JP2002136962A - Decontamination method for contaminated soil and system therefor - Google Patents

Decontamination method for contaminated soil and system therefor

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Publication number
JP2002136962A
JP2002136962A JP2001183955A JP2001183955A JP2002136962A JP 2002136962 A JP2002136962 A JP 2002136962A JP 2001183955 A JP2001183955 A JP 2001183955A JP 2001183955 A JP2001183955 A JP 2001183955A JP 2002136962 A JP2002136962 A JP 2002136962A
Authority
JP
Japan
Prior art keywords
soil
surfactant
washing
ice
water
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
JP2001183955A
Other languages
Japanese (ja)
Other versions
JP4636738B2 (en
Inventor
Naohito Okamoto
尚人 岡本
Katsumi Fujima
克己 藤間
Gakuo Kanazawa
岳夫 金沢
Shinichi Yamagami
伸一 山上
Shigesuke Iwabori
恵祐 岩堀
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.)
Mayekawa Manufacturing Co
Original Assignee
Mayekawa Manufacturing Co
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 Mayekawa Manufacturing Co filed Critical Mayekawa Manufacturing Co
Priority to JP2001183955A priority Critical patent/JP4636738B2/en
Publication of JP2002136962A publication Critical patent/JP2002136962A/en
Application granted granted Critical
Publication of JP4636738B2 publication Critical patent/JP4636738B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To provide a method and a system, which can surely remove contaminants from contaminated soil and efficiently treat a large volume of waste water generated when the soil is decontaminated. SOLUTION: This soil decontamination system having a soil decontamination process 1 for decontaminating soil 20 contaminated with polycyclic aromatic hydrocarbons by using a surfactant, is provided with a surfactant separation means 14 for separating waste water, which is generated after the soil decontamination process 1 and contains the surfactant involving the polycyclic aromatic hydrocarbons, into the polycyclic aromatic hydrocarbons and the surfactant by cooling the temperature of the waste water to the Krafft temperature of the surfactant or below and raising the temperature to the cloudpoint or above or by using ultrasonic waves, a freeze concentration means 13b for cooling and freezing waste water 31 containing the separated polycyclic aromatic hydrocarbons, an ice separating and melting means 13c for separating and melting ice which is generated by the freezing and does not contain the polycyclic aromatic hydrocarbons, and a wash water regulator 15 for generating wash water, which is supplied to a soil cleaner, by using the separated surfactant and water generated when the ice is melted.

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、対生態系有害物質
に汚染された土壌中から有害物質を分離除去する方法に
おいて、特に、界面活性剤を使用して土壌から対生態系
有害物質を分離する汚染土壌浄化方法及びその装置に関
する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for separating and removing harmful substances from soil contaminated with harmful substances against ecosystems, and more particularly to a method for separating harmful substances against ecosystems from soil using a surfactant. And a method for purifying contaminated soil.

【0002】[0002]

【従来の技術】従来より、産業廃棄物の不適切な取り扱
い、輸送途上の事故、農薬その他の化学物質の無知な使
用などにより土壌が汚染され、動植物を含む生態系に有
害な結果をもたらしている。急性毒性や変異原性の強い
化学物質はもちろんのこと、例え毒性のない炭化水素や
油脂類でも、生態系に適した環境を破壊し、生物の生存
を脅かす。これら有害物質は、例えば、鉛、六価クロ
ム、水銀などの重金属、農薬や殺虫剤に由来する有機金
属化合物や有機塩化物、電気産業から排出したPCBや
トリクレンなどの有機塩化物、焼却炉の残灰に含まれる
ダイオキシン類、機械工業などが排出する切削油や潤滑
油、タンカー事故による原油、原油精製工業からの各種
副生物やタールなど枚挙に遑がない。特に、都市交通や
コークス製造・アルミ精錬等から発生する多環芳香族炭
化水素類により汚染された土壌は極めて毒性が強いとさ
れている。これら有害物質は植物や土壌中の生物に害を
与えるのみならず、有害物質が地下水や河川等に溶解し
て水質を汚染し、大気中に揮発して拡散して大気を汚染
するので、人その他の生物にも悪影響をおよぼすことと
なる。特に多環芳香族炭化水素類は、近年、石油及び石
炭等の化石燃料を製造するためのプラントから環境中へ
の放出量増加が認められており、該多環芳香族炭化水素
類の持つ発癌性あるいは突然変異を誘発する変異原性の
人体及び環境に及ぼす影響が懸念されている。
2. Description of the Related Art Conventionally, soil is contaminated by improper handling of industrial waste, transportation accidents, ignorant use of pesticides and other chemical substances, and the like, resulting in harmful effects on ecosystems including animals and plants. I have. Even nontoxic hydrocarbons and oils, as well as highly toxic and mutagenic chemicals, destroy ecologically friendly environments and threaten the survival of living organisms. These harmful substances include, for example, heavy metals such as lead, hexavalent chromium and mercury, organometallic compounds and organic chlorides derived from pesticides and pesticides, organic chlorides such as PCB and trichlene discharged from the electric industry, and incinerators. Dioxins contained in the residual ash, cutting oil and lubricating oil discharged by the machinery industry, crude oil from tanker accidents, various by-products and tar from the crude oil refining industry, and so on. In particular, soil contaminated with polycyclic aromatic hydrocarbons generated from city traffic, coke production, aluminum smelting, and the like is considered to be extremely toxic. These harmful substances not only harm plants and organisms in the soil, but also dissolve in groundwater and rivers and contaminate water quality, and volatilize and diffuse into the air to pollute the air. Other organisms are also adversely affected. In particular, in recent years, an increase in the amount of polycyclic aromatic hydrocarbons released into the environment from plants for producing fossil fuels such as petroleum and coal has been recognized, and the carcinogenicity of the polycyclic aromatic hydrocarbons has been recognized. There is a concern about the effects on humans and the environment of gender or mutagenicity that induces mutations.

【0003】このような土壌汚染に対して、従来は、汚
染土壌を粉砕して空気を通すことにより対象物質を除去
する風乾法や汚染土壌をコンクリートにより封じ込める
固化、安定化法、低温若しくは高温で熱処理する熱分
解、熱脱着法、また汚染土壌に水、栄養分、空気等を供
給して土着の微生物により分解させる微生物分解処理法
などが用いられてきた。しかし、前記風乾法では有害物
質が土壌中に残留する可能性があるばかりであなく、大
気汚染の原因となる。固化、安定化法では処理後の汚染
物質の漏洩を経時的に監視する必要がある上に、大量の
土壌の処理が困難であるという問題を有している。また
熱分解、熱脱着法では有機塩化物系化合物の燃焼により
発生するダイオキシンの処理が必要となりコスト高とな
る。さらに、微生物分解処理法は低コストではあるが処
理時間が長く、実用性がない。
Conventionally, for such soil contamination, an air drying method in which the contaminated soil is removed by pulverizing the contaminated soil and passing air, a solidification and stabilization method in which the contaminated soil is sealed with concrete, or a method using a low or high temperature. Thermal decomposition and thermal desorption methods of heat treatment, and microbial decomposition treatment methods of supplying water, nutrients, air, and the like to contaminated soil to decompose them by indigenous microorganisms have been used. However, in the air drying method, not only harmful substances may remain in soil but also cause air pollution. The solidification and stabilization methods have a problem that it is necessary to monitor the leakage of contaminants after the treatment over time, and that it is difficult to treat a large amount of soil. In the thermal decomposition and thermal desorption methods, dioxin generated by the combustion of the organic chloride-based compound must be treated, which increases the cost. Further, the microbial decomposition treatment method is low in cost but long in treatment time, and is not practical.

【0004】そこで、このような土壌中の有害な有機化
合物の処理方法として、掘削した汚染土壌に界面活性剤
やアルカリ等を加えて水で洗浄し、汚染物質を抽出する
方法が提案されている。その一つとして、特開平9−7
5907号に界面活性剤を用いた土壌浄化方法が提案さ
れている。これは、有機化合物で汚染された土壌を掘削
し、攪拌槽にて該掘削土壌に所定濃度の界面活性剤溶液
を加えて攪拌混合して汚染物質を脱離し、脱離終了後、
固液分離装置により土壌と界面活性剤溶液を分離する方
法である。このようにして界面活性剤溶液を分離した土
壌は掘削場所へ戻し、界面活性剤溶液は活性炭吸着槽に
て汚染物質を除去した後再利用する。
Accordingly, as a method for treating harmful organic compounds in such soil, a method has been proposed in which a surfactant, an alkali, or the like is added to excavated contaminated soil, washed with water, and contaminants are extracted. . As one of them, JP-A-9-7
No. 5907 proposes a soil purification method using a surfactant. This is to excavate soil contaminated with organic compounds, add a surfactant solution of a predetermined concentration to the excavated soil in a stirring tank, stir and mix to desorb contaminants, and after the desorption is completed,
This is a method for separating a surfactant solution from soil by a solid-liquid separation device. The soil from which the surfactant solution has been separated in this way is returned to the excavation site, and the surfactant solution is reused after removing pollutants in an activated carbon adsorption tank.

