JP2002282837A - Purification method of oil contaminated soil - Google Patents

Purification method of oil contaminated soil

Info

Publication number
JP2002282837A
JP2002282837A JP2001096595A JP2001096595A JP2002282837A JP 2002282837 A JP2002282837 A JP 2002282837A JP 2001096595 A JP2001096595 A JP 2001096595A JP 2001096595 A JP2001096595 A JP 2001096595A JP 2002282837 A JP2002282837 A JP 2002282837A
Authority
JP
Japan
Prior art keywords
soil
oil
container
water
contaminated soil
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.)
Withdrawn
Application number
JP2001096595A
Other languages
Japanese (ja)
Inventor
Akiko Hirai
明子 平井
Ryozo Ushio
亮三 牛尾
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.)
Sumikon Serutekku KK
Original Assignee
Sumikon Serutekku KK
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 Sumikon Serutekku KK filed Critical Sumikon Serutekku KK
Priority to JP2001096595A priority Critical patent/JP2002282837A/en
Publication of JP2002282837A publication Critical patent/JP2002282837A/en
Withdrawn legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/52Mechanical processing of waste for the recovery of materials, e.g. crushing, shredding, separation or disassembly

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Extraction Or Liquid Replacement (AREA)
  • Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
  • Mixers With Rotating Receptacles And Mixers With Vibration Mechanisms (AREA)

Abstract

PROBLEM TO BE SOLVED: To propose a purification method of oil contaminated soil that not only can continuously remove the contaminant from the oil contaminated soil but also restrain the amount of soil which should be discharged requiring a high cost incineration to minimum. SOLUTION: In a rotary cylindrical vessel with no opening part in the peripheral surface and equipped with an agitation vane and a carrier vane therein, contaminated soil as a processing object and water are mixed and agitated. Then the admixture of the processing object and water is separated into three parts, a floating oil content, a solid phase, and a suspension liquid phase, respectively, and the separated floating oil content and the solid phase are recovered separately.

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、石油系化合物で汚
染された土壌を浄化する技術に関する。
TECHNICAL FIELD The present invention relates to a technique for purifying soil contaminated with petroleum compounds.

【0002】[0002]

【従来の技術】多数存在している石油類を扱う事業所や
工場の中には、漏洩や廃棄などによって土壌が油に汚染
されている場所が少なくない。現在、国による法規制の
整備が進められているとともに、地方自治体レベルでも
独自の規制や浄化指導を行う場合が増加してきている。
このような状況の中で、油で汚染された土壌の修復方法
の確立が必要とされている。従来、油による汚染された
土壌を浄化するためには、水酸化ナトリウムや過酸化水
素水、有機溶剤、界面活性剤等の化学洗浄剤を用いた洗
浄処理を行うことが提案されている。
2. Description of the Related Art There are a number of places and factories that handle a large number of petroleum products where the soil is contaminated with oil due to leakage or disposal. At present, laws and regulations are being prepared by the government, and the number of cases where local governments provide their own regulations and cleanup guidance is increasing.
Under such circumstances, there is a need to establish a method for remediating soil contaminated with oil. BACKGROUND ART Conventionally, in order to purify soil contaminated with oil, it has been proposed to perform a cleaning treatment using a chemical cleaning agent such as sodium hydroxide, hydrogen peroxide, an organic solvent, and a surfactant.

【0003】[0003]

【発明が解決しようとする課題】しかし、これらの方法
には以下のような問題がある。水酸化ナトリウムなどの
強アルカリを用いた洗浄では処理後、廃液・土壌共に中
和処理する必要がある。過酸化水素を用いて油を浮上さ
せる手法は水酸化ナトリウムなどのアルカリによる前処
理を必要とするため前記と同様に洗浄後に中和処理が必
要になり、かつ高価な薬剤を使用するためコストが高
い。有機溶剤や界面活性剤などの化学洗浄剤を用いた処
理では、分離した油が乳化してしまうため水溶液との分
離が困難であり、新たな処理を必要となりコストがかか
る。
However, these methods have the following problems. In the case of washing using a strong alkali such as sodium hydroxide, it is necessary to neutralize both the waste liquid and the soil after the treatment. The method of floating oil using hydrogen peroxide requires a pretreatment with an alkali such as sodium hydroxide, so that a neutralization treatment is required after washing as described above, and the cost is increased because expensive chemicals are used. high. In a treatment using a chemical cleaning agent such as an organic solvent or a surfactant, the separated oil is emulsified, so that it is difficult to separate the separated oil from an aqueous solution.

