JP2003236519A - Contaminated soil decontaminating material for soil contaminated with organic halogen compound and decontaminating method of contaminated soil using the same - Google Patents

Contaminated soil decontaminating material for soil contaminated with organic halogen compound and decontaminating method of contaminated soil using the same

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Publication number
JP2003236519A
JP2003236519A JP2002033620A JP2002033620A JP2003236519A JP 2003236519 A JP2003236519 A JP 2003236519A JP 2002033620 A JP2002033620 A JP 2002033620A JP 2002033620 A JP2002033620 A JP 2002033620A JP 2003236519 A JP2003236519 A JP 2003236519A
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JP
Japan
Prior art keywords
soil
contaminated
decontaminating
organic halogen
sulfate
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
Application number
JP2002033620A
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Japanese (ja)
Other versions
JP3841696B2 (en
Inventor
Hidehiro Tanaka
秀弘 田中
Hideo Ishida
秀朗 石田
Mitsuo Takahashi
光男 高橋
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.)
Denka Co Ltd
Original Assignee
Denki Kagaku Kogyo KK
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Application filed by Denki Kagaku Kogyo KK filed Critical Denki Kagaku Kogyo KK
Priority to JP2002033620A priority Critical patent/JP3841696B2/en
Publication of JP2003236519A publication Critical patent/JP2003236519A/en
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Publication of JP3841696B2 publication Critical patent/JP3841696B2/en
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  • Soil Conditioners And Soil-Stabilizing Materials (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To solve the problem of an unstable factor in a microbiological method, low working efficiency in a vacuum extraction method and large consumption of limestone in a method for blending soil with slaked lime and/or calcium aluminate powder in a method for decontaminating soil contaminated with organic halogen compounds. <P>SOLUTION: A decontaminating material for the soil contaminated with the organic halogen compounds is characterized by containing calcium aluminates and water. A method for injecting the contaminated soil decontaminating material into ground is also provided. Since organic halogen compounds such as fluorocarbon, trichloroethylene, carbon tetrachloride, tetrachloroethylene and methylene chloride can be effectively decontaminated by a small quantity of calcium aluminates, this method is effective for decontaminating the soil widely contaminated with a solvent of dry cleaning, a dewaxing agent of electronic parts and metallic products, a refrigerant or the like. <P>COPYRIGHT: (C)2003,JPO

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、主として有機ハロ
ゲン化合物等により汚染された土壌を効果的に浄化でき
る汚染土壌浄化材及びその浄化方法に関する。尚、本発
明で使用する部及び%は特に規定のない限り質量基準で
ある。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a polluted soil purification material and a purification method therefor capable of effectively purifying soil polluted mainly with organic halogen compounds and the like. The parts and% used in the present invention are based on mass unless otherwise specified.

【0002】[0002]

【従来の技術と課題】トリクロロエチレン、テトラクロ
ロエチレン、フロン、及び塩化メチレン等の有機ハロゲ
ン化合物は、ドライクリーニングの溶剤、電子部品や金
属製品の脱脂剤、及び冷媒等として広く利用されてい
る。
2. Description of the Related Art Organic halogen compounds such as trichloroethylene, tetrachloroethylene, freon, and methylene chloride are widely used as solvents for dry cleaning, degreasing agents for electronic parts and metal products, and refrigerants.

【0003】しかしながら、これらの有機ハロゲン化合
物は土壌中に留まるだけでなく、地下水、河川、及び井
戸水等を経由し、飲料水汚染の原因になると言われてい
る。これらの有機ハロゲン化合物は発ガン性が疑われて
おり、人の健康に重大な影響を及ぼすことから、有機ハ
ロゲン化合物により汚染された土壌を浄化することが望
まれていた。
However, it is said that these organic halogen compounds not only remain in the soil but also cause pollution of drinking water through groundwater, rivers, well water and the like. Since these organohalogen compounds are suspected to be carcinogenic and seriously affect human health, it has been desired to clean soil contaminated with the organohalogen compounds.

