JPH11197643A - Method for washing contaminated soil - Google Patents
Method for washing contaminated soilInfo
- Publication number
- JPH11197643A JPH11197643A JP10017991A JP1799198A JPH11197643A JP H11197643 A JPH11197643 A JP H11197643A JP 10017991 A JP10017991 A JP 10017991A JP 1799198 A JP1799198 A JP 1799198A JP H11197643 A JPH11197643 A JP H11197643A
- Authority
- JP
- Japan
- Prior art keywords
- soil
- acid
- contaminated
- treatment
- particle
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Landscapes
- Fire-Extinguishing Compositions (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明はカドミウム、鉛など
の重金属などで汚染された土壌を洗浄して、汚染物質を
除去する汚染土壌の洗浄方法に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for cleaning soil contaminated with heavy metals such as cadmium and lead to remove contaminants.
【0002】[0002]
【従来の技術】市街地再開発に伴う調査で工場跡地など
における土壌汚染が判明する事例が近年増加している
が、国内で現時点で行われている土壌汚染対策は、汚染
成分の不溶化処理や遮水工事、覆土工事などの周辺環境
から汚染土壌を遮断する処置方法が一般的である。しか
しながらこの方法は汚染物質そのものが現場に残り、処
置後においても土地利用に制限がある。2. Description of the Related Art In recent years, the number of cases in which soil contamination at factory sites and the like has been revealed through surveys associated with redevelopment of urban areas has been increasing. Generally, a treatment method for shielding contaminated soil from the surrounding environment such as water works and earth covering works is common. However, this method leaves the contaminants themselves on site and has limited land use even after treatment.
【0003】そこで最近は高濃度に汚染された土壌は廃
棄して、汚染現場の土を入れ替える処置も行われている
が、産業廃棄物の最終処分場が近い将来に不足すること
は明らかなため欧米で実用化されてきている「土壌洗浄
法」の導入が検討され始めている。[0003] Recently, measures have been taken to discard highly contaminated soil and replace the soil at the site of contamination. However, it is clear that the final disposal site for industrial waste will be insufficient in the near future. The introduction of the "soil cleaning method" that has been put into practical use in Europe and the United States is beginning to be considered.
【0004】この「土壌洗浄法」とは、汚染物質を除去
するために水または適当な溶媒を用いて土壌から汚染成
分を物理的、化学的に抽出分離するものであり、汚染土
壌を洗浄して汚染成分を高濃度に含有する粒子を除去
し、それにより得られる清浄物を汚染現場の埋め戻しに
用いることによって、廃棄物となる汚染物を減容化する
ことを目的としている。したがって得られた清浄物量
の、供給された汚染物量に対する割合が高いほど効果的
な浄化方法となる。[0004] The "soil washing method" is a method of physically and chemically extracting and separating contaminants from soil using water or a suitable solvent to remove contaminants. It is an object of the present invention to reduce the volume of contaminants as waste by removing particles containing a high concentration of contaminant components and using the resulting clean product for backfilling of a contaminated site. Therefore, the higher the ratio of the obtained amount of the clean substance to the amount of the supplied contaminant, the more effective the purification method.
【0005】このような汚染土壌を洗浄するために従来
提案されている方法には、分級による高濃度汚染粒子の
分離除去処理(以下分級処理という)やアトリション処
理、比重選別、浮遊選鉱、酸溶液やキレート剤溶液など
の溶媒による汚染成分の溶脱処理などがある。Conventionally proposed methods for cleaning such contaminated soil include separation and removal of high-concentration contaminant particles by classification (hereinafter referred to as classification), attrition, specific gravity separation, flotation, and acid separation. There is leaching treatment of contaminated components with a solvent such as a solution or a chelating agent solution.
【0006】分級処理法は、汚染元素を吸着する能力が
高い微小粒子を分離除去するとともに、汚染されていな
い粒度範囲の粒子を清浄物として取り出す目的で行われ
る。しかし土壌の風化が進みこれに伴って生成した二次
鉱物が汚染された微粒子を巻き込んで、汚染されていな
かった粒子の表面に固着するようになると、分級処理で
取り出される清浄物は非常に少なくなるという問題があ
る。[0006] The classification treatment is carried out for the purpose of separating and removing fine particles having a high ability to adsorb contaminating elements, and to take out particles having a particle size range that is not contaminated as clean products. However, as the weathering of the soil progresses and the resulting secondary minerals entrain the contaminated fine particles and become attached to the surface of the non-contaminated particles, very little cleanup is obtained by the classification process. Problem.