【0004】一方、特開2000−202422、20
00−202423には、石油系化合物による汚染土壌
と洗浄液(ケイ酸ナトリウム、有機溶剤)を周面部に開
口部を持つ回転式ふるいの中で撹拌と汚染部の分離を行
う洗浄方法か提案されている。しかしこの方法では回転
式ふるいの目詰まりが早く起こるため、連続的な処理が
困難である。また、周面の開口部から洗浄水が直ちに流
出してしまうため、汚染土壌と水の水分比率が安定せ
ず、制御が難しい。更に処理時に必ず発生する洗浄水中
の土壌細粒部の処理について詳しく触れられていない。
土壌細粒部には汚染が濃縮している場合が多く、その場
合焼却処分せざるを得ないため、発生する土壌細粒部の
量は処理コストに大きな影響を持っている。
On the other hand, JP-A-2000-202422, 20
00-202423 proposes a washing method in which a soil contaminated with petroleum compounds and a washing liquid (sodium silicate, organic solvent) are stirred in a rotary sieve having an opening on the peripheral surface and the contaminated part is separated. I have. However, in this method, clogging of the rotary sieve occurs quickly, so that continuous processing is difficult. In addition, since the washing water immediately flows out from the opening in the peripheral surface, the water ratio of the contaminated soil and water is not stable, and it is difficult to control. Furthermore, there is no detailed description of the treatment of the soil fine-grain portion in the wash water which always occurs during the treatment.
Contamination is often concentrated in the soil fines, and in that case, it is inevitable to incinerate. Therefore, the amount of soil fines generated has a great effect on the treatment cost.

【0005】本発明は、上記した従来技術の問題を解決
するためになされたもので、油に汚染された土壌から連
続的に汚染物質を除去することができ、かつ高コストな
焼却分として排出される土壌量を最小限に抑えることが
できる油汚染土壌の浄化方法を提案することを目的とす
るものである。
The present invention has been made to solve the above-mentioned problems of the prior art, and it is possible to continuously remove contaminants from soil contaminated with oil, and to discharge as high-cost incineration. It is an object of the present invention to propose a method of purifying oil-contaminated soil that can minimize the amount of soil to be removed.

【0006】[0006]