【0004】そこで、汚染された土壌に有機塩素系化合
物の分解可能な微生物(Saccharomyces、
Hansenula、及びCandida等)を含む液
体を注入する方法(以下「微生物法」という、特開平11
-277045号公報)、汚染された土壌を真空抽出法により
浄化する方法(以下「真空抽出法」という、特開2000-2
02425号公報)、消石灰及び/又はカルシウムアルミネ
ート類の粉末を汚染土壌と混合する方法(特開平10-427
32号公報)が提案されている。
Therefore, microorganisms capable of decomposing organochlorine compounds (Saccharomyces) in polluted soil,
A method of injecting a liquid containing Hansenula, Candida, etc. (hereinafter referred to as “microorganism method”)
-277045), a method for purifying contaminated soil by a vacuum extraction method (hereinafter referred to as "vacuum extraction method", Japanese Patent Laid-Open No. 2000-2
No. 02425), a method of mixing powder of slaked lime and / or calcium aluminate with contaminated soil (JP-A-10-427).
No. 32) is proposed.

【0005】しかし、微生物法では微生物が人体や環境
に与える影響については不明な点が多く、また、温度、
湿度、及び微生物の繁殖状況等の不安定要因があり、真
空抽出法は多量の土壌を処理するには効率が悪く、透水
性の低い粘度土壌には効果が薄い等の課題があり、消石
灰及び/又はカルシウムアルミネート類の粉末を汚染土
壌と混合する方法ではアルカリ性物質である消石灰及び
/又はカルシウムアルミネート類の粉末を土壌1m3あた
り150kgと多量に使用するために環境への影響が懸念さ
れる。また、消石灰及びカルシウムアルミネート類の原
料は石灰石であり、有限で貴重な資源である石灰石をセ
メント原料以外の用途で多量に消費することは好ましく
ないという問題点があった。
However, in the microbial method, there are many unclear points about the effects of microorganisms on the human body and the environment, and in addition to temperature,
There are instability factors such as humidity and microbial breeding conditions, the vacuum extraction method is inefficient in treating a large amount of soil, and there is a problem that the effect is weak for soil with low water permeability. In the method of mixing powder of calcium aluminate with contaminated soil, since a large amount of alkaline slaked lime and / or powder of calcium aluminate of 150 kg per 1 m 3 of soil is used, there is concern about environmental impact. It Further, the raw material of slaked lime and calcium aluminate is limestone, and it is not preferable to consume a large amount of limestone, which is a limited and valuable resource, for purposes other than the cement raw material.

【0006】本発明者らはこのような課題に鑑みて鋭意
検討した結果、特定の汚染土壌浄化材を用いることによ
り、微生物法における不安定要因、真空抽出法における
効率の悪さという課題を解決するとともに、消石灰及び
/又はカルシウムアルミネート類の粉末を土壌に混合す
る方法における環境への影響と石灰石の大量消費という
課題を解決することができることを知見し、本発明を完
成するに至った。
As a result of intensive studies in view of such problems, the present inventors have solved the problems of unstable factors in the microbial method and inefficiency in the vacuum extraction method by using a specific contaminated soil purification material. At the same time, they have found that they can solve the problems of environmental impact and the large consumption of limestone in the method of mixing powder of slaked lime and / or calcium aluminate with soil, and have completed the present invention.

【0007】[0007]

【課題を解決するための手段】すなわち、本発明はカル
シウムアルミネート類及び水を含有することを特徴とす
る、有機ハロゲン化合物で汚染された土壌に対する汚染
土壌浄化材であり、硫酸塩を含有する該汚染土壌浄化材
であり、遅延剤を含有する該汚染土壌浄化材であり、該
汚染土壌浄化材を地盤に注入することを特徴とする汚染
土壌浄化方法である。
That is, the present invention is a polluted soil remediation material for soil contaminated with organohalogen compounds, characterized by containing calcium aluminates and water and containing sulfate. The method for purifying contaminated soil is the method for purifying contaminated soil, which is the method for purifying contaminated soil containing a retarder, wherein the method for purifying contaminated soil comprises injecting the contaminated soil purification material into the ground.

