The fixing method for boron and fluorine is characterized in that at least one kind (A) selected from the group consisting of a compound of a rare-earth element and a compound of a group 4 element; and an aluminum compound (B) are added to an object to be treated and boron and/or fluorine in the object to be treated is fixed. The fixing agent for boron and fluorine comprises at least one kind (A) selected from the group consisting of the compound of the rare-earth element and the compound of the group 4 element; and the aluminum compound (B). <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、ホウ素、フッ素の固定化方法及び固定化剤組成物に関する。   The present invention relates to a method for immobilizing boron and fluorine, and an immobilizing agent composition.

焼却灰、焼却飛灰、溶融飛灰、溶融スラグ、石炭灰、鉱滓、汚泥、汚染土壌、シュレッダーダスト、工場から排出される廃水、埋立処分場の地下汚染水等には種々の有害物質が含有されており、人体に有害な重金属類が地下水、河川、海水に溶出すると重大な環境汚染を生じる虞がある。このため重金属の溶出量を一定値以下に規制したり、水中の重金属量を一定値以下に規制する種々の法律が定められている。従来より、飛灰等の固体状廃棄物中の重金属類を固定化して溶出を防止したり、廃水中の重金属類を捕集して除去する目的で、ジチオカルバミン酸基、リン酸基、カルボン酸基、カルバミン酸基、ジチオ酸基、アミノ燐酸基、チオール基、ザンセート基等の官能基を有する金属捕集剤で重金属類を固定化することが提案されている(特許文献1〜9等)。   Incinerated ash, incinerated fly ash, molten fly ash, molten slag, coal ash, slag, sludge, contaminated soil, shredder dust, wastewater discharged from factories, underground contaminated water in landfills, etc. contain various harmful substances If heavy metals harmful to the human body are eluted into groundwater, rivers and seawater, serious environmental pollution may occur. For this reason, various laws have been established to regulate the elution amount of heavy metals below a certain value, or regulate the amount of heavy metals in water below a certain value. Conventionally, dithiocarbamic acid group, phosphoric acid group, carboxylic acid are used for the purpose of immobilizing heavy metals in solid waste such as fly ash to prevent elution, or to collect and remove heavy metals in waste water. It is proposed to immobilize heavy metals with a metal scavenger having a functional group such as a group, a carbamic acid group, a dithioic acid group, an aminophosphoric acid group, a thiol group, or a xanthate group (Patent Documents 1 to 9 etc.) .

特開昭49-99978号JP 49-99978 特開昭51-111756号JP 51-111756 A 特開昭64-90083号JP-A-64-90083 特開平1-99679号JP-A-1-99679 特開平2-6889号JP-A-2-6889 特開平5-50055号Japanese Patent Laid-Open No. 5-50055 特開平5-212382号JP-A-5-212382 特開平6-15280号JP-A-6-15280 特開平12-136371号JP-A-12-136371

上記、焼却灰、焼却飛灰、溶融飛灰、溶融スラグ、石炭灰、鉱滓、汚泥、汚染土壌、シュレッダーダスト、工場から排出される廃水、埋立処分場の地下汚染水等には、鉛、クロム(III)、カドミウム、銅等の重金属類の他に、ホウ素やフッ素が含まれており、近年、ホウ素やフッ素に対しても重金属類と同様の規制が設けられつつある。しかしながら上記した従来から用いられている金属捕集剤は、重金属類を捕集、固定化することはできてもホウ素やフッ素を環境基準値以下に、又は排水基準値以下に無害化することは困難であった。   Lead, chromium, incineration ash, incineration fly ash, molten fly ash, molten slag, coal ash, mines, sludge, contaminated soil, shredder dust, waste water discharged from factories, underground contaminated water at landfill sites, etc. In addition to (III), heavy metals such as cadmium and copper, boron and fluorine are contained. In recent years, regulations similar to those for heavy metals are being provided for boron and fluorine. However, the above-described conventional metal scavengers can capture and immobilize heavy metals, but detoxify boron and fluorine below the environmental standard value or below the wastewater standard value. It was difficult.