【課題を解決するための手段】本発明は、油汚染土壌を
周面に開口部を持たない円筒状の容器で撹拌した後、浮
上油分、固相、懸濁水相に分離しそれぞれに対し処理を
行うことにより、最終的に廃棄する土壌細粒部の量を低
減させつつ、油汚染土壌を浄化する方法であり、第1発
明は周面部に開孔部を持たず、かつ容器内側に容器内径
の1/15以上の高さを有する、回転軸に平行な複数の
撹拌羽根を持ち、かつ容器内側に土壌を容器の円筒軸方
向に向かって搬送する羽根を複数持つ回転円筒容器中
で、処理対象汚染土壌と水を土壌の固体濃度にて50%
〜80%の範囲で混合・撹拌する工程と、処理汚染対象
物と水の混合物を浮上油分と固相と懸濁液相との3部に
分離する工程と、分離した浮上油分と固相とを別々に回
収する工程とを有する油汚染土壌の浄化方法であり、第
2発明は水平面に対し周面部が5〜30゜の範囲で傾斜
をつけて設置され、かつ周面部に開孔部を持たず、かつ
容器内側に容器内径の1/15以上の高さを有する、回
転軸に平行な複数の撹拌羽根を持つ回転円筒容器中で、
処理対象汚染土壌と水を土壌の固体濃度にて50%〜8
0%の範囲で混合・撹拌する工程と、処理汚染対象物と
水の混合物を浮上油分と固相と懸濁液相との3部に分離
する工程と、分離した浮上油分と固相とを別々に回収す
る工程とを有する油汚染土壌の浄化方法であり、第3発
明は水平面に対し周面部が5〜30゜の範囲で傾斜をつ
けて設置され、かつ周面部に開孔部を持たず、かつ容器
内側に容器内径の1/15以上の高さを有する、回転軸
に平行な複数の攪拌羽根を持ち、かつ容器内側に土壌を
容器の円筒軸方向に向かって搬送する羽根を複数持つ回
転円筒容器中で、処理対象汚染土壌と水を土壌の固体濃
度にて50%〜80%の範囲で混合・撹拌する工程と、
処理汚染対象物と水の混合物を浮上油分と固相と懸濁液
相との3部に分離する工程と、分離した浮上油分と固相
とを各々に回収する工程を有する油汚染土壌の浄化方法
であり、第4発明は前記回転円筒容器中内にある土壌を
容器の円筒軸方向に向かって搬送する羽根の向きを、周
面底部の傾斜方向とは逆の向きに付けることを特徴と
し、第5発明は前記回転円筒状容器内にある土壌を容器
の円筒軸方向に向かって搬送する羽根の長さを中心角と
して60〜270゜であり、かつ隣り合った羽根の個々
の間隔を中心角として30〜60゜開けることを特徴と
し、第6発明は浮上油と固相と懸濁液相との3部に分離
する前に汚染土壌と水の混合物を振動篩、可動棒篩、サ
イクロン分級機、水力分級機の何れかを用いて一定粒径
以上の土壌と粒径以下のスラリーに分離することを特徴
とし、第7発明は分離後の固相は、回転円筒状容器に返
送することを特徴とし、第8発明は懸濁液相中の懸濁成
分に付着している油分を、pH調整もしくは超音波処理
を行うことにより分離・浮上させること特徴とし、第9
発明は浮上油分と固相から分離した液相は、循環させて
回転円筒状容器内で処理対象汚染土壌と混合する水とし
て再利用することを特徴とし、第10発明は水は循環時
に30〜50℃の温度範囲に加温することを特徴とする
ものである。
According to the present invention, oil-contaminated soil is stirred in a cylindrical container having no opening on the peripheral surface, and then separated into a floating oil component, a solid phase, and a suspended aqueous phase, and each of them is treated. Is a method for purifying oil-contaminated soil while reducing the amount of soil fines to be finally discarded. The first invention does not have an opening on the peripheral surface and a container is provided inside the container. In a rotating cylindrical container having a plurality of stirring blades having a height equal to or more than 1/15 of the inner diameter and having a plurality of stirring blades parallel to the rotation axis, and having a plurality of blades for transporting soil toward the cylindrical axis direction of the container inside the container, 50% of contaminated soil and water to be treated as solid concentration of soil
Mixing and stirring in the range of ~ 80%, separating the mixture of water to be treated and water into three parts, a floating oil component, a solid phase and a suspension phase, And a method of purifying oil-contaminated soil having a step of separately recovering oil. In a rotating cylindrical container having a plurality of stirring blades parallel to the rotation axis, having no, and having a height of 1/15 or more of the inner diameter of the container inside the container,
The contaminated soil and water to be treated are 50% -8
A step of mixing and stirring in a range of 0%, a step of separating a mixture of the object to be treated and water into three parts of a floating oil component, a solid phase and a suspension phase, and a step of separating the separated floating oil component and the solid phase. A method of purifying oil-contaminated soil having a step of separately recovering the oil-contaminated soil. A plurality of agitating blades having a height equal to or more than 1/15 of the inner diameter of the container inside the container and parallel to the rotation axis, and a plurality of blades for transporting the soil toward the cylindrical axis of the container inside the container. Mixing and stirring the contaminated soil to be treated and water in the range of 50% to 80% in the solid concentration of the soil in a rotating cylindrical container having;
Purification of oil-contaminated soil, comprising the steps of separating a mixture of water to be treated and water into three parts, a floating oil component, a solid phase, and a suspension phase, and recovering the separated floating oil component and the solid phase, respectively. A method according to a fourth aspect of the present invention, characterized in that the direction of the blade for transporting the soil in the rotary cylindrical container toward the cylindrical axis direction of the container is opposite to the inclination direction of the bottom of the peripheral surface. According to a fifth aspect of the present invention, the length of the blade for transporting the soil in the rotary cylindrical container in the cylindrical axis direction of the container is 60 to 270 ° as a central angle, and the distance between the adjacent blades is According to a sixth aspect of the present invention, a mixture of contaminated soil and water is shaken, a movable rod sieve, or the like, before being separated into three parts of a floating oil, a solid phase, and a suspension phase. Use either a cyclone classifier or a hydraulic classifier to set the soil size The seventh invention is characterized in that the solid phase after separation is returned to a rotating cylindrical container, and the eighth invention is characterized in that the solid phase adheres to the suspended components in the suspension phase. The oil component is separated and floated by performing pH adjustment or ultrasonic treatment.
The invention is characterized in that the floating oil and the liquid phase separated from the solid phase are circulated and reused as water to be mixed with the contaminated soil to be treated in the rotating cylindrical container. It is characterized by heating to a temperature range of 50 ° C.

【0007】[0007]

【発明の実施の形態】図1は本発明の油汚染土壌の浄化
方法の一実施例を示す工程図、図2は同上の浄化方法の
混合・攪拌工程における回転円筒状容器を例示したもの
で、(a)は一部省略概略縦断側面図、(b)は概略縦
断正面図であり、1は混合・攪拌工程、2は分離工程、
3は油分回収工程、4は固相回収工程、5は土壌分離工
程、6は油分分離工程、7は加温工程、8はオイルセパ
レーター、11は回転円筒状容器である。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 is a process diagram showing an embodiment of the method for purifying oil-contaminated soil according to the present invention, and FIG. 2 is an illustration of a rotary cylindrical container in a mixing / stirring step of the above-mentioned purification method. (A) is a schematic longitudinal sectional side view partially omitted, and (b) is a schematic longitudinal sectional front view, wherein 1 is a mixing / stirring step, 2 is a separation step,
3 is an oil recovery step, 4 is a solid phase recovery step, 5 is a soil separation step, 6 is an oil separation step, 7 is a heating step, 8 is an oil separator, and 11 is a rotary cylindrical container.