【0008】[0008]

【発明の実施の形態】以下、本発明を詳細に説明する。BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described in detail below.

【0009】本汚染土壌浄化材は、主として有機ハロゲ
ン化合物からなる汚染土壌を浄化するものである。有機
ハロゲン化合物としては、トリクロロエチレン、テトラ
クロロエチレン、トランス−1,2−ジクロロエチレ
ン、シス−1,2−ジクロロエチレン、四塩化炭素、ク
ロロエタン、メチレンクロリド、クロロホルム、塩化ビ
ニルモノマー、1,1−ジクロロエタン、1,2−ジク
ロロエタン、1,2−ジクロロプロパン、ジクロロブロ
モエチレン、1,1,1−トリクロロエタン、PCB、
及びダイオキシン等の有機塩素化合物、ブロモジクロロ
メタン、クロロジブロモメタン、及びブロモホルム等の
有機臭素化合物、ヨードホルム等の有機ヨウ素化合物、
フロリナート及び液体状のフロン化合物等の有機フッ素
化合物等が挙げられる。
The polluted soil purifying material purifies polluted soil mainly composed of organic halogen compounds. Examples of the organic halogen compound include trichloroethylene, tetrachloroethylene, trans-1,2-dichloroethylene, cis-1,2-dichloroethylene, carbon tetrachloride, chloroethane, methylene chloride, chloroform, vinyl chloride monomer, 1,1-dichloroethane, 1,2. -Dichloroethane, 1,2-dichloropropane, dichlorobromoethylene, 1,1,1-trichloroethane, PCB,
And organic chlorine compounds such as dioxins, bromodichloromethane, chlorodibromomethane, and organic bromine compounds such as bromoform, organic iodine compounds such as iodoform,
Examples thereof include organic fluorine compounds such as fluorinate and liquid fluorocarbon compounds.

【0010】本汚染土壌浄化材は汚染物質が有機塩素化
合物のうちの1種又は2種以上の場合には、汚染土壌浄
化の効率が大きくなる。
The polluted soil purification material of the present invention has a high efficiency of purification of polluted soil when the pollutant is one or more of organic chlorine compounds.

【0011】本発明のカルシウムアルミネート類とは、
カルシアを含む原料と、アルミナを含む原料とを混合し
て、キルンでの焼成又は電気炉での溶融等の熱処理をし
て得られる化合物であり、CaOとAl23とを主たる
成分とし、CaOをC、Al 23をAとしたとき、化学
式Cmn(m,nは正の実数)で表わされる酸化物のうち水
和活性を有する物質の総称であり、結晶質及び非晶質の
いずれも存在するが、例えば結晶性の化合物ではC
3A、C127、CA等の組成のものが知られている。
The calcium aluminates of the present invention are
Mix the raw material containing calcia with the raw material containing alumina.
Heat treatment such as firing in a kiln or melting in an electric furnace.
Is a compound obtained by CaO and Al2O3And
As a component, CaO is C, Al 2O3Where A is chemistry
Formula CmAnOf the oxides represented by (m and n are positive real numbers), water
It is a general term for substances that have a Japanese activity and includes crystalline and amorphous substances.
Although both exist, for example, in a crystalline compound, C
3A, C12A7, CA, etc. are known.

【0012】カルシウムアルミネート類においてCaO
含有量が40%未満のものはアルミナセメントと同様の
組成となる。
CaO in calcium aluminates
If the content is less than 40%, the composition is similar to that of alumina cement.