【0007】またアトリション処理法は非汚染粒子表面
に汚染物質が付着している場合、粒子同士を擦り合わせ
ることによって摩耗研磨する方法であり、分級前に行う
のが一般的である。しかし現状のアトリション処理法で
は、汚染物質が二次鉱物とともに非汚染粒子表面に固着
している場合、長時間処理しても汚染物質を除去しきれ
ない。[0007] The attrition treatment method is a method in which when contaminants adhere to the surface of non-contaminated particles, the particles are abraded by rubbing the particles together, and is generally performed before classification. However, in the current attrition treatment method, when the contaminant is fixed on the surface of the non-contaminated particles together with the secondary mineral, the contaminant cannot be completely removed even if the treatment is performed for a long time.
【0008】さらに比重選別法も非汚染粒子の表面に汚
染物質が固着している場合には対応できない。また固着
している汚染微粒子と内側の非汚染粒子が分かれるまで
細かく粉砕すれば浮遊選鉱法での対応は可能だが、回収
される清浄物が細かくなりすぎてこれを埋め戻して土地
再利用をするには用い難い。Further, the specific gravity selection method cannot cope with the case where a contaminant adheres to the surface of non-contaminated particles. In addition, if fine grinding is performed until the contaminated fine particles and non-contaminating particles inside are separated, the flotation method can be used, but the collected recovered material is too fine and it is backfilled for land reuse. Is difficult to use.
【0009】酸濃度を非常に高くして汚染成分を溶脱す
る溶脱処理法によれば、二次鉱物ごと汚染物質を溶解さ
せることが可能となるが、これに用いる試薬使用量が莫
大になる上、その処理に長時間処理が必要となる。この
ように試薬使用量が多いとコストや廃水処理の面から実
施は困難となり、かつ処理時間が長くなると処理土壌量
を確保するためには設備を大型化せざるを得ず、いずれ
も実施の上から問題となっている。According to the leaching treatment method in which the contaminant is leached with an extremely high acid concentration, the contaminant can be dissolved together with the secondary mineral, but the amount of reagent used for this is enormous. However, the processing requires a long time. If the amount of reagent used is large as described above, implementation becomes difficult in terms of cost and wastewater treatment, and if the treatment time is long, equipment must be enlarged to secure the amount of treated soil. It is a problem from above.
【0010】[0010]
【発明が解決しようとする課題】本発明は上記の問題点
を解決するため、非汚染粒子表面に強固に固着した汚染
物質を効率よく分離除去することができる汚染土壌の洗
浄方法を提供することを目的とするものである。SUMMARY OF THE INVENTION In order to solve the above-mentioned problems, the present invention provides a method for cleaning contaminated soil capable of efficiently separating and removing contaminants firmly adhered to the surface of non-contaminated particles. It is intended for.
【0011】[0011]
【課題を解決するための手段】本発明者らは鋭意研究を
重ねた結果、表面に汚染物質が固着している土壌粒子に
対して酸を添加するのと同時、または添加後に強いアト
リション処理を加えることにより粒子表面に強固に固着
した汚染物質を効率よく分離除去することができること
を見出し本発明を完成するに至った。Means for Solving the Problems As a result of intensive studies, the present inventors have conducted a strong attrition treatment simultaneously with or after the addition of an acid to soil particles having contaminants adhered to the surface. It has been found that contaminants firmly adhered to the particle surface can be efficiently separated and removed by adding the compound, and the present invention has been completed.
【0012】したがって上記目的を達成するため本発明
は、重金属などにより汚染された土壌を洗浄する方法に
おいて、該汚染土壌に酸を添加するのと同時、または添
加後に強いアトリション処理を加える汚染土壌の洗浄方
法を特徴とするものである。[0012] Therefore, in order to achieve the above object, the present invention relates to a method for cleaning soil contaminated with heavy metals and the like, wherein a contaminated soil is subjected to a strong attrition treatment simultaneously with or after the addition of an acid to the contaminated soil. Is characterized by the following cleaning method.
【0013】[0013]
【発明の実施の形態】本発明は重金属などによる土壌汚
染において、高濃度で汚染を含有する微粒子を巻き込み
ながら、非汚染粒子表面に固着する二次鉱物層を酸と反
応させて溶解または脆化しながら強いアトリション処理
を行い、通常のアトリション処理や酸溶解処理単独では
浄化できなかった土壌粒子を清浄土として回収するもの
である。BEST MODE FOR CARRYING OUT THE INVENTION In the present invention, in the case of soil contamination by heavy metals, etc., a secondary mineral layer adhered to the surface of non-contaminated particles is dissolved or embrittled by reacting with an acid while involving fine particles containing the contamination at high concentration. However, strong attrition treatment is performed, and soil particles that cannot be purified by ordinary attrition treatment or acid dissolution treatment alone are collected as clean soil.