【0008】図1に示す混合・攪拌工程1は、処理対象
汚染土壌と水を回転円筒状容器にて混合・攪拌する工程
であり、ここで用いられる回転円筒状容器としては、図
2にその概略を示すごとく、周面部に開孔部のない密閉
構造の円筒状の容器11内に当該容器内径の1/15以
上の高さを有する回転軸11−1に平行な複数の攪拌羽
根11−2と、容器11内側に土壌を容器の円筒軸方向
に向って搬送する羽根11−3を備えた回転円筒状容器
11aを用いる。この円筒状容器11aには、図面には
示していないが、処理対象土壌と水を投入する投入口
と、汚染土壌と水の混合物の排出口が設けられているこ
とはいうまでもない。なお、前記搬送羽根11−3は円
筒状容器11の周面底部の傾斜方向とは逆の向きに付け
てもよい。その理由は、円筒状容器11a内における処
理対象土壌の滞留時間を長くすることで、処理対象土壌
と水の混合、撹拌を十分に行なうためである。また、こ
の羽根11−3の長さとしては中心角として60〜27
0゜、隣り合った羽根の個々の間隔を中心角として30
〜60゜開けることが好ましい。その理由は、搬送用羽
根11−3と、搬送用羽根11−3間に配置した撹拌用
羽根11−2との両方を効率よく働かせるためである。
The mixing / stirring step 1 shown in FIG. 1 is a step of mixing and stirring the contaminated soil to be treated and water in a rotary cylindrical container. The rotary cylindrical container used here is shown in FIG. As schematically shown, a plurality of agitating blades 11-parallel to a rotating shaft 11-1 having a height equal to or more than 1/15 of the inner diameter of the container are provided in a cylindrical container 11 having a closed structure having no opening on the peripheral surface. 2, and a rotating cylindrical container 11a provided with a blade 11-3 for transporting soil in the cylindrical axis direction of the container inside the container 11. Although not shown in the drawing, it is needless to say that the cylindrical container 11a is provided with an inlet for charging the soil to be treated and water, and an outlet for a mixture of contaminated soil and water. In addition, the said conveyance blade 11-3 may be attached in the direction opposite to the inclination direction of the peripheral surface bottom part of the cylindrical container 11. The reason is that the residence time of the soil to be treated in the cylindrical container 11a is lengthened to sufficiently mix and stir the water with the soil to be treated. The length of the blade 11-3 is 60 to 27 as the central angle.
0 °, 30 as the center angle of each interval between adjacent blades
It is preferable to open up to 60 °. The reason is that both the transport blade 11-3 and the stirring blade 11-2 disposed between the transport blade 11-3 work efficiently.

【0009】分離工程2は、前記混合・攪拌工程1で混
合された汚染土壌と水の混合物を浮上油分と固相と懸濁
液相との3部に分離する工程である。油分回収工程3
は、前記分離工程2で分離した浮上油分を回収する工程
であり、固相回収工程4は同じく分離工程2で分離した
固相を回収する工程である。土壌分離工程5は、前記分
離工程2で浮上油分と固相と懸濁液相との3部に分離す
る前段で汚染土壌と水の混合物中の土壌の粗粒部を分離
する工程である。油分分離工程6は、分離工程2で分離
した懸濁液に付着している油分を回収する工程である。
The separation step 2 is a step of separating the mixture of the contaminated soil and water mixed in the mixing / stirring step 1 into three parts: a floating oil component, a solid phase, and a suspension phase. Oil recovery process 3
Is a step of recovering the floating oil separated in the separation step 2, and a solid phase recovery step 4 is a step of collecting the solid phase separated in the separation step 2. The soil separation step 5 is a step of separating coarse particles of soil in a mixture of contaminated soil and water at a stage before separation into three parts of a floating oil component, a solid phase, and a suspension phase in the separation step 2. The oil separation step 6 is a step of collecting the oil adhering to the suspension separated in the separation step 2.

【0010】上記の処理工程において、油によって汚染
された土壌を修復する場合は、まず処理対象汚染土壌と
水を混合・攪拌工程1の開口部のない円筒状容器11に
入れて、容器ごと回転させる。この土壌を回転する工程
では、土壌全体が回り擦られることでアトリション効果
が高まり洗浄効果は飛躍的に向上する。この手法だと、
アトリションに際し機械的圧縮などのような高動力エネ
ルギーを要する工程を経ずに効果的にア卜リションが行
える。
When the soil contaminated by oil is to be repaired in the above-mentioned treatment step, first, the contaminated soil to be treated and water are put into a cylindrical container 11 having no opening in the mixing / stirring step 1, and the container is rotated. Let it. In the step of rotating the soil, the attrition effect is enhanced by rubbing the entire soil, and the cleaning effect is dramatically improved. With this technique,
Attrition can be effectively performed without a step requiring high power energy such as mechanical compression.