【0013】また、これらのカルシウムアルミネート類
の一部をアルカリ金属酸化物、アルカリ土類金属酸化
物、酸化ケイ素、酸化チタン、酸化鉄、アルカリ金属ハ
ロゲン化合物、アルカリ土類金属ハロゲン化合物、アル
カリ金属硫酸塩、及びアルカリ土類金属硫酸塩等が置換
した固溶体も使用可能である。
Further, a part of these calcium aluminates is an alkali metal oxide, an alkaline earth metal oxide, silicon oxide, titanium oxide, iron oxide, an alkali metal halogen compound, an alkaline earth metal halogen compound, an alkali metal. It is also possible to use a solid solution in which a sulfate, an alkaline earth metal sulfate or the like is substituted.

【0014】カルシウムアルミネート類の中では、結晶
質及び非晶質のいずれも使用可能であるが、少量の汚染
土壌浄化材で汚染土壌を浄化できる点で、非晶質が好ま
しい。
Among the calcium aluminates, both crystalline and amorphous can be used, but amorphous is preferable because the polluted soil can be purified with a small amount of the polluted soil purifying material.

【0015】カルシウムアルミネート類中のCaO含有
量とAl23含有量は、CaO含有量5〜65%、Al
23含有量95〜35%が好ましく、CaO含有量40
〜50%でAl23含有量60〜50%がより好まし
い。CaO含有量やAl23含有量がこの範囲外では汚
染土壌浄化の効率が低下する場合がある。
The CaO content and the Al 2 O 3 content in the calcium aluminates are such that the CaO content is 5 to 65%, the Al
2 O 3 content of 95 to 35% is preferable, CaO content of 40
It is more preferable that the Al 2 O 3 content is 60 to 50% at 50%. If the CaO content or the Al 2 O 3 content is outside this range, the efficiency of cleaning the contaminated soil may decrease.

【0016】カルシウムアルミネート類の比表面積は、
少量の土壌浄化材量で浄化できる点から、大きいことが
好ましい。カルシウムアルミネート類のブレーン比表面
積は、3,000cm2/g以上が好ましく、5,000
cm2/g以上がより好ましく、8,000〜10,00
0cm2/gが最も好ましい。3,000cm2/g未満で
は汚染土壌の浄化が十分にできない恐れがあり、10,
000cm2/gを超えると粉砕動力が必要となり、コス
ト増の要因となるからである。
The specific surface area of calcium aluminates is
A large amount is preferable because it can be purified with a small amount of soil purification material. The Blaine specific surface area of calcium aluminates is preferably 3,000 cm 2 / g or more,
cm 2 / g or more is more preferable, 8,000 to 10,000
Most preferred is 0 cm 2 / g. If it is less than 3,000 cm 2 / g, the contaminated soil may not be sufficiently purified.
This is because if it exceeds 000 cm 2 / g, crushing power is required, which causes a cost increase.

【0017】さらに、本発明では、土壌浄化の効率を大
きくするために、カルシウムアルミネート類に硫酸塩を
併用することが好ましい。
Further, in the present invention, it is preferable to use a sulfate together with calcium aluminate in order to increase the efficiency of soil purification.

【0018】本発明の硫酸塩としては、ミョウバン類、
6水塩、10水塩、16水塩、及び18水塩等の含水硫
酸アルミニウム、無水硫酸アルミニウム、0.5水塩及
び2水塩等の含水硫酸カルシウム、無水硫酸カルシウ
ム、7水塩及び10水塩等の含水硫酸ナトリウム、無水
硫酸ナトリウム、1水塩、6水塩、及び7水塩等の含水
硫酸マグネシウム、無水硫酸マグネシウム、3水塩、6
水塩、7水塩、7.5水塩、9水塩、10水塩、及び1
2水塩等の含水硫酸鉄、無水硫酸鉄(II)、無水硫酸
鉄(III)等の無水硫酸鉄、硫酸リチウム1水塩、並
びに無水硫酸リチウム等が挙げられる。これらの中で
は、土壌浄化の効率の点で、無水硫酸アルミニウム及び
硫酸アルミニウム18水塩が好ましい。
The sulfates of the present invention include alums,
Hydrated aluminum sulfate such as hexahydrate, 10-hydrate, 16-hydrate and 18-hydrate, anhydrous aluminum sulfate, hydrous calcium sulfate such as 0.5-hydrate and 2-hydrate, anhydrous calcium sulfate, 7-hydrate and 10-hydrate Hydrous sodium sulfate such as hydrate, anhydrous sodium sulfate, monohydrate, hexahydrate, and hydrous magnesium sulfate such as heptahydrate, anhydrous magnesium sulfate, trihydrate, 6
Hydrous salt, 7-hydrated salt, 7.5-hydrated salt, 9-hydrated salt, 10-hydrated salt, and 1
Examples include hydrous iron sulfate such as dihydrate, anhydrous iron sulfate (II), anhydrous iron sulfate such as anhydrous iron sulfate (III), lithium sulfate monohydrate, and anhydrous lithium sulfate. Among these, anhydrous aluminum sulfate and aluminum sulfate 18-hydrate are preferable in terms of soil purification efficiency.