本発明者らは上記課題を解決すべく鋭意研究した結果、希土類元素の化合物や4族元素の化合物と、アルミニウム化合物とを併用することにより、ホウ素やフッ素を効率良く固定化できることを見出し本発明を完成するに至った。   As a result of intensive studies to solve the above problems, the present inventors have found that boron and fluorine can be efficiently immobilized by using a rare earth element compound or a group 4 element compound in combination with an aluminum compound. It came to complete.

即ち本発明は、
(1)希土類元素の化合物、4族元素の化合物よりなる群から選ばれた少なくとも1種(A)と、アルミニウム化合物(B)とを被処理物に添加し、被処理物中のホウ素及び/又はフッ素を固定化することを特徴とするホウ素、フッ素の固定化方法、
(2)希土類元素の化合物、4族元素の化合物よりなる群から選ばれた少なくとも1種(A)と、アルミニウム化合物(B)とからなることを特徴とするホウ素、フッ素の固定化剤組成物、
を要旨とする。
That is, the present invention
(1) At least one selected from the group consisting of rare earth element compounds and group 4 element compounds (A) and an aluminum compound (B) are added to the object to be treated, and boron and / or Or boron, characterized by immobilizing fluorine, a method for immobilizing fluorine,
(2) A boron / fluorine fixing agent composition comprising at least one (A) selected from the group consisting of a rare earth element compound and a group 4 element compound, and an aluminum compound (B) ,
Is the gist.

本発明方法は、従来の金属捕集剤では固定化することが困難であったホウ素、フッ素を確実に固定化することができ、ホウ素やフッ素の溶出による環境汚染を防止することができる。   The method of the present invention can reliably fix boron and fluorine, which have been difficult to fix with conventional metal scavengers, and can prevent environmental pollution due to elution of boron and fluorine.