【0011】投入する水の量は、土壌の固体濃度は50
%〜80%、好ましくは60%〜75%になるように調
節することが望ましい。その理由は固体濃度50%未満
ではアトリション効率が低下し浄化効果も下がるだけで
なく、使用する洗浄水の量も増加し、他方、固体濃度が
80%を超えると混合・攪拌工程後に一定粒径以上の土
壌と粒径以下のスラリーに分離するとき、分離が不十分
になり浄化効果が下がるためである。
[0011] The amount of water to be supplied is as follows.
% To 80%, preferably 60% to 75%. The reason for this is that if the solid concentration is less than 50%, not only the attrition efficiency is reduced and the purification effect is reduced, but also the amount of washing water used is increased. This is because, when the slurry is separated into the soil having a diameter of not less than the diameter and the slurry having the diameter of not more than the diameter, the separation becomes insufficient and the purification effect is lowered.

【0012】また、円筒状容器11が水平に設置されて
いる場合は、周面部に土壌搬送用の羽根11−3を付け
ることにより土壌が円筒状容器11内を一定速度で進み
連続処理が可能となる。更に回転軸11−1に平行な撹
拌羽根11−2を付けることにより土壌が回転時に高所
まで持ち上がり落下することでアトリション効果が更に
向上する。この時この撹拌羽根11−2の高さは円筒状
容器11の直径の1/15以上が好ましい。その理由は
1/15未満では土壌が撹拌羽根11−2によって高所
まで持ち上がらず、アトリションの効果を下げるためで
ある。また、円筒状容器11は傾斜を付けて設置するこ
とも可能である。この場合傾斜によって土壌が搬送され
るため搬送用の羽根11−3はなくてもよい。
When the cylindrical container 11 is installed horizontally, the soil can be advanced at a constant speed in the cylindrical container 11 by attaching blades 11-3 for conveying the soil to the peripheral surface to enable continuous treatment. Becomes Further, by attaching the stirring blade 11-2 parallel to the rotating shaft 11-1, the attraction effect is further improved by lifting the soil to a high place and falling when rotating. At this time, the height of the stirring blade 11-2 is preferably at least 1/15 of the diameter of the cylindrical container 11. The reason is that if it is less than 1/15, the soil is not lifted to a high place by the stirring blade 11-2, and the effect of the attrition is reduced. Further, the cylindrical container 11 can be installed with an inclination. In this case, since the soil is transported by the inclination, the transport blade 11-3 may not be provided.

【0013】上記の円筒状容器11によれば、容器周面
部が開口部を持たないため回転処理中は常に最適な固液
比を一定に保つことができ、アトリション効果も高い状
態を保つことができる。混合物は、直接分離工程2へ導
入するか、または土壌分離工程5を経て分離工程2へ導
入する。この場合、混合・攪拌工程1での攪拌時に発生
した土壌の細粒部は汚染が濃縮されているので、土壌分
離工程5でこの粒子ごとスラリーとして分離すると、高
い油除去効率を得ることができる。またこの時、土壌分
離工程5では振動篩、可動棒篩、サイクロン分級機、水
力分級機のいずれかを用いて粗流部を分離することが望
ましい。なお初期汚染濃度が高濃度の場合は、撹拌−分
離の工程を多段にしてもよい。
According to the cylindrical container 11, since the container peripheral surface has no opening, the optimum solid-liquid ratio can always be kept constant during the rotation process, and the attrition effect can be kept high. Can be. The mixture is introduced directly into the separation step 2 or through the soil separation step 5 into the separation step 2. In this case, since the fine particles of the soil generated during the stirring in the mixing / stirring step 1 are highly contaminated, if the particles are separated as a slurry in the soil separation step 5, high oil removal efficiency can be obtained. . At this time, in the soil separation step 5, it is desirable to separate the coarse flow portion using any of a vibration sieve, a movable bar sieve, a cyclone classifier, and a hydraulic classifier. When the initial contamination concentration is high, the stirring-separation step may be performed in multiple stages.