【0019】硫酸塩の使用量は、カルシウムアルミネー
ト類100部に対して50〜300部が好ましく、10
0〜200部がより好ましい。50部未満だと土壌浄化
の効率が小さくなるおそれがあり、300部を超えると
硫酸塩が水に対して十分に溶解しないおそれがある。。
The amount of sulfate to be used is preferably 50 to 300 parts per 100 parts of calcium aluminate, 10
0 to 200 parts is more preferable. If it is less than 50 parts, the efficiency of soil purification may be reduced, and if it exceeds 300 parts, the sulfate may not be sufficiently dissolved in water. .

【0020】水及びカルシウムアルミネート類の混合割
合は、汚染物質の濃度及び土壌への注入方法により変化
し、例えばカルシウムアルミネート濃度が高い本汚染土
壌浄化材を少量土壌に加圧注入する方法、及びカルシウ
ムアルミネート濃度が低い本汚染土壌浄化材を多量に散
布する方法等の多様な散布形態があり、また土壌により
最適値が異なるために配合割合は一義的には決められな
いが、一般的にはカルシウムアルミネート類100部に
対して、水100〜100,000部が好ましく、10
0〜10,000部がより好ましい。
The mixing ratio of water and calcium aluminate changes depending on the concentration of pollutants and the method of injecting into the soil. For example, a method of injecting a small amount of the present polluted soil purification material having a high concentration of calcium aluminate into the soil, There are various spraying forms such as a method of spraying a large amount of this polluted soil purification material with low calcium aluminate concentration, and the optimum value differs depending on the soil, so the mixing ratio cannot be uniquely determined, but in general Is preferably 100 to 100,000 parts of water per 100 parts of calcium aluminate.
0 to 10,000 parts is more preferable.

【0021】なお、汚染土壌浄化材と水との混合物を土
壌中に十分浸透させる目的で、遅延剤を併用することが
可能である。
A retarder may be used in combination for the purpose of sufficiently permeating the mixture of the polluted soil purifying material and water into the soil.

【0022】遅延剤としては、例えばクエン酸、酒石
酸、グルコン酸、及びリンゴ酸等のオキシカルボン酸、
これらオキシカルボン酸の塩であるオキシカルボン酸塩
が挙げられる。これらの遅延剤を1種又は2種以上を併
用しても良い。これらのなかでは、遅延効果が大きい点
でクエン酸及びクエン酸の塩が好ましく、クエン酸及び
クエン酸ナトリウムがより好ましい。
Examples of the retarder include oxycarboxylic acids such as citric acid, tartaric acid, gluconic acid and malic acid,
Examples thereof include oxycarboxylic acid salts which are salts of these oxycarboxylic acids. These retarders may be used alone or in combination of two or more. Among these, citric acid and salts of citric acid are preferable, and citric acid and sodium citrate are more preferable, because of their large delaying effect.