【0014】すなわち本発明では、硝酸、塩酸、硫酸な
どの酸の作用によって二次鉱物のうち炭酸塩などの酸と
反応し易い鉱物から溶解または変質が進み、二次鉱物層
全体としては薄層化および脆化を起こす。ここで強いア
トリション処理を加えると、薄層化および脆化した二次
鉱物ごと汚染物質を剥ぎ取り、内部の非汚染粒子を得る
ことができる。したがって二次鉱物層全体を溶解する必
要がないため単なる溶解処理と比較して少ない酸投入量
および処理時間で、通常のアトリション処理単独では対
応できない土壌からも清浄物を得ることができるもので
ある。That is, in the present invention, the secondary minerals are dissolved or deteriorated by the action of an acid such as nitric acid, hydrochloric acid, sulfuric acid or the like from the secondary minerals which easily react with an acid such as a carbonate. Cause embrittlement and embrittlement. If a strong attrition treatment is applied here, the contaminants can be stripped off together with the thinned and embrittled secondary minerals, and internal non-contaminated particles can be obtained. Therefore, since it is not necessary to dissolve the entire secondary mineral layer, it is possible to obtain a clean product from soil that cannot be dealt with by ordinary attrition treatment alone, with a smaller amount of acid input and treatment time compared to a simple dissolution treatment. is there.
【0015】本発明における強いアトリション処理と
は、ドラム型スクラバーや、ドラムウォッシャー、窯業
原料の選鉱時に用いられるアトリションマシンなどの装
置を用いて回転数30〜100回/分で、5〜60分間
行って実施するものであり、これにより強いアトリショ
ンを汚染土壌に対してより効率的に加えることができ
る。しかしドラム型スクラバーやドラムウォッシャーで
アトリション処理する場合には、液体を固液比6:4以
上の割合で加えるとアトリション効率が大きく低下する
ので、該割合未満でアトリション処理をする必要があ
る。この強いアトリション処理は酸を添加するのと同時
に実施することも、あるいは酸添加後放置して酸の作用
が進んでから実施することもできる。In the present invention, the strong attrition treatment is performed by using a device such as a drum type scrubber, a drum washer, and an attrition machine used for mineral processing of raw materials for ceramics at a rotation speed of 30 to 100 times / min. Minutes, so that strong attrition can be more efficiently added to the contaminated soil. However, when the attrition process is performed by a drum type scrubber or a drum washer, if the liquid is added at a solid-liquid ratio of 6: 4 or more, the attrition efficiency is greatly reduced. is there. This strong attrition treatment can be carried out simultaneously with the addition of the acid, or can be carried out after the addition of the acid and after the action of the acid has progressed.
【0016】[0016]
【実施例】次に本発明の実施例を、比較例とともに説明
する。硫化カドミウムと硫化鉛で汚染された粒径75〜
2000μmの砂に対して、実施例1、比較例1〜3の
4通りの処理を行った結果をまとめて表1に示す。19
97年現在での土壌汚染に関する基準としては、環境庁
の「重金属等に係る土壌汚染対策指針」があり、そこで
はCdに対しては9mg/kg、Pbに対しては600
mg/kgという含有量参考値が示されている。Next, examples of the present invention will be described together with comparative examples. Particle size 75 ~ contaminated with cadmium sulfide and lead sulfide
Table 1 summarizes the results of the four treatments of Example 1 and Comparative Examples 1 to 3 performed on 2000 μm sand. 19
The standards for soil contamination as of 1997 include the Environmental Agency's “Guidelines for Measures against Soil Pollution Related to Heavy Metals, etc.”, where 9 mg / kg for Cd and 600 mg for Pb.
Content reference values of mg / kg are shown.
【0017】実施例1 試験対象砂2kgを水480ミリリットル、14N硝酸
20ミリリットルとともに容積10リットルのドラム型
スクラバーへ投入し、回転数50回/分の酸添加強アト
リション処理を15分間行った後、目開き75μmの篩
で湿式分級し、粒径75μm以上の粒子を回収した。Example 1 2 kg of sand to be tested was put into a 10-liter drum type scrubber together with 480 ml of water and 20 ml of 14N nitric acid, and subjected to a strong acid addition treatment at 50 revolutions / minute for 15 minutes. And wet classification with a sieve having a mesh size of 75 μm to collect particles having a particle size of 75 μm or more.
【0018】比較例1 試験対象砂2kgを水500ミリリットルとともに容積
10リットルのドラム型スクラバ−へ投入し、回転数5
0回/分のアトリション処理を1時間行った後、目開き
75μmの篩で湿式分級し、粒径75μm以上の粒子を
回収した。Comparative Example 1 2 kg of sand to be tested was put into a 10-liter drum type scrubber together with 500 ml of water, and the number of rotations was 5
After performing attrition treatment 0 times / minute for 1 hour, wet classification was performed with a sieve having openings of 75 μm, and particles having a particle size of 75 μm or more were collected.