【0014】分離工程2では、前記混合物またはスラリ
ーを浮上油分と固相と懸濁液相に分離する。このうち浮
上油分は油分回収工程3にて回収し、固相は固相回収工
程4にて回収する。浮上油分の回収では、油除去方法と
してシートなどの油吸着剤やべルト式油水分離機やフロ
ート液面吸引式油水分離機を用いることが可能である。
固相回収工程4にて回収した固相の浄化がさらに必要な
場合は、円筒状容器11に返送するのが望ましい。分離
した懸濁液相中には懸濁成分が分散している。この懸濁
成分が処理土壌全体に占める割合としては大体において
数%程度ではあるが、油分が吸着しているため汚染濃度
は高い。そこで、懸濁成分の汚染濃度を低減させるた
め、油分分離工程6でpH処理あるいは超音波処理など
を用いて懸濁成分と油分を分離させ、回収することが望
ましい。また、固液分離後の水相(液相)はオイルセパ
レーター8などに通過させることで処理水中の油濃度を
低下させ処理対象汚染土壌と混合する水(洗浄水)とし
て再利用するのが望ましい。その際、この水は循環時に
30〜50℃の水温に加温することが望ましい。これは
水温を上げることにより油の粘性が低下するため洗浄効
果が上がるためである。しかし水温が上がりすぎると油
分中の揮発成分が気相へ拡散し、周辺地区へ臭気が広が
るおそれがある上、加温のため大掛かりな設備が必要と
なりコストが掛かるので50℃以下であることが望まし
い。なお30℃未満では洗浄効果が上がらない。加温工
程7はその水を30〜50℃の温度に加温する工程であ
る。
In the separation step 2, the mixture or slurry is separated into a floating oil component, a solid phase and a suspension phase. Of these, the floating oil is collected in an oil recovery step 3, and the solid phase is recovered in a solid phase recovery step 4. In recovering the floating oil, an oil adsorbent such as a sheet, a belt type oil / water separator, or a float liquid level suction type oil / water separator can be used as an oil removing method.
If it is necessary to further purify the solid phase recovered in the solid phase recovery step 4, it is desirable to return the solid phase to the cylindrical container 11. Suspended components are dispersed in the separated suspension phase. Although the proportion of this suspended component in the whole treated soil is about several percent in general, the concentration of contamination is high because oil is adsorbed. Therefore, in order to reduce the contamination concentration of the suspended component, it is desirable to separate and collect the suspended component and the oil component by using a pH treatment or an ultrasonic treatment in the oil component separation step 6. Further, it is desirable that the water phase (liquid phase) after solid-liquid separation is passed through an oil separator 8 or the like to reduce the oil concentration in the treated water and reused as water mixed with the contaminated soil to be treated (wash water). . At this time, it is desirable that this water be heated to a water temperature of 30 to 50 ° C. during circulation. This is because increasing the water temperature lowers the viscosity of the oil, thereby increasing the cleaning effect. However, if the water temperature is too high, the volatile components in the oil will diffuse into the gas phase, and the odor may spread to the surrounding area. In addition, large equipment is required for heating and the cost is high. desirable. If the temperature is lower than 30 ° C., the cleaning effect is not improved. The heating step 7 is a step of heating the water to a temperature of 30 to 50C.

【0015】[0015]

【実施例】実施例1 油汚染土壌(汚染濃度:5wt%)5000gを直径3
00mm、長さ400mmの円筒状容器に入れ、水2L
を円筒状容器内に差し込んだパイプで汚染土壌に振りか
けながら、円筒状容器を12rpmの速度で回転させ
た。この時投入後約10分で円筒状容器を出てきた土壌
と洗浄水を振動ふるいによって粒径0.7mm以上の土
壌とそれ未満の土壌に分離した。ふるい下に分離したス
ラリーの中で、受槽で分離した浮遊油分は油吸着マット
によって回収し、沈澱土壌は受槽底部から引き抜き円筒
状容器に返送した。中間部水相は超音波ホモジナイザー
を用いた油分離処理・固液分離処理後、洗浄水として再
利用した。処理後の粒径0.7mm以下および以上の両
方を合わせた土壌総体としての土壌中の油分を分析した
ところ、0.2wt%にまで減少しており油分除去率は
96%であり、従来の一般的な焼却法と比較して処理コ
ストは約1/3にまで低減した。また、振動ふるいに大
きな閉塞は見られず、最後までふるい分け効率に変化は
なかった。
EXAMPLES Example 1 5000 g of oil-contaminated soil (contamination concentration: 5 wt%) was used with a diameter of 3
Put into a cylindrical container of 00 mm and length of 400 mm and add 2 L of water.
Was sprinkled on contaminated soil with a pipe inserted into the cylindrical container, and the cylindrical container was rotated at a speed of 12 rpm. At this time, the soil and the washing water which came out of the cylindrical container about 10 minutes after the introduction were separated into soil having a particle diameter of 0.7 mm or more and soil having a particle diameter of less than 0.7 mm by a vibrating sieve. Of the slurry separated under the sieve, the suspended oil separated in the receiving tank was recovered by an oil absorption mat, and the precipitated soil was pulled out from the bottom of the receiving tank and returned to the cylindrical container. The intermediate aqueous phase was reused as washing water after oil separation treatment and solid-liquid separation treatment using an ultrasonic homogenizer. When the oil content in the soil as a whole of the soil in which the particle diameter after treatment was 0.7 mm or less and both of them were analyzed, the oil content was reduced to 0.2 wt%, and the oil removal rate was 96%. The processing cost was reduced to about 1/3 compared with the general incineration method. No large blockage was observed in the vibrating sieve, and there was no change in the sieving efficiency to the end.