【0023】遅延剤の使用量は、その種類により効果が
異なるため、一義的には決められないが、カルシウムア
ルミネート類100部に対して、0.01〜10部が好
ましく、0.05〜5部がより好ましい。0.01部未
満では遅延効果が小さい恐れがあり、10部を超えて添
加すると土壌浄化の効率が小さくなるばかりでなく、不
経済である。
The amount of the retarder used cannot be uniquely determined because the effect varies depending on the type, but it is preferably 0.01 to 10 parts, and preferably 0.05 to 100 parts with respect to 100 parts of calcium aluminate. 5 parts is more preferred. If it is less than 0.01 part, the retarding effect may be small, and if it is added in excess of 10 parts, not only the efficiency of soil purification decreases but it is uneconomical.

【0024】本汚染土壌浄化材の使用量は特に限定され
ず、有機ハロゲン化合物の浸透深さ、土壌の種類等によ
り異なるために一義的に決められないが、例えば土壌1
3中に汚染物質が10〜100g程度含まれる場合に
は、土壌1m3に対して、カルシウムアルミネート類換
算で0.1〜1,000gが好ましく、10〜100g
がより好ましい。0.1g未満では汚染土壌浄化の効率
が低下する場合があり、1,000gを超えても汚染土
壌浄化の効率は変わらず、経済的に好ましくない。
The amount of the polluted soil purification material used is not particularly limited and cannot be uniquely determined because it varies depending on the penetration depth of the organic halogen compound, the type of soil, etc.
when m contaminants during 3 is contained about 10 to 100 g, to the soil 1 m 3, preferably 0.1~1,000g calcium aluminates terms, 10 to 100 g
Is more preferable. If it is less than 0.1 g, the efficiency of purification of contaminated soil may decrease, and if it exceeds 1,000 g, the efficiency of purification of contaminated soil does not change, which is not economically preferable.

【0025】また、本汚染土壌浄化材を土壌と混合する
方法として、土壌と本汚染土壌浄化材をミキサー類で混
合する方法の他に、ポンプ注入、ジェット注入、土壌表
面に単に散布する方法、及びスプリンクラーによる散布
等が挙げられるが、ポンプ注入及びジェット注入のよう
な、加圧による注入方法が好ましい。
As a method of mixing the present contaminated soil purification material with soil, in addition to a method of mixing the soil and the present contaminated soil purification material with a mixer, pump injection, jet injection, or simply spraying on the soil surface, And spraying with a sprinkler, etc., but an injection method by pressurization such as pump injection and jet injection is preferable.

【0026】[0026]

【実施例】以下、本発明の実験例を示し、本発明をさら
に説明するが、本発明はこれらに限定されるものではな
い。
EXAMPLES The present invention will be further described below with reference to experimental examples of the present invention, but the present invention is not limited thereto.

【0027】実験例1 汚染物質としてトリクロロエチレンを使用し、土壌中の
トリクロロエチレン量が50mg/リットルになるように汚
染土壌を作製した。次に、カルシウムアルミネート類10
0部及び水2,000部を混合し、汚染土壌浄化材を作製し
た。
Experimental Example 1 Trichlorethylene was used as a pollutant, and a contaminated soil was prepared so that the amount of trichlorethylene in the soil would be 50 mg / liter. Next, calcium aluminates 10
0 parts and 2,000 parts of water were mixed to prepare a polluted soil purification material.

【0028】続いて、汚染土壌1m3 に対し、この混合
物を表1に示す汚染土壌浄化材量となるようにポンプ注
入した。1日間放置後、土壌中のトリクロロエチレン量
を測定した。結果を表1に併記する。
Subsequently, the mixture was pumped into 1 m 3 of the contaminated soil so that the amount of the contaminated soil purification material shown in Table 1 was obtained. After standing for 1 day, the amount of trichlorethylene in the soil was measured. The results are also shown in Table 1.