【0005】かかる界面活性剤を用いた処理方法では、
土壌浄化処理においてはコスト的にも安価で簡易な処理
が可能であるが、その一方土壌の洗浄の際に大量の汚染
水が発生するという問題を有しており、土壌洗浄設備に
高い処理能力を備える排水処理設備を併設する必要があ
る。かかる問題を解決するために特開平10−2166
93号では、図3に示すように、化学洗浄剤が添加され
た洗浄水Wを湛える洗浄槽02内に汚染土壌Bを収容し
て化学洗浄することにより汚染土壌Bから汚染物質Aを
分離させた後、空気中の気体成分が過分に溶解した過飽
和水を洗浄槽02内に供給して洗浄水W中に微細気泡を
発生させ、この微細気泡を汚染物質Aに付着させること
により汚染物質Aを洗浄水Wの水面に浮かび上がらせて
回収する汚染物質分離方法を提案している。
In the treatment method using such a surfactant,
In the case of soil purification treatment, it is inexpensive and simple treatment is possible, but on the other hand, there is a problem that a large amount of contaminated water is generated when soil is washed. It is necessary to add a wastewater treatment facility equipped with To solve such a problem, Japanese Patent Application Laid-Open No. H10-2166
In No. 93, as shown in FIG. 3, the contaminated soil B is accommodated in the cleaning tank 02 filled with the cleaning water W to which the chemical cleaning agent has been added, and the contaminated soil A is separated from the contaminated soil B by chemical cleaning. After that, supersaturated water in which the gas component in the air is excessively dissolved is supplied into the cleaning tank 02 to generate fine bubbles in the cleaning water W. A method of separating contaminants that floats on the surface of the washing water W and recovers the pollutants is proposed.

【0006】[0006]

【発明が解決しようとする課題】しかしながら、かかる
方法では、上記記載のごとく簡略化された洗浄処理シス
テムにより設備コストの大幅な削減が可能となるが、土
壌の種類によっては洗浄槽中での気泡の発生により、汚
染物質とともに土壌が浮遊して回収されてしまい最終的
な汚染物質の処理量が増加したり、逆に、洗浄槽内が常
に流動状態にあるため下部の土壌中に汚染物質が僅かに
残留する惧れがあり、本発明における被処理物質である
多環芳香族炭化水素のように微量でも非常に毒性の強い
汚染物質の処理には適さない。したがって、本発明はか
かる従来技術の課題に鑑み、界面活性剤を用いた土壌洗
浄により排出される大量の排水から確実に有害物質を分
離することが可能で、かつ洗浄に用いられる水を循環利
用でき、排水処理を含む土壌浄化処理を効率良く行うこ
とが可能な汚染土壌浄化方法及びその装置を提供するこ
とを目的とする。
However, in such a method, the facility cost can be greatly reduced by the simplified cleaning system as described above, but depending on the type of soil, air bubbles in the cleaning tank may be reduced. As a result, the soil is suspended and collected together with the contaminants, and the final treatment amount of the contaminants is increased. There is a possibility that they will remain slightly, and they are not suitable for treating very toxic contaminants even in trace amounts, such as the polycyclic aromatic hydrocarbons to be treated in the present invention. Accordingly, the present invention has been made in view of the problems of the related art, and it is possible to reliably separate harmful substances from a large amount of wastewater discharged by soil washing using a surfactant, and to circulate water used for washing. It is an object of the present invention to provide a method and an apparatus for contaminated soil purification that can efficiently perform soil purification treatment including wastewater treatment.

【0007】[0007]

【課題を解決するための手段】本発明はかかる課題を解
決するために、界面活性剤水溶液を用いて対生態系有害
物質で汚染された土壌を洗浄する洗浄工程と、浄化土壌
からなる固相と当該有害物質を取込んだ乳化物を含む界
面活性剤水溶液からなる液相とに固液分離する固液分離
工程とを有する汚染土壌浄化方法において、前記固液分
離した液相を冷却、凍結させて氷を生成させることによ
り当該有害物質を前記液相中に濃縮するとともに、当該
有害物質が除かれた前記氷を融解し、生成した水を前記
土壌洗浄に再循環利用することを特徴とする。
In order to solve the above-mentioned problems, the present invention provides a washing step for washing soil contaminated with harmful substances against ecosystems using an aqueous solution of a surfactant, and a solid phase comprising purified soil. And a solid-liquid separation step of solid-liquid separation into a liquid phase comprising a surfactant aqueous solution containing an emulsion incorporating the harmful substance, wherein the solid-liquid separated liquid phase is cooled and frozen. Concentrating the harmful substance in the liquid phase by generating ice, melting the ice from which the harmful substance has been removed, and recycling the generated water for the soil washing. I do.

【0008】ここに言う対生態系有害物質とは、急性毒
性や変異原性・催奇性のある化学物質及び生物に付着若
しくは経口進入して、呼吸、発汗、運動、消化吸収機能
など生命維持に必要な諸機能を阻害する物質をいう。前
者に属するものが、例えば、鉛、水銀、六価クロムのよ
うな無機物、有機水銀や有機錫化合物のような有機金属
化合物、トリクロロエチレン、テトラクロロエチレン、
ポリ塩化ビフェニル、6塩化ベンゼンのような有機塩化
物、アントラセン、フェナントレン、ピレン、フルオラ
ンテン、クリセン、ベンゾピレン、ペリレンのような多
環式芳香族炭化水素、後者に属するものが、例えば、原
油、原油精製溜分、鉱油、タールのような原油由来物質
などがある。
[0008] The harmful substances against ecosystems referred to herein are chemical substances having acute toxicity, mutagenicity and teratogenicity, and adhere to or invade organisms, and are useful for sustaining life such as respiration, sweating, exercise, digestion and absorption functions. A substance that inhibits various necessary functions. Those belonging to the former include, for example, lead, mercury, inorganic substances such as hexavalent chromium, organometallic compounds such as organic mercury and organotin compounds, trichloroethylene, tetrachloroethylene,
Organic chlorides such as polychlorinated biphenyls and hexachlorobenzenes; polycyclic aromatic hydrocarbons such as anthracene, phenanthrene, pyrene, fluoranthene, chrysene, benzopyrene and perylene; those belonging to the latter, for example, crude oil, crude oil refining There are crude oil derived substances such as distillate, mineral oil and tar.

【0009】前記した有害な物質には水溶性のものも含
まれるが、多くは水不溶性のものが多く、いずれにせ
よ、土壌粒子に吸着されているので、限られた時間と水
で土壌を洗浄するには土壌粒子表面の濡れを高めて吸着
している有害物を離脱させ、可溶化若しくは乳化によっ
て、水相に分散せしめて、土壌粒子表面の有害物濃度を
低下させる機能を有する界面活性剤の使用は不可欠であ
る。
Although the above harmful substances include water-soluble substances, many of them are water-insoluble substances. In any case, since the harmful substances are adsorbed on soil particles, the soil can be removed for a limited time and with water. In order to wash, surface activity has the function of increasing the wetting of the soil particle surface, removing adsorbed harmful substances, dissolving or emulsifying and dispersing in the aqueous phase, and reducing the concentration of harmful substances on the surface of soil particles. The use of agents is essential.

【0010】界面活性剤には、一般に知られている陰イ
オン界面活性剤、陽イオン界面活性剤、両性界面活性
剤、非イオン界面活性剤のいずれも使用することができ
る。更に具体的には例えば、脂肪酸ナトリウム、硫酸ア
ルキル塩、硫酸アルキルポリオキシエチレン塩、アルキ
ルベンゼンスルホン酸塩、α―オレフィンスルホン酸、
のような陰イオン界面活性剤、アルキルトリメチルアン
モニュウム塩、トリエタノールアミン・ジ脂肪酸エステ
ル四級塩のような陽イオン界面活性剤、アルキルジメチ
ルアミンオキシド、アルキルカルボキシベタイン、アミ
ドアミノ酸塩のような両性イオン界面活性剤、ポリオキ
シエチレンアルキルエーテル、ポリオキシエチレンアル
キルフェニルエーテル、脂肪酸ポリオキシエチレンエス
テル、脂肪酸ソルビタンエステルのような非イオン界面
活性剤の中から選ぶことができ、二種以上を組み合わせ
て用いることもできる。
As the surfactant, any of generally known anionic surfactants, cationic surfactants, amphoteric surfactants and nonionic surfactants can be used. More specifically, for example, fatty acid sodium, alkyl sulfate, alkyl polyoxyethylene sulfate, alkyl benzene sulfonate, α-olefin sulfonic acid,
Anionic surfactants, such as cationic surfactants, such as alkyltrimethylammonium salts, triethanolamine / difatty acid ester quaternary salts, zwitterions, such as alkyldimethylamine oxides, alkylcarboxybetaines, and amide amino acid salts Can be selected from nonionic surfactants such as surfactants, polyoxyethylene alkyl ethers, polyoxyethylene alkyl phenyl ethers, fatty acid polyoxyethylene esters, and fatty acid sorbitan esters, and use in combination of two or more. Can also.