【0019】比較例2 試験対象砂2kgを水20リットル、14N硝酸200
ミリリットルとともに撹拌羽根付き水槽中に投入し、羽
根回転数700回/分の酸溶解処理を1時間行った後、
目開き75μmの篩で湿式分級し、粒径75μm以上の
粒子を回収した。COMPARATIVE EXAMPLE 2 2 kg of sand to be tested was weighed in 20 liters of water and 200 N of 14N nitric acid.
Milliliter and into a water tank with stirring blades, and after performing an acid dissolution treatment at a blade rotation speed of 700 times / minute for 1 hour,
Wet classification was performed with a sieve having an opening of 75 μm, and particles having a particle size of 75 μm or more were collected.
【0020】比較例3 試験対象砂2kgを水1980ミリリットル、14N硝
酸20ミリリットルとともに容積10リットルのドラム
型スクラバーへ投入し、回転数50回/分の酸添加アト
リション処理を15分間行った後、目開き75μmの篩
で湿式分級し、粒径75μm以上の粒子を回収した。Comparative Example 3 2 kg of sand to be tested was put into a 10-liter drum type scrubber together with 1980 ml of water and 20 ml of 14N nitric acid, and an acid addition treatment of 50 revolutions / minute was performed for 15 minutes. Wet classification was performed with a sieve having an opening of 75 μm, and particles having a particle size of 75 μm or more were collected.
【0021】[0021]
【表1】 [Table 1]
【0022】[0022]
【発明の効果】以上述べた通り本発明によれば、非汚染
粒子表面に固着した汚染物質を分離除去するための酸添
加強アトリション処理を組み入れたことにより、従来の
単なるアトリション処理や酸溶解処理では浄化できない
汚染物質が非汚染粒子表面に強固に固着した土壌から効
率よく清浄土を取り出すことができるようになり、また
従来の処理方法よりも所要時間が短縮されたり、所要試
薬量を節減することができる効果がある。As described above, according to the present invention, an acid-added strong attrition treatment for separating and removing contaminants adhered to the surface of non-contaminated particles is incorporated. It is possible to efficiently remove clean soil from soil in which contaminants that cannot be purified by dissolution treatment are firmly adhered to the surface of non-contaminated particles, and the required time is shorter than the conventional treatment method, and the amount of reagent required is reduced. There is an effect that can be saved.
Claims (1)
する方法において、該汚染土壌に酸を添加するのと同
時、または添加後に強いアトリション処理を加えること
を特徴とする汚染土壌の洗浄方法。1. A method for cleaning soil contaminated with heavy metals or the like, wherein a strong attrition treatment is performed simultaneously with or after the acid is added to the contaminated soil.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP01799198A JP3891372B2 (en) | 1998-01-14 | 1998-01-14 | How to clean contaminated soil |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP01799198A JP3891372B2 (en) | 1998-01-14 | 1998-01-14 | How to clean contaminated soil |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH11197643A true JPH11197643A (en) | 1999-07-27 |
JP3891372B2 JP3891372B2 (en) | 2007-03-14 |
Family
ID=11959204
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP01799198A Expired - Fee Related JP3891372B2 (en) | 1998-01-14 | 1998-01-14 | How to clean contaminated soil |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP3891372B2 (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2013178147A (en) * | 2012-02-28 | 2013-09-09 | Shimizu Corp | Washing processing method for cesium contaminated soil |
JP2013178148A (en) * | 2012-02-28 | 2013-09-09 | Shimizu Corp | Washing processing method for cesium contaminated soil |
JP2013248559A (en) * | 2012-05-31 | 2013-12-12 | Shimizu Corp | Method for cleaning heavy metal contaminated soil |
JP2014035333A (en) * | 2012-08-10 | 2014-02-24 | Shimizu Corp | Decontamination treatment method for burned ash |
-
1998
- 1998-01-14 JP JP01799198A patent/JP3891372B2/en not_active Expired - Fee Related
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2013178147A (en) * | 2012-02-28 | 2013-09-09 | Shimizu Corp | Washing processing method for cesium contaminated soil |
JP2013178148A (en) * | 2012-02-28 | 2013-09-09 | Shimizu Corp | Washing processing method for cesium contaminated soil |
JP2013248559A (en) * | 2012-05-31 | 2013-12-12 | Shimizu Corp | Method for cleaning heavy metal contaminated soil |
JP2014035333A (en) * | 2012-08-10 | 2014-02-24 | Shimizu Corp | Decontamination treatment method for burned ash |
Also Published As
Publication number | Publication date |
---|---|
JP3891372B2 (en) | 2007-03-14 |
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