【0029】<使用材料> カルシウムアルミネート類ア:12CaO・7Al23
組成に対応する非晶質、ブレーン比表面積8,500c
2/g、合成品。 カルシウムアルミネート類イ:CaO・Al23結晶
質、ブレーン比表面積8,500cm2/g、合成品。 カルシウムアルミネート類ウ:8CaO・Na2O・3
Al23組成に対応する非晶質、ブレーン比表面積8,
500cm2/g、合成品。 トリクロロエチレン:和光純薬社製、1級試薬
<Materials used> Calcium aluminates a: 12CaO · 7Al 2 O 3
Amorphous corresponding to the composition, Blaine specific surface area of 8,500c
m 2 / g, synthetic product. Calcium aluminates a: CaO.Al 2 O 3 crystalline, Blaine specific surface area of 8,500 cm 2 / g, synthetic product. Calcium aluminates C: 8CaO ・ Na 2 O ・ 3
Amorphous corresponding to Al 2 O 3 composition, Blaine specific surface area 8,
500 cm 2 / g, synthetic product. Trichlorethylene: Wako Pure Chemical Industries, Ltd. first-grade reagent

【0030】<試験方法> トリクロロエチレン量:日本工業規格K0125の5.1、5.
2、5.3.1、5.4.1又は5.5に定める方法に準ずる。
<Test method> Trichlorethylene amount: Japanese Industrial Standard K0125, 5.1, 5.
Follow the method specified in 2, 5.3.1, 5.4.1 or 5.5.

【0031】[0031]

【表1】 [Table 1]

【0032】実験例2 汚染物質として四塩化炭素を用い、四塩化炭素濃度を30
mg/リットルとした点以外は、実験例1と同様に行っ
た。結果を表2に併記する。
Experimental Example 2 Carbon tetrachloride was used as a pollutant, and the concentration of carbon tetrachloride was 30%.
The same procedure as in Experimental Example 1 was carried out except that mg / liter was used. The results are also shown in Table 2.

【0033】<使用材料> 土壌:新潟県姫川産 四塩化炭素:和光純薬社製、1級試薬<Materials used> Soil: Himekawa, Niigata Prefecture Carbon tetrachloride: Wako Pure Chemical Industries, Ltd. first-grade reagent

【0034】<試験方法> 四塩化炭素量:日本工業規格K0125の5.1、5.2、5.3.
1、5.4.1又は5.5に定める方法に準ずる。
<Test method> Carbon tetrachloride amount: 5.1, 5.2, 5.3 of Japanese Industrial Standard K0125.
Follow the method specified in 1, 5.4.1 or 5.5.

【0035】[0035]

【表2】
[Table 2]

【0036】実験例3 カルシウムアルミネート類ア100部、表3に示す量の硫
酸塩、水2,000部を混合して汚染土壌浄化材として調製
し、カルシウムアルミネート類の使用量が土壌1m3あた
り100gとなるようにポンプ注入したこと以外は、実験例
1と同様に行った。結果を表3に併記する。
Experimental Example 3 100 parts of calcium aluminate, sulphate of the amounts shown in Table 3 and 2,000 parts of water were mixed to prepare a polluted soil purifying material, and the amount of calcium aluminate used was 1 m 3 of soil. The same procedure as in Experimental Example 1 was carried out except that 100 g of the solution was pumped. The results are also shown in Table 3.

【0037】[0037]

【表3】 [Table 3]

【0038】実験例4 汚染土壌浄化材として、カルシウムアルミネート類ア10
0部、水2,000部、表4に示す硫酸塩150部及び遅延剤A
1部からなる土壌浄化材を表2に示す量用いたこと以外
は、実験例1と同様に行った。結果を表4に併記する。
Experimental Example 4 As a pollutant for polluted soil, calcium aluminate 10
0 part, 2,000 parts of water, 150 parts of sulfate shown in Table 4 and retarder A
The same procedure as in Experimental Example 1 was carried out except that the soil purifying material consisting of 1 part was used in the amount shown in Table 2. The results are also shown in Table 4.