【0011】特に、土壌中にはカルシウムイオンなど、
界面活性剤のクラフト点を下げてその機能効果を低減さ
せるような、金属イオンがふくまれるので、これらの金
属イオンと高い反応性を持つキレート剤やゼオライトな
どの金属封鎖剤を併用することも好ましい。
In particular, calcium ions and the like in the soil
Since metal ions are included, such as lowering the Kraft point of the surfactant and reducing its functional effect, it is also preferable to use a sequestering agent such as a chelating agent or zeolite having high reactivity with these metal ions. .

【0012】そして本発明は、界面活性剤により土壌と
分離された有害物質を含む排水を、冷凍機等により冷却
して凍結させ、不純物を含まない真氷を生成させること
により界面活性剤及び有害物質等の不純物を濃縮し、前
記真氷を融解して生成した水を土壌洗浄に再循環利用す
ることにより、水と界面活性剤及び有害物質を確実に分
離することが可能となり、さらに水の再利用が容易に可
能となるために、コストが低減するとともに効率の良い
土壌洗浄が可能となる。尚、前記排水を凍結させる際に
は、該排水中に微細気泡を放出して絶えず空気で攪拌動
揺させるとよい。そうすることにより、排水中の水の結
晶の核周辺は常に物質移動が頻繁に行われるので、続い
て精製する結晶が純粋な水の結晶のみとなり、これによ
り排水の不純物濃縮、精製が効率よく行われる。
According to the present invention, the wastewater containing harmful substances separated from the soil by the surfactant is cooled and frozen by a refrigerator or the like to produce true ice free of impurities, thereby producing the surfactant and the harmful wastewater. By concentrating impurities such as substances and recycling the water generated by melting the true ice for soil washing, it is possible to reliably separate water, surfactants and harmful substances. Since re-use can be easily performed, cost can be reduced and efficient soil cleaning can be performed. When the wastewater is frozen, fine bubbles are preferably released into the wastewater and constantly stirred and shaken by air. By doing so, mass transfer is always carried out frequently around the nucleus of the water crystal in the wastewater, so that the crystal to be subsequently purified is only pure water crystal, thereby efficiently concentrating impurities in the wastewater and purifying efficiently. Done.

【0013】更に本発明の汚染土壌浄化方法は、前記分
離した液相を、含有界面活性剤のクラフト点以下に冷却
するか、曇点以上に昇温するか、超音波を照射すること
により、液相の有害物質の可溶化若しくは乳化を破壊し
て上層と下層に二層分離し、当該有害物質を含む下層は
冷却、凍結して氷を生成させることにより当該有害物質
を前記下層中に濃縮するとともに、当該有害物質が除か
れた前記氷を融解し、生成した水を前記土壌洗浄に再循
環利用することを特徴とする。
Further, in the method for purifying contaminated soil according to the present invention, the separated liquid phase is cooled to a temperature lower than the Kraft point of the contained surfactant, heated to a temperature higher than the cloud point, or irradiated with ultrasonic waves. The solubilization or emulsification of the liquid phase harmful substance is destroyed and the upper layer and the lower layer are separated into two layers, and the lower layer containing the harmful substance is cooled and frozen to form ice to concentrate the harmful substance in the lower layer. And melting the ice from which the harmful substances have been removed, and recycling the generated water for the soil washing.

【0014】これは、前記界面活性剤により汚染土壌を
洗浄処理した後の排水を、凍結させる前にクラフト点以
下に冷却することで、イオン性界面活性剤のミセル形成
による溶解度を大幅に減少させて該界面活性剤を分離さ
せる工程を含むものである。クラフト点とは、周知のよ
うに界面活性剤の水中でのミセル形成による溶解度が急
激に増大する温度のことで、通常、この温度以上で界面
活性剤を使用しないと溶解度が小さく、役に立たない。
一方、非イオン性界面活性剤は、曇点以上の温度で溶解
度が急激に低下する。
[0014] This is because the wastewater after washing the contaminated soil with the surfactant is cooled to a point below the Kraft point before freezing, thereby greatly reducing the solubility of the ionic surfactant due to micelle formation. And the step of separating the surfactant. The Krafft point is, as is well known, a temperature at which the solubility of a surfactant due to micelle formation in water sharply increases. Usually, if the surfactant is not used at a temperature higher than this temperature, the solubility is small and useless.
On the other hand, the solubility of the nonionic surfactant rapidly decreases at a temperature higher than the cloud point.

【0015】また、このようにして分離した界面活性剤
は比重が水より小さいため上層に溜まり、一方比重の水
より大きい有害物質若しくは水溶性の有害物質は下層に
移行するため、二層に分離した排水のうち界面活性剤を
含む上層は再度循環使用することができるのでコストの
削減を図ることができる。さらに有害物質と界面活性剤
とが分離するため、次工程での有害物質処理が容易にな
る。即ち本発明の汚染土壌浄化方法の更なる特徴は、前
記二層分離して有害物質が除かれた界面活性剤を前記土
壌洗浄に再循環利用することを特徴とする。
The surfactant separated in this way has a lower specific gravity than water and accumulates in the upper layer. On the other hand, harmful substances or water-soluble harmful substances having a specific gravity higher than water migrate to the lower layer and are separated into two layers. The upper layer containing the surfactant in the waste water can be recycled and used again, so that the cost can be reduced. Furthermore, since the harmful substance and the surfactant are separated, the treatment of the harmful substance in the next step becomes easy. That is, a further feature of the method for purifying contaminated soil of the present invention is that the two-layer separated surfactant from which harmful substances have been removed is recycled and used for the soil washing.

【0016】さて、前記固液分離によって得られた有害
物質を取り込んだ液相中の、当該有害物質が水不溶性で
且つ比重が水より小さい場合は、前記含有界面活性剤の
クラフト点以下に降温したり、超音波の作用により界面
活性剤および有害物質を分離析出させる操作をしたと
き、当該有害物質は界面活性剤とともに、上層に移行す
る。この場合、界面活性剤と有害物質との分離は別の方
法で行うか、若しくは上層界面活性剤とも別途分解工程
へ移送して無害化する必要がある。
When the harmful substance in the liquid phase containing the harmful substance obtained by the solid-liquid separation is water-insoluble and has a specific gravity smaller than water, the temperature is lowered to the Kraft point of the surfactant contained. When an operation of separating or depositing a surfactant and a harmful substance by the action of ultrasonic waves is performed, the harmful substance moves to the upper layer together with the surfactant. In this case, it is necessary to separate the surfactant and the harmful substance by another method, or to transfer the surfactant and the upper layer surfactant separately to a decomposing step to make them harmless.

【0017】また、本発明による土壌の洗浄処理は処理
の条件によっては必ずしも一度の回分操作で所望の浄化
が得られない場合もあり得る。即ち、処理器の大きさ、
一度に処理すべき土壌の量、これによって限られる使用
可能な水の量、界面活性剤の能力や濃度によって、処理
率((初期土壌汚染濃度−処理後土壌汚染濃度)×10
0/初期土壌汚染濃度)は100%とはならず、条件に
よって異なる。このような場合、設定した土壌の最終到
達汚染濃度に応じて、複数回の洗浄を繰り返す多段処理
によって処理目的を達成することができる。即ち、更に
本発明の汚染土壌浄化方法の特徴とするところは、前記
固液分離した固相を前記洗浄工程に戻し、洗浄工程と固
液分離工程を複数回繰り返す、多段洗浄を行うことにあ
る。
Further, in the soil washing treatment according to the present invention, a desired purification may not always be obtained by a single batch operation depending on treatment conditions. That is, the size of the processor,
Depending on the amount of soil to be treated at one time, the amount of available water limited by this, the capacity and concentration of the surfactant, the treatment rate ((initial soil contamination concentration-soil contamination concentration after treatment)) x 10
0 / initial soil contamination concentration) is not 100% and varies depending on conditions. In such a case, the processing object can be achieved by multi-stage processing in which washing is repeated a plurality of times according to the set final arrival contamination concentration of the soil. That is, a further feature of the method for purifying contaminated soil of the present invention is to perform multi-stage washing in which the solid-liquid separated solid phase is returned to the washing step, and the washing step and the solid-liquid separation step are repeated a plurality of times. .