【0016】実施例2 油汚染土壌(汚染濃度:5wt%)5000gを直径3
00mm、長さ400mmの円筒状容器に入れ、40℃
に加温した2Lの水を円筒状容器内に差し込んだパイプ
より汚染土壌に振りかけながら、円筒状容器を12rp
mの速度で回転させた。投入後約10分で円筒状容器を
出てきた土壌と洗浄水を振動ふるいによって粒径0.7
mm以上の土壌とそれ以下の土壌に分離した。ふるい下
に分離したスラリーの中で、受槽で分離した浮遊油分は
油吸着マットによって回収し、沈澱土壌は受槽底部から
引き抜き円筒状容器に返送した。中間部水相は超音波ホ
モジナイザーを用いた油分離処理を行った、油水分離・
固液分離処理を行ない、洗浄水として再利用した。処理
後の粒径0.7mm以下および以上の両方を合わせた土
壌総体としての土壌中の油分を分析したところ、0.1
wt%にまで減少しており油分除去率は98%であっ
た。
Example 2 5000 g of oil-contaminated soil (contamination concentration: 5 wt%) was treated with a diameter of 3
00mm, put in a cylindrical container of 400mm length, 40 ℃
While heating 2 L of water heated to the contaminated soil through a pipe inserted into the cylindrical container, the cylindrical container was
at a speed of m. Approximately 10 minutes after charging, the soil and washing water that came out of the cylindrical container were washed with a vibrating sieve to a particle size of 0.7.
The soil was separated into soil of mm or more and soil of less than mm. In the slurry separated under the sieve, the suspended oil separated in the receiving tank was recovered by an oil absorption mat, and the precipitated soil was pulled out from the bottom of the receiving tank and returned to the cylindrical container. The middle aqueous phase was subjected to oil separation using an ultrasonic homogenizer.
A solid-liquid separation treatment was performed and reused as washing water. Analysis of the oil content in the soil as a whole of the combined soil having a particle size of 0.7 mm or less after treatment and 0.1 mm or less showed 0.1%.
wt%, and the oil removal rate was 98%.

【0017】実施例3 片端直径300mm、もう片端の直径400mm長さ5
00mmのラッパ形容器で、水は円筒状容器内の片端5
0mmの場所に差し込んだパイプより流速0.3L/m
inで容器のもう片端より連続的投入される油汚染土壌
(汚染濃度:5wt%)に振りかけながら、円錐状容器
を12rpmの速度で回転させた。この時回転状容器内
土壌の固体濃度は常に65〜75%であった。投入後約
10分で円筒状容器を出てきた土壌と懸濁水はそれぞれ
に回収した。分離した懸濁水の中で、浮遊油分は油吸着
マットによって回収し、沈澱土壌は受槽底部から引き抜
き円錐状容器に返送した。中間部水相は超音波ホモジナ
イザーを用いた油分離処理・固液分離処理後、洗浄水と
して再利用した。処理後の粒径0.7mm以下および以
上の両方を合わせた土壌総体としての土壌中の油分を分
析したところ、0.2wt%にまで減少しており油分除
去率は96%であった。また、振動ふるいに大きな閉塞
は見られず、最後まで処理効率に変化はなかった。
Example 3 One end has a diameter of 300 mm and the other end has a diameter of 400 mm and a length of 5 mm.
In a 00mm trumpet-shaped container, water is placed at one end 5 in a cylindrical container.
Flow rate 0.3L / m from pipe inserted at 0mm
The cone-shaped container was rotated at a speed of 12 rpm while sprinkling oil-contaminated soil (contamination concentration: 5 wt%) continuously charged from the other end of the container in. At this time, the solid concentration of the soil in the rotary container was always 65 to 75%. Approximately 10 minutes after the introduction, the soil and the suspended water that came out of the cylindrical container were separately collected. In the separated suspension water, the suspended oil was recovered by an oil absorption mat, and the precipitated soil was withdrawn from the bottom of the receiving tank and returned to the conical vessel. The intermediate aqueous phase was reused as washing water after oil separation treatment and solid-liquid separation treatment using an ultrasonic homogenizer. Analysis of the oil content in the soil as a whole of the soil having a particle diameter of 0.7 mm or less after the treatment and a combination of the above both showed that the oil content was reduced to 0.2 wt%, and the oil removal rate was 96%. In addition, no large blockage was observed in the vibrating sieve, and there was no change in treatment efficiency until the end.

【0018】[0018]

【発明の効果】以上説明したごとく、本発明によれば、
油に汚染された土壌から連続的に汚染物質を除去するこ
とができ、かつ高コストな焼却分として排出される土壌
量を最小限に抑えることができる。従って、本発明によ
り汚染土壌の優れた低コストな処理技術が提供されるこ
ととなり環境保護にも寄与できる。
As described above, according to the present invention,
The pollutants can be continuously removed from the oil-contaminated soil, and the amount of soil discharged as high-cost incineration can be minimized. Therefore, the present invention provides an excellent low-cost treatment technique for contaminated soil and can contribute to environmental protection.