【0039】<使用材料> 硫酸塩α:硫酸アルミニウム18水塩、平均粒子径0.3m
m、市販品。 硫酸塩β:無水硫酸カルシウム、平均粒子径0.3mm、市
販品。 遅延剤A:クエン酸、市販品。
<Material used> Sulfate α: Aluminum sulfate 18-hydrate, average particle diameter 0.3 m
m, commercial product. Sulfate β: anhydrous calcium sulfate, average particle size 0.3 mm, commercial product. Retarder A: citric acid, a commercial product.

【0040】[0040]

【表4】
[Table 4]

【0041】実験例5 汚染物質として四塩化炭素を使用し、土壌1m3中の四
塩化炭素量が30g/m3になるように汚染土壌を作製した。
次に、カルシウムアルミネート類ア100部、硫酸塩α150
部及び遅延剤A1部からなる汚染土壌浄化材を表5に示
す量を用いたこと以外は、実験例1と同様に行った。結
果を表5に併記する。
Experimental Example 5 Carbon tetrachloride was used as a pollutant, and a contaminated soil was prepared so that the amount of carbon tetrachloride in 1 m 3 of soil was 30 g / m 3 .
Next, 100 parts of calcium aluminate, sulfate α150
Parts and the retardant A1 part were used in the same manner as in Experimental Example 1 except that the amount of the contaminated soil purifying material shown in Table 5 was used. The results are also shown in Table 5.

【0042】[0042]

【表5】 [Table 5]

【0043】[0043]

【発明の効果】以上のように、本汚染土壌浄化材を使用
することにより、少量のカルシウムアルミネート類でフ
ロン、トリクロロエチレン、四塩化炭素、テトラクロロ
エチレン、及び塩化メチレン等の有機ハロゲン化合物を
効果的に浄化できるため、ドライクリーニングの溶剤、
並びに、電子部品及び金属製品の脱脂剤、冷媒等により
広範囲にわたって汚染された土壌の浄化に有効である。
As described above, by using the polluted soil remediation material, a small amount of calcium aluminates can be used to effectively bring out organic halogen compounds such as CFCs, trichloroethylene, carbon tetrachloride, tetrachloroethylene, and methylene chloride. Because it can be purified, it is a solvent for dry cleaning,
In addition, it is effective for cleaning soil contaminated over a wide range with degreasing agents for electronic parts and metal products, refrigerants and the like.

───────────────────────────────────────────────────── 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) C09K 17/14 B09B 3/00 ZAB // C09K 101:00 Fターム(参考) 4D004 AA41 AB05 AB06 AB08 AC07 CA34 CC03 CC11 CC15 4H026 AA01 AA03 AA07 AB04 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) C09K 17/14 B09B 3/00 ZAB // C09K 101: 00 F term (reference) 4D004 AA41 AB05 AB06 AB08 AC07 CA34 CC03 CC11 CC15 4H026 AA01 AA03 AA07 AB04

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 カルシウムアルミネート類及び水を含有
することを特徴とする、有機ハロゲン化合物で汚染され
た土壌に対する汚染土壌浄化材。
1. A soil remediation material for soil contaminated with organic halogen compounds, which comprises calcium aluminates and water.
【請求項2】 硫酸塩を含有することを特徴とする請求
項1記載の汚染土壌浄化材。
2. The polluted soil remediation material according to claim 1, which contains a sulfate.
【請求項3】 遅延剤を含有することを特徴とする請求
項1又は請求項2記載の汚染土壌浄化材。
3. The polluted soil remediation material according to claim 1, which contains a retarder.
【請求項4】 請求項1〜3のうちの一項記載の汚染土
壌浄化材を地盤に注入することを特徴とする汚染土壌浄
化方法。
4. A method for purifying contaminated soil, comprising injecting the contaminated soil purifying material according to claim 1 into the ground.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013205274A (en) * 2012-03-29 2013-10-07 Taiheiyo Material Kk Radioactive contaminant treatment method

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013205274A (en) * 2012-03-29 2013-10-07 Taiheiyo Material Kk Radioactive contaminant treatment method

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