【0018】例えば、前記制約条件により、一度の洗浄
処理による到達処理率が90%しか得られず、1000
ppmの汚染物質濃度で汚染された、汚染土壌を1pp
m以下の最終到達汚染濃度まで下げたいとき、n回以上
繰り返す多段洗浄を行うべきとすれば、 (1−0.9)n×1000ppm≦1ppm 10−n≦10−3 ∴n≧3 即ち、3回以上洗浄すれば目的は達せられることにな
る。
For example, due to the above-mentioned constraints, only 90% of the reaching processing rate can be obtained by one cleaning processing,
1pp contaminated soil contaminated with ppm contaminant concentration
When it is desired to perform the multi-stage cleaning to be repeated n times or more when it is desired to reduce the concentration to the final attainment concentration of m or less, (1-0.9) n × 1000 ppm ≦ 1 ppm 10−n ≦ 10−3 ∴n ≧ 3 The purpose can be achieved by washing three or more times.

【0019】これらの発明を効果的に実施する装置の発
明として、本発明は、界面活性剤水溶液を用いて対生態
系有害物質で汚染された土壌を洗浄する土壌洗浄手段を
具えた土壌浄化装置において、前記土壌洗浄後の、当該
有害物質を取り込んだ界面活性剤を含む排水を冷却して
凍結させる凍結濃縮手段と、凍結により生成した界面活
性剤を含まない真氷を分離して融解する氷分離融解手段
と、を具えるとともに、前記氷分離融解手段により生成
した水を前記土壌洗浄手段に返送して再利用することを
特徴とする。
As an invention of an apparatus for effectively implementing these inventions, the present invention relates to a soil purification apparatus provided with a soil washing means for washing soil contaminated with ecologically harmful substances using an aqueous solution of a surfactant. A freeze-concentrating means for cooling and freezing wastewater containing the surfactant incorporating the harmful substance after the soil washing, and ice for separating and melting the surfactant-free true ice generated by freezing Separating and melting means, and water produced by the ice separating and melting means is returned to the soil washing means for reuse.

【0020】さらに、本発明の汚染土壌浄化装置は界面
活性剤水溶液を用いて対生態系有害物質で汚染された土
壌を洗浄する土壌洗浄手段を具えた土壌浄化装置におい
て、前記土壌洗浄後の、当該有害物質を取り込んだ界面
活性剤を含む排水を冷却して凍結させる凍結濃縮手段
と、凍結により生成した界面活性剤を含まない真氷を分
離して融解する氷分離融解手段と、を具えるとともに、
前記氷分離融解手段により生成した水を前記土壌洗浄手
段に返送して再利用することを特徴とする。
Further, the present invention provides a soil purification apparatus provided with soil washing means for washing soil contaminated with ecologically harmful substances using an aqueous solution of a surfactant, Freeze-concentrating means for cooling and freezing wastewater containing a surfactant incorporating the harmful substance, and ice separation and melting means for separating and melting true ice free of surfactant generated by freezing. With
The water generated by the ice separating and melting means is returned to the soil washing means for reuse.

【0021】また、前記汚染土壌浄化装置において、更
に本発明は、前記凍結濃縮手段と前記氷分離融解手段と
が、ヒートポンプの放熱/吸熱サイクルにより同一槽で
行われることを特徴とする。これにより、前記凍結濃縮
手段と氷分離融解手段とを兼ね備えた槽に、ヒートポン
プサイクル/冷凍サイクルを交互に形成させる構成とす
ることで、真氷の移動を省き簡易な設備となり、かつ設
置面積が削減する。
Further, in the above-mentioned contaminated soil purification apparatus, the present invention is further characterized in that the freeze-concentrating means and the ice separating / thawing means are performed in the same tank by a heat radiation / heat absorption cycle of a heat pump. With this configuration, a heat pump cycle / refrigeration cycle is alternately formed in a tank having both the freeze-concentrating means and the ice separating / thawing means. Reduce.

【0022】さらにまた、本発明は前記氷分離融解手段
にて氷の融解を凝縮器側で、前記凍結濃縮手段にて排水
の凍結を蒸発器側で行うとともに、前記界面活性剤分離
手段での界面活性剤を含む排水のクラフト点温度以下へ
の冷却に前記氷の融解水を利用し、前記凍結濃縮時の凝
縮熱を前記洗浄水調整器の加温熱源と前記界面活性剤分
離手段での界面活性剤を含む排水の曇点以上への昇温と
に利用するヒートポンプで連結したことを特徴とする。
Still further, according to the present invention, ice is melted on the condenser side by the ice separation and melting means, and wastewater is frozen on the evaporator side by the freeze concentration means. The melting water of the ice is used for cooling the wastewater containing the surfactant to a temperature below the Kraft point, and the heat of condensation at the time of the freeze concentration is heated by the heating heat source of the washing water regulator and the surfactant separating means. It is characterized by being connected by a heat pump used to raise the temperature of the wastewater containing surfactant to a temperature higher than the cloud point.

【0023】前記洗浄水調整器は界面活性剤の溶解度を
増加させるためにクラフト点以上に保持する必要があ
り、一方、界面活性剤分離手段では該界面活性剤を浮遊
分離させるためにクラフト点以下あるいは曇点に保たな
ければならない。そこで、かかる発明では、イオン性界
面活性剤を用いたときは、氷の生成時の凝縮熱を前記洗
浄水調整器に導き温度を上昇させ、また氷の融解により
生成した低温の融解水を前記界面活性剤分離手段に導い
て該界面活性剤分離手段を低温に維持し、非イオン性界
面活性剤を用いたときは、氷の生成時の凝縮熱を利用す
ることにより、熱効率のよい土壌浄化装置を提供するこ
とが可能となる。尚、上記したように氷の融解水からの
冷熱を利用して界面活性剤分離手段を冷却する方法とは
別に、氷を融解する際の融解熱を利用して冷却する方法
を利用してもよい。
The washing water conditioner must be maintained at a temperature higher than the Kraft point in order to increase the solubility of the surfactant. On the other hand, the surfactant separating means requires a temperature lower than the Kraft point to suspend and separate the surfactant. Alternatively, it must be kept at the cloud point. Therefore, in this invention, when an ionic surfactant is used, heat of condensation at the time of generation of ice is led to the washing water regulator to raise the temperature, and low-temperature molten water generated by melting of ice When the non-ionic surfactant is used, the heat is condensed during the formation of ice, and the soil is purified with high thermal efficiency. A device can be provided. Incidentally, apart from the method of cooling the surfactant separating means using the cold heat from the melting water of ice as described above, it is also possible to use a method of cooling using the heat of melting when melting the ice. Good.

【0024】更に本発明の汚染土壌浄化装置は、前記洗
浄工程と固液分離工程間で、前記固液分離した固相を前
記洗浄工程に戻し、洗浄工程と固液分離工程を複数回繰
り返す、多段洗浄を行うための戻入手段を備えたことを
特徴とする。
Further, the contaminated soil purification apparatus of the present invention returns the solid-liquid separated solid phase to the washing step between the washing step and the solid-liquid separation step, and repeats the washing step and the solid-liquid separation step a plurality of times. A return means for performing multi-stage cleaning is provided.

【0025】戻入手段は、固液分離器の固相排出口に接
続し、土壌洗浄器の土壌投入口へと固相を導く、ベルト
コンベヤ、スクリューコンベヤ、バケットコンベヤ等の
移送手段を含めて構成することができる。
The return means includes a transfer means such as a belt conveyor, a screw conveyor, a bucket conveyor, etc., which is connected to the solid phase discharge port of the solid-liquid separator and guides the solid phase to the soil input port of the soil washer. can do.

【0026】[0026]

【発明の実施の形態】以下、図面を参照して本発明の好
適な実施例を例示的に詳しく説明する。但しこの実施例
に記載されている構成部品の寸法、材質、形状、その相
対的配置等は特に特定的な記載がない限りは、この発明
の範囲をそれに限定する趣旨ではなく、単なる説明例に
過ぎない。図1は本発明の第1実施形態にかかる土壌浄
化装置の全体構成図で、図2は第2実施形態の全体構成
図である。図1に示すように、本発明の第1実施形態に
かかる土壌浄化装置は、土壌洗浄工程1と凍結濃縮工程
3とから構成され、該土壌洗浄工程1は、土壌洗浄機1
0、固液分離器11、12、戻入手段35からなり、凍
結濃縮工程3は、貯留槽13a、凍結濃縮手段13b及
び氷分離融解手段13cからなる有害物質分離手段13
と冷凍・ヒートポンプ装置16とで構成される。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Preferred embodiments of the present invention will be illustratively described in detail below with reference to the drawings. However, the dimensions, materials, shapes, relative arrangements, and the like of the components described in this embodiment are not intended to limit the scope of the invention thereto, unless otherwise specified, and are merely illustrative examples. Not just. FIG. 1 is an overall configuration diagram of a soil purification device according to a first embodiment of the present invention, and FIG. 2 is an overall configuration diagram of a second embodiment. As shown in FIG. 1, the soil purification apparatus according to the first embodiment of the present invention includes a soil washing step 1 and a freeze concentration step 3, and the soil washing step 1 is a soil washing machine 1
0, solid-liquid separators 11, 12 and return means 35. The freeze-concentration step 3 comprises a harmful substance separation means 13 comprising a storage tank 13a, a freeze-concentration means 13b and an ice separation / thaw means 13c.
And a refrigeration / heat pump device 16.