本発明において用いる(A)群の希土類元素化合物としては、スカンジウム、イットリウム、ランタン、セリウム、プラセオジム、ネオジム、プロメチウム、サマリウム、ユーロピウム、ガドリニウム、テルビウム、ジスプロシウム、ホルミウム、エルビウム、ツリウム、イッテルビウム、ルテチウム等希土類元素の塩化物、臭化物、ヨウ化物、硫化物、フッ化物、硝酸塩、炭酸塩、硫酸塩、酢酸塩、シュウ酸塩、酸化物、窒化物、オキシ塩化物、アルコキシド、水酸化物、アンモニウム塩、それらの複合塩等が挙げられる。代表的なものとしては、塩化スカンジウム、水酸化スカンジウム、硫酸スカンジウム、硝酸スカンジウム、酸化スカンジウム、シュウ酸スカンジウム、ヨウ化イットリウム、フッ化イットリウム、塩化イットリウム、炭酸イットリウム、硝酸イットリウム、シュウ酸イットリウム、水酸化イットリウム、硫酸イットリウム、酸化イットリウム、塩化プロメチウム、水酸化プロメチウム、硫酸プロメチウム、硝酸プロメチウム、酸化プロメチウム、フッ化ランタン、硫化ランタン、塩化ランタン、臭化ランタン、ヨウ化ランタン、水素化ランタン、窒化ランタン、シュウ酸ランタン、炭酸ランタン、水酸化ランタン、硫酸ランタン、硝酸ランタン、酸化ランタン、酢酸ランタン、塩化セリウム、炭酸セリウム、水酸化セリウム、硫酸セリウム、硝酸セリウム、酸化セリウム、酢酸セリウム、塩化プラセオジム、硝酸プラセオジム、酸化プラセオジム、水酸化プラセオジム、塩化ネオジム、硝酸ネオジム、炭酸ネオジム、酸化ネオジム、水酸化ネオジム、塩化プロメチウム、硝酸プロメチウム、硫酸プロメチウム、水酸化プロメチウム、塩化サマリウム、硝酸サマリウム、塩化ユーロピウム、硫酸ユーロピウム、塩化ガドリニウム、硝酸ガドリニウム、水酸化ガドリニウム、塩化テルビウム、炭酸テルビウム、水酸化テルビウム、塩化ジスプロシウム、硝酸ジスプロシウム、酸化ジスプロシウム、塩化ホルミウム、硝酸ホルミウム、水酸化ホルミウム、酸化ホルミウム、塩化エルビウム、硝酸エルビウム、硫酸エルビウム、水酸化エルビウム、酸化ツリウム、水酸化ツリウム、塩化イッテルビウム、硝酸イッテルビウム、塩化ルテチウム、酸化ルテチウム又はそれらの複合化合物、セリウム、ランタンを主成分とする精鉱を化学処理した塩化希土等が挙げられる。また、4族元素の化合物としてはチタン、ジルコニウム、ハフニウム等の塩化物、臭化物、ヨウ化物、硫化物、フッ化物、硝酸塩、炭酸塩、硫酸塩、酢酸塩、シュウ酸塩、酸化物、窒化物、オキシ塩化物、アルコキシド、水酸化物、アンモニウム塩、それらの複合塩等が挙げられる。代表的なものとしては、塩化ジルコニウム、炭酸ジルコニウム、水酸化ジルコニウム、硫酸ジルコニウム、硝酸ジルコニウム、酸化ジルコニウム、酢酸ジルコニウム、オキシ塩化ジルコニウム、塩化チタン、水酸化チタン、酸化チタン、塩化ハフニウム、オキシ塩化ハフニウム、シュウ酸ハフニウム、水酸化ハフニウム、又はそれらの複合化合物等が挙げられる。上記希土類元素の化合物、4族元素の化合物は、1種又は2種以上を混合して用いることができるが、中でもランタン、セリウム、イットリウム、ネオジウム、プラセオジウム、サマリウム、ジルコ二ウムの化合物が好ましい。特に、上記元素の塩化物、硝酸塩、硫酸塩、炭酸塩、酢酸塩、シュウ酸塩が好ましく、代表的なものとしては、塩化ランタン、硝酸ランタン、酢酸ランタン、シュウ酸ランタン、塩化セリウム、硝酸セリウム、塩化イットリウム、硝酸イットリウム、硫酸イットリウム、塩化ネオジウム、硝酸ネオジウム、硫酸ネオジウム、硝酸プラセオジウム、塩化プラセオジウム、硫酸プラセオジウム、塩化サマリウム、硝酸サマリウム、塩化ジルコ二ウム等が挙げられる。   As the rare earth element group (A) used in the present invention, scandium, yttrium, lanthanum, cerium, praseodymium, neodymium, promethium, samarium, europium, gadolinium, terbium, dysprosium, holmium, erbium, thulium, ytterbium, lutetium and the like Elemental chloride, bromide, iodide, sulfide, fluoride, nitrate, carbonate, sulfate, acetate, oxalate, oxide, nitride, oxychloride, alkoxide, hydroxide, ammonium salt, These complex salts are exemplified. Typical examples include scandium chloride, scandium hydroxide, scandium sulfate, scandium nitrate, scandium oxide, scandium oxalate, yttrium iodide, yttrium fluoride, yttrium chloride, yttrium carbonate, yttrium nitrate, yttrium oxalate, hydroxide Yttrium, Yttrium sulfate, Yttrium oxide, Promethium chloride, Promethium hydroxide, Promethium sulfate, Promethium nitrate, Promethium oxide, Lanthanum sulfide, Lanthanum chloride, Lanthanum bromide, Lanthanum iodide, Lanthanum hydride, Lanthanum nitride, Shu