【0027】前記土壌洗浄工程で土壌洗浄機10には、
例えば、有害物質を含有する汚染土壌20の投入口から
導入された該汚染土壌20を螺旋形スクリューの回転に
より下流側へ移動させるスクリューフィーダを用い、該
土壌洗浄機10の下流側に洗浄水供給口を設け、洗浄水
21及び界面活性剤を土壌投入口側へ通流させて汚染土
壌の洗浄が行われるようにする。また、固液分離器11
は前記土壌洗浄機10の下流側、つまり土壌排出口側に
設け、該土壌洗浄機10により洗浄が行われた土壌か
ら、ろ過により液体分を除くフィルタシックナー等を用
いるとよい。固液分離した土壌は例えばバケットコンベ
ヤなどの戻入手段35により再度土壌洗浄機に戻し入れ
洗浄を繰り返すことが出来るように構成する。さらに、
その下流側には沈澱により排水中に残留した土壌を分離
する固液分離器12を設ける。
In the soil washing step, the soil washer 10
For example, using a screw feeder that moves the contaminated soil 20 introduced from the inlet of the contaminated soil 20 containing harmful substances to the downstream side by rotating a helical screw, supplies washing water to the downstream side of the soil washer 10. An opening is provided, and the washing water 21 and the surfactant are caused to flow to the side of the soil input port so that the contaminated soil is washed. Also, the solid-liquid separator 11
It is preferable to use a filter thickener or the like provided downstream of the soil washer 10, that is, on the side of the soil discharge port, for removing the liquid component from the soil washed by the soil washer 10 by filtration. The solid-liquid separated soil is configured to be returned to the soil washer again by the return means 35 such as a bucket conveyor, and the washing can be repeated. further,
On the downstream side, a solid-liquid separator 12 for separating the soil remaining in the wastewater by settling is provided.

【0028】前記凍結濃縮工程は、有害物質を取り込ん
だ界面活性剤を含む排水から純水を分離する工程で、貯
留槽13a、凍結濃縮手段13b及び氷分離融解手段1
3cが併設された有害物質分離手段13と、冷凍・ヒー
トポンプ装置16とからなる。前記凍結濃縮手段13b
は、冷凍・ヒートポンプ装置16の蒸発器側に位置して
冷凍サイクル16aが形成されており、該凍結濃縮手段
13bに蓄えられた排水を冷却することにより純水を凍
結させて不純物と分離する構成となっている。一方、前
記氷分離融解手段13cは、前記冷凍・ヒートポンプ装
置16の凝縮器側に位置してヒートポンプサイクル16
bが形成され、これにより融解した純水29は前記土壌
洗浄機10に循環させて再利用する。
The freeze-concentration step is a step of separating pure water from wastewater containing a surfactant containing harmful substances. The storage tank 13a, the freeze-concentration means 13b, and the ice separation / thaw means 1
The refrigeration / heat pump device 16 includes a toxic substance separation means 13 provided with 3c. The freeze concentration means 13b
Has a configuration in which a refrigeration cycle 16a is formed on the evaporator side of the refrigeration / heat pump device 16, and the pure water is frozen and separated from impurities by cooling the wastewater stored in the freeze-concentrating means 13b. It has become. On the other hand, the ice separation and melting means 13c is located on the condenser side of the refrigeration /
As a result, the purified water 29 is circulated to the soil washer 10 for reuse.

【0029】尚、前記洗浄水21中に含まれる界面活性
剤は、陰イオン界面活性剤、陽イオン界面活性剤、非イ
オン界面活性剤のいずれを用いてもよく、例えばアルキ
ルベンゼンスルホン酸塩、アビエチン酸塩、脂肪酸せっ
けん、ポリオキシエチレンアルキルエーテル、ポリオキ
シエチレンノニルフェニルエーテル等、一種若しくは複
数組合わせて、汚染物質及び土壌に適した界面活性剤を
使用する。
The surfactant contained in the washing water 21 may be any of an anionic surfactant, a cationic surfactant, and a nonionic surfactant. For example, alkyl benzene sulfonate, abieticin A surfactant suitable for pollutants and soil is used in combination with one or more of acid salts, fatty acid soaps, polyoxyethylene alkyl ether, polyoxyethylene nonylphenyl ether, and the like.

【0030】次に、かかる第1実施形態における汚染土
壌の浄化工程を説明する。まず、有害物質を含有する汚
染土壌20を土壌洗浄機10に投入し、その下流側から
供給する洗浄水21との混合により該汚染土壌20から
有害物質を分離した後、水分を含む浄化土壌をフィルタ
で上下に仕切られた固液分離器11に導入して液体分を
除去する。一度の洗浄で有害物濃度が所定値に下がらな
い場合は、戻入手段35により、分離された土壌を再び
土壌洗浄機に戻して、洗浄を繰り返す。そして、浄化さ
れた土壌24は掘削現場に戻されたり、土壌利用場所へ
搬送されるなどして環境中に返還される。一方、前記土
壌洗浄機10を経て有害物質を取り込んだ界面活性剤を
含む排水23は、前記固液分離器11で浄化土壌から分
離された液体分26とともに固液分離器12に導かれ、
ここで液体中に残存する浄化土壌25を沈澱分離した
後、凍結濃縮工程3に送り出される。
Next, the step of purifying contaminated soil in the first embodiment will be described. First, the contaminated soil 20 containing a harmful substance is put into the soil washer 10, and the harmful substance is separated from the contaminated soil 20 by mixing with the washing water 21 supplied from the downstream side. The liquid is introduced into the solid-liquid separator 11 which is vertically separated by a filter to remove the liquid. If the concentration of the harmful substance does not fall to a predetermined value by one washing, the separated soil is returned to the soil washer again by the return means 35, and the washing is repeated. Then, the purified soil 24 is returned to the environment by being returned to the excavation site or transported to a soil use place. On the other hand, wastewater 23 containing a surfactant that has taken in harmful substances through the soil washer 10 is guided to the solid-liquid separator 12 together with the liquid component 26 separated from the purified soil by the solid-liquid separator 11,
Here, after the purified soil 25 remaining in the liquid is precipitated and separated, it is sent to the freeze concentration step 3.

【0031】前記土壌洗浄工程1から排出される有害物
質含有排水27は、バルブa、cとを開の状態にしてポ
ンプ18により有害物質分離手段13の貯留槽13aに
一時的に貯留され、所要量貯留された時点で凍結濃縮手
段13bに供給される。そして、該凍結濃縮手段13b
にて、前記冷凍・ヒートポンプ装置16により形成され
た冷凍サイクル16aの冷媒管に純水が氷結するため、
有害物質を取り込んだ界面活性剤が濃縮された排水は該
凍結濃縮手段13bの下部に溜まり、バルブa、cを閉
に、バルブb、eを開にした状態でポンプ18により有
害物質濃縮排水30として分解工程へ排出される。前記
排水30が完全に排出された後、バルブb、eを閉め、
凍結濃縮手段13bに今度はヒートポンプサイクル16
bを形成させて、氷分離融解手段13cとして機能させ
ることにより、冷媒管に氷結した氷を融解して純水を得
ることができる。ここで得た純水29は前記土壌洗浄工
程に返送して再利用する。
The wastewater 27 containing harmful substances discharged from the soil washing step 1 is temporarily stored in the storage tank 13a of the harmful substance separation means 13 by the pump 18 with the valves a and c opened. When the amount is stored, it is supplied to the freeze concentration means 13b. And the freeze concentration means 13b
Since pure water freezes on the refrigerant pipe of the refrigeration cycle 16a formed by the refrigeration / heat pump device 16,
The wastewater in which the surfactant containing the harmful substance is concentrated is collected in the lower part of the freeze concentration means 13b, and the harmful substance concentrated wastewater 30 is pumped by the pump 18 with the valves a and c closed and the valves b and e open. And discharged to the decomposition process. After the drainage 30 is completely discharged, the valves b and e are closed,
The heat pump cycle 16
By forming b and functioning as the ice separating and melting means 13c, ice frozen in the refrigerant tube can be melted to obtain pure water. The pure water 29 obtained here is returned to the soil washing step and reused.