Lanthanum acid, Lanthanum carbonate, Lanthanum hydroxide, Lanthanum sulfate, Lanthanum nitrate, Lanthanum oxide, Lanthanum acetate, Cerium chloride, Cerium carbonate, Cerium hydroxide, Cerium sulfate, Cerium oxide, cerium oxide, cerium acetate, praseodymium chloride, praseodymium nitrate, praseodymium oxide, praseodymium hydroxide, neodymium chloride, neodymium nitrate, neodymium carbonate, neodymium oxide, neodymium hydroxide, promethium chloride, promethium nitrate, promethium sulfate, promethium hydroxide , Samarium chloride, samarium nitrate, europium chloride, europium sulfate, gadolinium chloride, gadolinium nitrate, gadolinium hydroxide, terbium chloride, terbium carbonate, terbium hydroxide, dysprosium chloride, dysprosium nitrate, dysprosium oxide, holmium chloride, holmium nitrate, hydroxide Holmium, holmium oxide, erbium chloride, erbium nitrate, erbium sulfate, erbium hydroxide, thulium oxide, thulium hydroxide, yttrium chloride Rubiumu, ytterbium nitrate, lutetium chloride, lutetium oxide or a composite compound thereof, cerium, rare earth chloride, and the like that lanthanum was chemically treated to concentrate mainly containing. In addition, group 4 element compounds include chlorides, bromides, iodides, sulfides, fluorides, nitrates, carbonates, sulfates, acetates, oxalates, oxides, nitrides such as titanium, zirconium and hafnium. , Oxychlorides, alkoxides, hydroxides, ammonium salts, and complex salts thereof. Typical examples include zirconium chloride, zirconium carbonate, zirconium hydroxide, zirconium sulfate, zirconium nitrate, zirconium oxide, zirconium acetate, zirconium oxychloride, titanium chloride, titanium hydroxide, titanium oxide, hafnium chloride, hafnium oxychloride, Examples thereof include hafnium oxalate, hafnium hydroxide, or composite compounds thereof. The rare earth element compound and the group 4 element compound may be used alone or in combination of two or more. Among them, lanthanum, cerium, yttrium, neodymium, praseodymium, samarium and zirconium compounds are preferred. In particular, chlorides, nitrates, sulfates, carbonates, acetates, and oxalates of the above elements are preferable. Typical examples include lanthanum chloride, lanthanum nitrate, lanthanum acetate, lanthanum oxalate, cerium chloride, and cerium nitrate. Yttrium chloride, yttrium nitrate, yttrium sulfate, neodymium chloride, neodymium nitrate, neodymium sulfate, praseodymium nitrate, praseodymium chloride, praseodymium sulfate, samarium chloride, samarium nitrate, zirconium chloride and the like.

(B)群のアルミニウム化合物としては、塩化アルミニウム、硫酸アルミニウム、硝酸アルミニウム、ポリ硫酸アルミニウム等が挙げられるが、なかでも硫酸アルミニウム、ポリ硫酸アルミニウムが好ましく、特に硫酸アルミニウムが好ましい。アルミニウム化合物は2種以上を併用することができる。   Examples of the aluminum compound of group (B) include aluminum chloride, aluminum sulfate, aluminum nitrate, and polyaluminum sulfate, among which aluminum sulfate and polyaluminum sulfate are preferable, and aluminum sulfate is particularly preferable. Two or more aluminum compounds can be used in combination.

本発明方法は、上記(A)群の希土類元素の化合物及び/又は4族元素の化合物と、(B)群のアルミニウム化合物とを被処理物に添加して、被処理物中のホウ素及び/又はフッ素を捕集、固定化する。本発明方法において(A)群の化合物と、(B)群の化合物とは、どちらを先に被処理物に添加しても良く、両者を混合した固定化剤組成物として添加しても良い。(A)群の化合物、(B)群の化合物を別々に添加する場合も、両者を混合した固定化剤組成物として添加する場合も、(A)群の化合物と(B)群の化合物との比率は重量比で、(A)群の化合物:(B)群の化合物=99:1〜10:90が好ましい。被処理物に対する添加量は、(A)群の化合物と(B)群の化合物とを合計した量で0.1〜20wt%が好ましい。(A)群の化合物、(B)群の化合物は、粉末等の固体状で添加しても、水溶液やスラリーとして添加しても良い。被処理物が廃水等の液体の場合、ホウ素及び/又はフッ素を捕集して生成した不溶物を沈殿分離することで、廃水等に含まれているホウ素、フッ素を除去することができる。またフロック被処理物が固体の場合、必要によって更に水を添加して静置するか、混練してホウ素、フッ素を固定化することができる。   In the method of the present invention, the rare earth element compound and / or the group 4 element compound of group (A) and the aluminum compound of group (B) are added to the object to be treated, and boron and / or Alternatively, fluorine is collected and immobilized. In the method of the present invention, either the compound of the group (A) or the compound of the group (B) may be added to the object to be treated first, or may be added as a fixing agent composition in which both are mixed. . Whether the compound of (A) group and the compound of (B) group are added separately or when they are added as a fixing agent composition in which both are mixed, the compound of (A) group and the compound of (B) group The ratio of is a weight ratio, preferably (A) group compound: (B) group compound = 99: 1 to 10:90. The amount added to the object to be treated is preferably 0.1 to 20 wt% in terms of the total amount of the compound of group (A) and the compound of group (B). The compound of group (A) and the compound of group (B) may be added as a solid such as powder, or may be added as an aqueous solution or slurry. When the object to be treated is a liquid such as waste water, boron and fluorine contained in the waste water can be removed by precipitating and separating insoluble matter generated by collecting boron and / or fluorine. Further, when the floc material to be processed is solid, if necessary, water can be further added and left still, or kneaded to fix boron and fluorine.

本発明方法が処理対象とする被処理物としては、工場や研究所等から排出される廃水、埋立て処分場の地下汚染水、洗煙排水、ゴミ焼却場において生成する焼却灰や焼却飛灰、溶融飛灰、溶融スラグ、火力発電所等において燃料の石炭を燃焼させた際に発生する石炭灰、鉱滓、汚泥、汚染土壌、シュレッダーダスト等が挙げられる。   The treated objects to be treated by the method of the present invention include waste water discharged from factories and research institutes, underground contaminated water at landfill sites, smoke washing drainage, incineration ash and incineration fly ash generated at garbage incineration sites. Examples include coal ash, slag, sludge, contaminated soil, and shredder dust generated when fuel coal is burned in molten fly ash, molten slag, thermal power plants, and the like.

以下、実施例を挙げて本発明を更に詳細に説明する
実施例1〜5、比較例1〜6
フッ化ナトリウム及びホウ酸を水に溶解させて、ホウ素濃度100mg/L、フッ素濃度100mg/Lとなるように調製した模擬廃水1リットル当たりに対し、表1に示す所定量の(A)群の化合物、(B)群のアルミニウム化合物を添加し、30分間攪拌した後、静置した。不溶化物をNo.5Cの濾紙(保持孔径:1μm)にて分離除去した後、廃水中に残存するホウ素、フッ素濃度を以下の方法で測定した。結果を表1に示した。
Hereinafter, Examples 1 to 5 and Comparative Examples 1 to 6 illustrating the present invention in more detail with reference to Examples.
Sodium fluoride and boric acid were dissolved in water, and per 1 liter of simulated wastewater prepared to have a boron concentration of 100 mg / L and a fluorine concentration of 100 mg / L, a predetermined amount of group (A) shown in Table 1 Compound, an aluminum compound of group (B) was added and stirred for 30 minutes, then allowed to stand. The insolubilized material was No. After separating and removing with 5C filter paper (holding hole diameter: 1 μm), the boron and fluorine concentrations remaining in the wastewater were measured by the following method. The results are shown in Table 1.