【0032】このように、前記冷凍・ヒートポンプ装置
16により冷凍・ヒートポンプサイクルを交互に形成す
ることにより、後述する図2に示すように1つの槽で純
水を生成することもできるし、図1に示すように、2槽
若しくはそれ以上の槽を設置して夫々時間差をもって前
記凍結濃縮手段13b及び氷分離融解手段13cとする
ことで、前記土壌洗浄工程1から排出される大量の排水
を効率良く処理することができ、また、冷凍・ヒートポ
ンプ装置16の蒸発器側及び凝縮器側の熱エネルギを有
効に活用することができ、動力の無駄を低減することが
できる。
As described above, by alternately forming the refrigeration / heat pump cycle by the refrigeration / heat pump device 16, pure water can be generated in one tank as shown in FIG. As shown in FIG. 2, two or more tanks are installed and the freeze concentration means 13b and the ice separation and thawing means 13c are provided with a time difference, respectively, so that a large amount of wastewater discharged from the soil washing step 1 can be efficiently removed. The heat energy can be effectively used on the evaporator side and the condenser side of the refrigeration / heat pump device 16, and waste of power can be reduced.

【0033】また、図2の本発明における第2実施形態
は、上記した第1実施形態にさらに界面活性剤と有害物
質とを分離する工程を設けた装置で、土壌洗浄工程1と
凍結濃縮工程3と界面活性剤リサイクル工程2とからな
る。かかる第2実施形態において、土壌洗浄工程1は第
1実施形態と同様の構成となっている。界面活性剤リサ
イクル工程では、使用界面活性剤がイオン性の場合は水
溶液をクラフト点以下に冷却して分離し、使用界面活性
剤が非イオン性の場合は水溶液を逆に曇点以上に温めて
分離する必要がある。前記土壌洗浄工程1から排出され
る有害物質含有排水27の処理工程である界面活性剤リ
サイクル工程2は、界面活性剤分離手段14と洗浄水調
整器15とから構成され、該界面活性剤分離手段14は
使用した含有界面活性剤のクラフト点以下あるいは曇点
以上に維持されており、前記洗浄水調整器15は同クラ
フト点以上あるいは曇点以下に保たれている。これによ
り、前記界面活性剤分離手段14では界面活性剤の溶解
度が非常に低いため該界面活性剤が分離し、逆に洗浄水
調整器15では界面活性剤が溶解するようになってい
る。そして、次工程の凍結濃縮工程3では前記第1実施
形態と同様に、排水中の不純物を濃縮分離して純水を得
るように構成されている。
The second embodiment of the present invention shown in FIG. 2 is an apparatus in which a step of separating a surfactant and a harmful substance is further provided in the first embodiment described above. 3 and a surfactant recycling step 2. In the second embodiment, the soil washing step 1 has the same configuration as that of the first embodiment. In the surfactant recycling process, if the used surfactant is ionic, the aqueous solution is cooled below the Kraft point to separate it, and if the used surfactant is nonionic, the aqueous solution is heated to the cloud point or higher. Need to be separated. The surfactant recycling step 2, which is a processing step of the harmful substance-containing wastewater 27 discharged from the soil washing step 1, includes a surfactant separating means 14 and a washing water adjuster 15, and the surfactant separating means Numeral 14 is maintained below the Kraft point or above the cloud point of the surfactant used, and the washing water regulator 15 is maintained above the Kraft point or below the cloud point. As a result, the surfactant is separated in the surfactant separating means 14 because the solubility of the surfactant is very low. On the contrary, the surfactant is dissolved in the washing water regulator 15. In the subsequent freeze concentration step 3, the impurities in the waste water are concentrated and separated to obtain pure water, as in the first embodiment.

【0034】かかる第2実施形態の流れを説明するに、
土壌洗浄工程1にて第1実施形態と同様に汚染土壌の洗
浄処理により排出される排水27は、バルブaを開くこ
とにより界面活性剤分離手段14に導かれ、ここで界面
活性剤が浮遊分離するとともに本例の場合有害物質は比
重が水より大きいので該界面活性剤分離手段14下部に
沈降する。分離された界面活性剤33は洗浄水調整器1
5へ導かれ、また、下部に沈降した有害物質を含む排水
は、バルブd、cを開いた状態でポンプ18により、凍
結濃縮工程3の貯留槽13aに送給される。尚、界面活
性剤分離手段14は超音波や超音波を伴う微細気泡を槽
内に付与して、該微細気泡や超音波により界面活性剤と
有害物質の分離を行うことも可能である。また、前記非
イオン性界面活性剤の場合、昇温して分離するときっこ
の超音波による昇温効果で曇点以上にすることも可能で
ある。前記貯留槽13aに貯留された排水は一定量溜ま
ると凍結濃縮手段13bに移される。該凍結濃縮手段1
3bでは、冷凍・ヒートポンプ装置16により形成され
る冷凍サイクル16aにより純水部分が氷結するため、
有害物質は濃縮されて下部に溜り、三方弁19、バルブ
b及びeを開いて該濃縮された有害物質濃縮排水34を
有害物質分解処理工程等の具備された設備へ送給する。
このとき、氷生成の際の凝縮熱は前記洗浄水調整器15
に供給し、該凝縮熱を洗浄水調整器15の温度を使用界
面活性剤のクラフト点以上に保つために利用する。つま
り、該凍結濃縮手段13b側に冷凍サイクル16aを、
前記洗浄水調整器15側にヒートポンプサイクル16
b’を形成するように冷凍・ヒートポンプ装置16を構
成することにより、かかる土壌洗浄装置を効率良く運転
することが可能となる。
To explain the flow of the second embodiment,
The wastewater 27 discharged by the cleaning treatment of the contaminated soil in the soil cleaning step 1 as in the first embodiment is guided to the surfactant separating means 14 by opening the valve a, where the surfactant is separated by floating. At the same time, in the case of this example, the harmful substance has a specific gravity higher than that of water, so that the harmful substance settles below the surfactant separating means 14. The separated surfactant 33 is used as the washing water conditioner 1
The wastewater guided to 5 and containing the harmful substances settled in the lower part is sent to the storage tank 13a in the freeze concentration step 3 by the pump 18 with the valves d and c open. The surfactant separating means 14 can also apply ultrasonic waves or fine bubbles accompanied by ultrasonic waves to the inside of the tank, and separate the surfactant and the harmful substance by the fine bubbles or ultrasonic waves. In the case of the nonionic surfactant, it is also possible to raise the temperature to be higher than the cloud point by the effect of increasing the temperature by ultrasonic waves when separating by heating. When a certain amount of wastewater stored in the storage tank 13a accumulates, the wastewater is transferred to the freeze concentration means 13b. The freeze concentration means 1
In 3b, since the pure water portion freezes due to the refrigeration cycle 16a formed by the refrigeration / heat pump device 16,
The harmful substance is concentrated and accumulates in the lower part, and the three-way valve 19 and the valves b and e are opened to send the concentrated harmful substance concentrated wastewater 34 to equipment provided with a harmful substance decomposition treatment process or the like.
At this time, the heat of condensation at the time of ice formation is reduced by the washing water regulator 15.
And the heat of condensation is used to maintain the temperature of the washing water regulator 15 above the Kraft point of the surfactant used. That is, the refrigeration cycle 16a is provided on the freeze concentration means 13b side.
A heat pump cycle 16 is provided on the washing water regulator 15 side.
By configuring the refrigeration / heat pump device 16 so as to form b ′, it becomes possible to efficiently operate such a soil cleaning device.

【0035】前記凍結濃縮手段13bから有害物質濃縮
排水34を完全に排出した後、該凍結濃縮手段13bに
ヒートポンプサイクル16bを形成させて氷分離融解手
段13cに移行することにより、氷結した氷が融解され
て純水を得ることができる。ここで得た融解水29は、
洗浄水調整器15方向に三方弁19を開いて、該洗浄水
調整器15に送給する。このとき、低温の該融解水29
の冷熱を利用して前記界面活性剤分離手段14の冷却を
行なうようにする。これにより、該界面活性剤分離手段
14でもって効率良く熱交換ができ、ここで温度の上昇
した純水29が導入された洗浄水調整器15を使用界面
活性剤のクラフト点以上に温める際、或いは使用界面活
性剤の曇点以下に冷却する際にも熱エネルギが少なくて
すむ。尚、界面活性剤分離手段14の冷却方法として、
前記したように融解水あるいは凝縮熱を利用する他に、
前記氷分離融解手段13cでの氷融解の際の蒸発熱を用
いて形成した冷凍サイクルを利用してもよい。
After the harmful substance concentrated wastewater 34 is completely discharged from the freeze-concentration means 13b, a heat pump cycle 16b is formed in the freeze-concentration means 13b and transferred to the ice separation and thawing means 13c, whereby the frozen ice is melted. Pure water can be obtained. The molten water 29 obtained here is
The three-way valve 19 is opened in the direction of the washing water regulator 15, and the three-way valve 19 is fed to the washing water regulator 15. At this time, the low-temperature molten water 29
The cooling of the surfactant separating means 14 is performed by utilizing the cold heat. Thereby, heat exchange can be efficiently performed by the surfactant separating means 14, and when the washing water regulator 15 into which the purified water 29 whose temperature has been raised is introduced is heated to a temperature higher than the Kraft point of the used surfactant, Alternatively, less heat energy is required for cooling to below the cloud point of the surfactant used. In addition, as a cooling method of the surfactant separating means 14,
As mentioned above, besides utilizing the melting water or heat of condensation,
A refrigeration cycle formed using heat of evaporation at the time of melting the ice in the ice separating and melting means 13c may be used.

【0036】前記界面活性剤分離手段14で分離した界
面活性剤33を含む排水と、凍結濃縮工程3で生成され
た純水29とが供給された洗浄水調整器15では、これ
らを混合して土壌洗浄に適した洗浄水を調整し、前記土
壌洗浄工程1に供給して洗浄水の再利用化を図る。これ
により、大量に排出される排水を低減できるとともに、
界面活性剤及び水の循環利用が可能となり、コストの削
減につながる。尚、前記界面活性剤分離手段14にて界
面活性剤及び有害物質と分離された水は、前記純水29
とともに洗浄水調整器15で利用することが好ましい。
In the washing water regulator 15 to which the waste water containing the surfactant 33 separated by the surfactant separating means 14 and the pure water 29 generated in the freeze concentration step 3 are supplied, these are mixed. Washing water suitable for soil washing is adjusted and supplied to the soil washing step 1 to reuse the washing water. This will reduce the amount of wastewater discharged in large quantities,
Recycling of surfactant and water becomes possible, leading to cost reduction. The water separated from the surfactant and the harmful substance by the surfactant separating means 14 is the pure water 29.
In addition, it is preferable to use the cleaning water regulator 15.

【0037】[0037]

【発明の効果】以上記載のごとく、本発明によれば、対
生態系有害物質により汚染された土壌の洗浄処理に使用
された大量の排水から確実に有害物質を取り除くことが
可能で、かつ排水量を減少させることができるととも
に、洗浄に用いられる水や界面活性剤を循環利用するこ
とによりコスト的に安価な土壌浄化方法及び装置が提供
できる。また、かかる発明に用いる凍結濃縮工程におい
て、冷凍・ヒートポンプサイクルを有効に活用すること
により、熱効率のよい装置が可能となり、動力の無駄が
省ける。
As described above, according to the present invention, it is possible to reliably remove harmful substances from a large amount of wastewater used for cleaning soil contaminated with ecological harmful substances, It is possible to provide an inexpensive and low-cost soil purification method and apparatus by circulating and using water and a surfactant used for washing. Further, in the freeze-concentration step used in the present invention, by effectively utilizing the refrigeration / heat pump cycle, a device having high thermal efficiency can be provided, and waste of power can be eliminated.

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

【図1】 本発明の第1実施形態にかかる土壌浄化装置
の全体構成図である。
FIG. 1 is an overall configuration diagram of a soil purification device according to a first embodiment of the present invention.

【図2】 本発明の第2実施形態にかかる土壌浄化装置
の全体構成図である。
FIG. 2 is an overall configuration diagram of a soil purification device according to a second embodiment of the present invention.

【図3】 従来の汚染土壌浄化装置の実施形態を示す概
略図である。
FIG. 3 is a schematic diagram showing an embodiment of a conventional contaminated soil purification device.

【符号の説明】[Explanation of symbols]

1 土壌洗浄工程 2 界面活性剤リサイクル工程 3 凍結濃縮工程 10 土壌洗浄機 11、12 固液分離器 13 有害物質分離手段 13a 貯留槽 13b 凍結濃縮手段 13c 氷分離融解手段 15 洗浄水調整器 16 冷凍・ヒートポンプ装置 18 ポンプ 19 三方弁 20 汚染土壌 29 融解水(純水) 34 有害物質濃縮排水 35 戻入手段 DESCRIPTION OF SYMBOLS 1 Soil washing process 2 Surfactant recycling process 3 Freeze-concentration process 10 Soil washer 11, 12 Solid-liquid separator 13 Hazardous substance separation means 13a Storage tank 13b Freeze-concentration means 13c Ice separation / thaw means 15 Washing water regulator 16 Freezing / Heat pump device 18 Pump 19 Three-way valve 20 Contaminated soil 29 Melted water (pure water) 34 Concentrated wastewater of harmful substances 35 Return means

───────────────────────────────────────────────────── 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) B09C 1/04 C02F 1/36 1/08 B09B 3/00 304K C02F 1/22 ZAB 1/24 5/00 S 1/36 (72)発明者 金沢 岳夫 東京都江東区牡丹2丁目13番1号 株式会 社前川製作所内 (72)発明者 山上 伸一 東京都江東区牡丹2丁目13番1号 株式会 社前川製作所内 (72)発明者 岩堀 恵祐 静岡県清水市折戸519−1−201 Fターム(参考) 4D004 AA41 AB02 AB03 AB06 CA13 CA40 CA45 CB44 CB50 CC03 CC05 4D037 AA11 AB06 AB08 AB14 BA01 BA11 BA21 BA26 CA06 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) B09C 1/04 C02F 1/36 1/08 B09B 3/00 304K C02F 1/22 ZAB 1/24 5/00 S 1/36 (72) Inventor Takeo Kanazawa 2-13-1, Botan, Koto-ku, Tokyo Inside the Maekawa Works Co., Ltd. (72) Inventor Shinichi Yamagami 2-3-1 Botan, Koto-ku, Tokyo Co., Ltd. Maekawa Corporation Inside the factory (72) Inventor Keisuke Iwahori 519-1-201 Orito F-term (reference) 4D004 AA41 AB02 AB03 AB06 CA13 CA40 CA45 CB44 CB50 CC03 CC05 4D037 AA11 AB06 AB08 AB14 BA01 BA11 BA26 CA06

Claims (9)