フッ素分析法:JIS K 0102 工場排水試験法 34.1 ランタンーアリザリンコンプレキソン吸光光度法
ホウ素分析法:JIS K 0102 工場排水試験法 47.3 ICP発光分光分析法
Fluorine analysis method: JIS K 0102 factory drainage test method 34.1 Lanthanum-alizarin complexone photometric method Boron analysis method: JIS K 0102 factory drainage test method 47.3 ICP emission spectroscopy

(表1)

Figure 2006116389
※1:廃水に添加後の割合 (Table 1)
Figure 2006116389
* 1: Ratio after addition to wastewater

実施例6〜10、比較例7〜12
ペーパースラッジやプラスチックをロータリキルンで焼却したときの焼却灰(フッ素含有量4100mg/kg、ホウ素含有量350mg/kg)100g当たりに対して、表2に示す所定量の(A)群の化合物と(B)群のアルミニウム化合物、水30gを添加して15分間混練した。処理後の焼却灰と未処理の焼却灰について、ホウ素溶出濃度、フッ素溶出濃度を環境庁告示第46号試験に準じて測定した結果を表2に示す。
Examples 6-10, Comparative Examples 7-12
With respect to 100 g of incinerated ash (fluorine content: 4100 mg / kg, boron content: 350 mg / kg) when paper sludge or plastic is incinerated in a rotary kiln, a predetermined amount of a compound of group (A) shown in Table 2 ( The aluminum compound of group B) and 30 g of water were added and kneaded for 15 minutes. Table 2 shows the results of measuring the boron elution concentration and fluorine elution concentration in accordance with the Environmental Agency Notification No. 46 test for the treated and untreated incineration ash.

(表2)

Figure 2006116389
※2:飛灰に添加後の割合 (Table 2)
Figure 2006116389
* 2: Ratio after adding to fly ash

Claims (2)

希土類元素の化合物、4族元素の化合物よりなる群から選ばれた少なくとも1種(A)と、アルミニウム化合物(B)とを被処理物に添加し、被処理物中のホウ素及び/又はフッ素を固定化することを特徴とするホウ素、フッ素の固定化方法。 At least one selected from the group consisting of a rare earth element compound and a group 4 element compound (A) and an aluminum compound (B) are added to the object to be treated, and boron and / or fluorine in the object to be treated are added. A method for immobilizing boron and fluorine, characterized by immobilization. 希土類元素の化合物、4族元素の化合物よりなる群から選ばれた少なくとも1種(A)と、アルミニウム化合物(B)とからなることを特徴とするホウ素、フッ素の固定化剤組成物。
A boron and fluorine fixing agent composition comprising at least one (A) selected from the group consisting of a rare earth element compound and a group 4 element compound, and an aluminum compound (B).
JP2004305006A 2004-10-20 2004-10-20 Fixing method for boron and fluorine and fixing agent composition Pending JP2006116389A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2004305006A JP2006116389A (en) 2004-10-20 2004-10-20 Fixing method for boron and fluorine and fixing agent composition

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2004305006A JP2006116389A (en) 2004-10-20 2004-10-20 Fixing method for boron and fluorine and fixing agent composition

Publications (1)

Publication Number Publication Date
JP2006116389A true JP2006116389A (en) 2006-05-11

Family

ID=36534780

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2004305006A Pending JP2006116389A (en) 2004-10-20 2004-10-20 Fixing method for boron and fluorine and fixing agent composition

Country Status (1)