【特許請求の範囲】[Claims] 【請求項1】 界面活性剤水溶液を用いて対生態系有害
物質で汚染された土壌を洗浄する洗浄工程と、浄化土壌
からなる固相と当該有害物質を取込んだ乳化物を含む界
面活性剤水溶液からなる液相とに固液分離する固液分離
工程とを有する汚染土壌浄化方法において、 前記固液分離した液相を冷却、凍結させて氷を生成させ
ることにより当該有害物質を前記液相中に濃縮するとと
もに、当該有害物質が除かれた前記氷を融解し、生成し
た水を前記土壌洗浄に再循環利用することを特徴とする
汚染土壌浄化方法。
1. A washing step for washing soil contaminated with ecological harmful substances using an aqueous solution of a surfactant, a surfactant comprising a solid phase comprising purified soil and an emulsion incorporating the harmful substances. A solid-liquid separation step of solid-liquid separation into a liquid phase composed of an aqueous solution, wherein the solid-liquid separated liquid phase is cooled and frozen to generate ice, thereby converting the harmful substance into the liquid phase. A method for purifying contaminated soil, characterized in that the ice, from which the harmful substances have been removed, is melted, and the generated water is recycled for the soil washing.
【請求項2】 界面活性剤水溶液を用いて対生態系有害
物質で汚染された土壌を洗浄する洗浄工程と、浄化土壌
からなる固相と当該有害物質を取込んだ乳化物を含む界
面活性剤水溶液からなる液相とに固液分離する固液分離
工程とを有する汚染土壌浄化方法において、 前記分離した液相を、含有界面活性剤のクラフト点以下
に冷却、含有界面活性剤の曇点以上に昇温もしくは超音
波を照射することにより、液相の有害物質の可溶化若し
くは乳化を破壊して上層と下層に二層分離し、当該有害
物質を含む下層は冷却、凍結して氷を生成させることに
より当該有害物質を前記下層中に濃縮するとともに、当
該有害物質が除かれた前記氷を融解し、生成した水を前
記土壌洗浄に再循環利用することを特徴とする汚染土壌
浄化方法。
2. A washing step for washing soil contaminated with ecologically harmful substances using an aqueous solution of a surfactant, and a surfactant comprising a solid phase composed of purified soil and an emulsion incorporating the harmful substances. A solid-liquid separation step of solid-liquid separation into a liquid phase comprising an aqueous solution, wherein the separated liquid phase is cooled below the Kraft point of the contained surfactant and above the cloud point of the contained surfactant By heating or irradiating ultrasonic waves to break up the solubilization or emulsification of harmful substances in the liquid phase and separate into two layers, an upper layer and a lower layer.The lower layer containing the harmful substances is cooled and frozen to form ice Contaminating the harmful substance in the lower layer by melting, melting the ice from which the harmful substance has been removed, and recycling the generated water for the soil washing.
【請求項3】 前記二層分離して有害物質が除かれた界
面活性剤を前記土壌洗浄に再循環利用することを特徴と
する請求項1若しくは2記載の汚染土壌浄化方法。
3. The method for purifying contaminated soil according to claim 1, wherein the surfactant separated from the two layers to remove harmful substances is recycled for the soil washing.
【請求項4】 前記固液分離した固相を前記洗浄工程に
戻し、洗浄工程と固液分離工程を複数回繰り返す、多段
洗浄を行うことを特徴とする請求項1乃至3いずれかの
項記載の汚染土壌浄化方法。
4. The multi-stage washing in which the solid-liquid separated solid phase is returned to the washing step, and the washing step and the solid-liquid separation step are repeated a plurality of times. Contaminated soil purification method.
【請求項5】 界面活性剤水溶液を用いて対生態系有害
物質で汚染された土壌を洗浄する土壌洗浄手段を具えた
土壌浄化装置において、 前記土壌洗浄後の、当該有害物質を取り込んだ界面活性
剤を含む排水を冷却して凍結させる凍結濃縮手段と、 凍結により生成した界面活性剤を含まない真氷を分離し
て融解する氷分離融解手段と、を具えるとともに、 前記氷分離融解手段により生成した水を前記土壌洗浄手
段に返送して再利用することを特徴とする汚染土壌浄化
装置。
5. A soil purification apparatus provided with a soil washing means for washing soil contaminated with ecologically harmful substances using an aqueous solution of a surfactant, wherein the surfactant containing the harmful substances after the soil washing is used. A freeze-concentrating means for cooling and freezing the wastewater containing the agent; and an ice separation and melting means for separating and melting the true ice free of surfactant generated by freezing, and the ice separation and melting means. A contaminated soil purification device, wherein the generated water is returned to the soil washing means for reuse.
【請求項6】 界面活性剤水溶液を用いて対生態系有害
物質で汚染された土壌を洗浄する土壌洗浄手段を具えた
土壌浄化装置において、 前記土壌洗浄後の、当該有害物質を取り込んだ界面活性
剤を含む排水を含有界面活性剤のクラフト点以下に冷却
するか、曇点以上に昇温するか、超音波を照射するかし
て、液相の乳化を破壊して上層と下層に二層分離する二
層分離手段と、 分離された当該有害物質を含む下層を冷却して凍結させ
る凍結濃縮装置と、 凍結により生成した当該有害物質が除かれた氷を分離し
て融解する氷分離融解手段と、 分離された界面活性剤及び氷の融解により生成した水と
を利用して土壌洗浄機に供給する洗浄水を調製する洗浄
水調製器と、を具えることを特徴とする汚染土壌浄化装
置。
6. A soil purification apparatus provided with a soil washing means for washing soil contaminated with ecologically harmful substances using an aqueous solution of a surfactant, wherein the surfactant containing the harmful substances after the soil washing is taken. Cool the wastewater containing the agent below the Kraft point of the surfactant contained, raise the temperature above the cloud point, or irradiate ultrasonic waves to destroy the emulsification of the liquid phase and form two layers, an upper layer and a lower layer. A two-layer separating means for separating, a freeze-concentrating apparatus for cooling and freezing the separated lower layer containing the harmful substance, and an ice separating and melting means for separating and melting ice from which the harmful substance generated by freezing is removed. A contaminated soil purification device, comprising: a cleaning water preparation device that prepares cleaning water to be supplied to a soil cleaning device using the separated surfactant and water generated by melting of ice. .
【請求項7】 前記凍結濃縮手段と前記氷分離融解手段
とが、ヒートポンプの放熱/吸熱サイクルにより同一槽
で行われることを特徴とする請求項5若しくは6記載の
汚染土壌浄化装置。
7. The contaminated soil purification apparatus according to claim 5, wherein the freeze concentration means and the ice separation / thawing means are performed in the same tank by a heat radiation / endothermic cycle of a heat pump.
【請求項8】 前記氷分離融解手段にて氷の融解を凝縮
器側で、前記凍結濃縮手段にて排水の凍結を蒸発器側で
行うとともに、前記界面活性剤分離手段での界面活性剤
を含む排水のクラフト点以下への冷却に前記氷の融解水
を利用し、前記凍結濃縮時の凝縮熱を前記洗浄水調製器
の加温熱源と前記界面活性剤分離手段での界面活性剤を
含む排水の曇点以上への昇温とに利用するヒートポンプ
で連結したことを特徴とする請求項5乃至7いずれかの
項記載の汚染土壌浄化装置。
8. The method of melting ice on the condenser side by the ice separating and thawing means, freezing the waste water on the evaporator side by the freeze concentrating means, and removing the surfactant by the surfactant separating means. The melting water of the ice is used for cooling the wastewater containing water to a temperature lower than the Kraft point, and the heat of condensation at the time of freeze concentration includes the heating heat source of the washing water preparation device and the surfactant in the surfactant separating means. The contaminated soil purification apparatus according to any one of claims 5 to 7, wherein the apparatus is connected by a heat pump used to raise the temperature of the wastewater to a temperature higher than the cloud point.
【請求項9】 前記固液分離した固相を前記洗浄工程に
戻し、洗浄工程と固液分離工程を複数回繰り返す、多段
洗浄を行うための戻入手段を備えたことを特徴とする請
求項5乃至8いずれかの項記載の汚染土壌浄化装置。
9. A return means for performing multi-stage washing, wherein the solid-liquid separated solid phase is returned to the washing step, and the washing step and the solid-liquid separation step are repeated a plurality of times. 9. A contaminated soil purification apparatus according to any one of claims 8 to 8.
JP2001183955A 2000-08-24 2001-06-18 Contaminated soil purification method and apparatus Expired - Fee Related JP4636738B2 (en)

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JP2000-253328 2000-08-24
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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009220015A (en) * 2008-03-17 2009-10-01 Railway Technical Res Inst Method for treating washing wastewater containing chlorine-containing organic compound
JP2011011134A (en) * 2009-06-30 2011-01-20 Kanagawa Univ Method and agent for decontamination
KR200464231Y1 (en) * 2012-09-28 2012-12-18 (주)동명엔터프라이즈 Apparatus for ultrasonic washing of soil
JP2015087130A (en) * 2013-10-28 2015-05-07 株式会社本間組 Radioactive substance removal method and removal device
CN108817058A (en) * 2018-07-05 2018-11-16 上海艾库环境工程有限公司 A kind of soil remediation method

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5697503A (en) * 1980-01-07 1981-08-06 Nippon Oil & Fats Co Ltd Separation of constituent component from mixed composition of plural component of org. compound
JPH0975907A (en) * 1995-09-07 1997-03-25 Kajima Corp Method of purifying contaminated soil
JPH09327689A (en) * 1996-06-10 1997-12-22 Hitachi Ltd Waste water recycling system
JPH10216693A (en) * 1997-02-10 1998-08-18 Shimizu Corp Separation of contaminant from contaminated soil and device therefor
JPH11319892A (en) * 1998-03-16 1999-11-24 Mayekawa Mfg Co Ltd Waste water treatment and waste water treating device
JP2001334258A (en) * 2000-05-29 2001-12-04 Nippon Paint Plant Engineering Co Ltd Method and system for recycling cleaning water

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5697503A (en) * 1980-01-07 1981-08-06 Nippon Oil & Fats Co Ltd Separation of constituent component from mixed composition of plural component of org. compound
JPH0975907A (en) * 1995-09-07 1997-03-25 Kajima Corp Method of purifying contaminated soil
JPH09327689A (en) * 1996-06-10 1997-12-22 Hitachi Ltd Waste water recycling system
JPH10216693A (en) * 1997-02-10 1998-08-18 Shimizu Corp Separation of contaminant from contaminated soil and device therefor
JPH11319892A (en) * 1998-03-16 1999-11-24 Mayekawa Mfg Co Ltd Waste water treatment and waste water treating device
JP2001334258A (en) * 2000-05-29 2001-12-04 Nippon Paint Plant Engineering Co Ltd Method and system for recycling cleaning water

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009220015A (en) * 2008-03-17 2009-10-01 Railway Technical Res Inst Method for treating washing wastewater containing chlorine-containing organic compound
JP2011011134A (en) * 2009-06-30 2011-01-20 Kanagawa Univ Method and agent for decontamination
KR200464231Y1 (en) * 2012-09-28 2012-12-18 (주)동명엔터프라이즈 Apparatus for ultrasonic washing of soil
JP2015087130A (en) * 2013-10-28 2015-05-07 株式会社本間組 Radioactive substance removal method and removal device
CN108817058A (en) * 2018-07-05 2018-11-16 上海艾库环境工程有限公司 A kind of soil remediation method

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