Country Link
JP (1) JP2006116389A (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10277563A (en) * 1997-04-03 1998-10-20 Unitika Ltd Fixing agent for boron and method for treating waste water containing boron
JP2000263064A (en) * 1999-03-23 2000-09-26 Unitika Ltd Boron fixation agent and method for treating boron- containing wastewater
JP2001200236A (en) * 2000-01-21 2001-07-24 Environmental Control Center Co Ltd Arsenic insolubilizing treatment agent for arsenic contaminant and its preparation process
JP2003320376A (en) * 2002-02-26 2003-11-11 National Institute Of Advanced Industrial & Technology Treatment method for fluorine-containing wastewater and chemical agent used therein
JP2004000963A (en) * 2002-04-26 2004-01-08 National Institute Of Advanced Industrial & Technology Treatment method of boron-containing drainage, and medicament used for the same
JP2004148289A (en) * 2002-09-04 2004-05-27 Japan Organo Co Ltd Fluorine or phosphorus-containing water treatment equipment

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH10277563A (en) * 1997-04-03 1998-10-20 Unitika Ltd Fixing agent for boron and method for treating waste water containing boron
JP2000263064A (en) * 1999-03-23 2000-09-26 Unitika Ltd Boron fixation agent and method for treating boron- containing wastewater
JP2001200236A (en) * 2000-01-21 2001-07-24 Environmental Control Center Co Ltd Arsenic insolubilizing treatment agent for arsenic contaminant and its preparation process
JP2003320376A (en) * 2002-02-26 2003-11-11 National Institute Of Advanced Industrial & Technology Treatment method for fluorine-containing wastewater and chemical agent used therein
JP2004000963A (en) * 2002-04-26 2004-01-08 National Institute Of Advanced Industrial & Technology Treatment method of boron-containing drainage, and medicament used for the same
JP2004148289A (en) * 2002-09-04 2004-05-27 Japan Organo Co Ltd Fluorine or phosphorus-containing water treatment equipment

Similar Documents

Publication Publication Date Title
JP4481360B1 (en) Insolubilizing material
JPH10137716A (en) Waste treating material and treatment of waste
JP2006000778A (en) Waste treatment method
JP2006116389A (en) Fixing method for boron and fluorine and fixing agent composition
JP2004314058A (en) Treatment method for waste
JP2003181411A (en) Heavy metal elution preventing agent and treatment method of contaminated medium
JP2010051840A (en) Agent for treating flue gas, and method for treating flue gas
JP3762965B2 (en) Methods for insolubilizing heavy metal elements contained in pollutants such as waste
JPH1099814A (en) Treatment of waste
JP2018103133A (en) Soil treatment material and purification method of heavy metal contaminated soil
JP5608352B2 (en) Methods for insolubilizing hazardous substances
JP4119534B2 (en) Metal and dioxin and / or organochlorine compound simultaneous treating agent and processing method
JP4476110B2 (en) Heavy metal scavengers containing morpholine dithiocarbamic acid alkali metal salts
JP2736097B2 (en) Detoxification method of industrial waste containing hazardous heavy metals
JPH01304100A (en) Apparatus for treating waste water desulfurized by wet exhaust gas desulfurization device
JP2005199221A (en) Detoxicating processing method for sludge or soil
JPH1111992A (en) Cement based material to be solidified or hydraulic material of incineration ash in which harmful heavy metal is insolubilized
JP4345493B2 (en) Soil purification agent and soil purification method
JP2007268429A (en) Method of suppressing elution of arsenic from soil contaminated by arsenic
JPH10151429A (en) Treatment for detoxifying harmful heavy metal contained in high alkaline dust collection ash
JP5733944B2 (en) Heavy metal immobilizing agent and method for treating heavy metal contaminants using the same
JP4702874B2 (en) Heavy metal-containing waste treatment agent and heavy metal-containing waste treatment method
JP3565359B2 (en) Treatment method of fly ash of city garbage incinerator
JP4450520B2 (en) Flue gas treating agent and treatment method
JPH10156308A (en) Treatment of alkaline fly ash

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20070919

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20091210

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20091216

A02 Decision of refusal

Free format text: JAPANESE INTERMEDIATE CODE: A02

Effective date: 20100407