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

【図1】本発明の油汚染土壌の浄化方法の一実施例を示
す工程図である。
FIG. 1 is a process diagram showing one embodiment of a method for purifying oil-contaminated soil according to the present invention.

【図2】同上の浄化方法の混合・攪拌工程における回転
円筒状容器を例示した概略図で、(a)は一部省略概略
縦断側面図、(b)は概略縦断正面図である。
FIG. 2 is a schematic view illustrating a rotating cylindrical container in a mixing / stirring step of the above purification method, in which (a) is a schematic vertical sectional side view partially omitted, and (b) is a schematic vertical sectional front view.

【符号の説明】[Explanation of symbols]

1 は混合・攪拌工程 2 分離工程 3 油分回収工程 4 は固相回収工程 5 土壌分離工程 6 油分分離工程 7 加温工程 8 オイルセパレータ 11 回転円筒状容器 11−1 回転軸 11−2 撹拌羽根 11−3 搬送用の羽根 1 is a mixing / stirring step 2 Separation step 3 Oil recovery step 4 is a solid phase recovery step 5 Soil separation step 6 Oil separation step 7 Heating step 8 Oil separator 11 Rotating cylindrical container 11-1 Rotating shaft 11-2 Stirrer blade 11 -3 blades for transport

───────────────────────────────────────────────────── 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) B03B 5/00 B03B 5/00 Z 5/28 B 5/28 5/66 5/66 7/00 7/00 9/06 9/06 B09B 5/00 ZABS B09C 1/02 3/00 304K 1/08 Fターム(参考) 4D004 AA41 AB02 CA10 CA13 CA15 CA22 CA35 CA40 CB09 CB28 CB34 CB45 CC03 DA03 DA06 DA09 4D056 AB01 AB13 AC22 BA13 CA06 CA13 CA17 DA01 DA05 4D071 AA04 AA05 AA53 AA64 4G036 AA04 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification code FI Theme coat ゛ (Reference) B03B 5/00 B03B 5/00 Z 5/28 B 5/28 5/66 5/66 7/00 7 / 00 9/06 9/06 B09B 5/00 ZABS B09C 1/02 3/00 304K 1/08 F term (reference) 4D004 AA41 AB02 CA10 CA13 CA15 CA22 CA35 CA40 CB09 CB28 CB34 CB45 CC03 DA03 DA06 DA09 4D056 AB01 AB13 AC22 BA13 CA06 CA13 CA17 DA01 DA05 4D071 AA04 AA05 AA53 AA64 4G036 AA04

Claims (10)

【特許請求の範囲】[Claims] 【請求項1】 油で汚染された土壌を浄化する方法であ
つて、周面部に開孔部を持たず、かつ容器内側に容器内
径の1/15以上の高さを有する回転軸に平行な複数の
撹拌羽根を持ち、かつ容器内側に土壌を容器の円筒軸方
向に向かって搬送する羽根を複数持つ回転円筒容器中
で、処理対象汚染土壌と水を土壌の固体濃度にて50%
〜80%の範囲で混合・撹拌する工程と、処理汚染対象
物と水の混合物を浮上油分と固相と懸濁液相との3部に
分離する工程と、分離した浮上油分と固相とを別々に回
収する工程とを有する油汚染土壌の浄化方法。
1. A method for purifying soil contaminated with oil, wherein the method has no opening on the peripheral surface and is parallel to a rotating shaft having a height of at least 1/15 of the inner diameter of the container inside the container. In a rotating cylindrical container having a plurality of stirring blades and a plurality of blades for transporting soil toward the cylindrical axis of the container inside the container, the contaminated soil to be treated and water are reduced to 50% by solid concentration of the soil.
Mixing and stirring in the range of ~ 80%, separating the mixture of water to be treated and water into three parts, a floating oil component, a solid phase and a suspension phase, Recovering oil separately from the soil.
【請求項2】 油で汚染された土壌を浄化する方法であ
つて、水平面に対し周面部が5〜30゜の範囲で傾斜を
つけて設置され、かつ周面部に開孔部を持たず、かつ容
器内側に容器内径の1/15以上の高さを有する、回転
軸に平行な複数の撹拌羽根を持つ回転円筒容器中で、処
理対象汚染土壌と水を土壌の固体濃度にて50%〜80
%の範囲で混合・撹拌する工程と、処理汚染対象物と水
の混合物を浮上油分と固相と懸濁液相との3部に分離す
る工程と、分離した浮上油分と固相とを別々に回収する
工程とを有する油汚染土壌の浄化方法。
2. A method for purifying soil contaminated with oil, wherein the peripheral surface is installed at an angle of 5 to 30 ° with respect to a horizontal plane, and the peripheral surface has no opening, In a rotary cylindrical container having a plurality of agitating blades parallel to the rotation axis and having a height of 1/15 or more of the inner diameter of the container inside the container, the contaminated soil and water to be treated are reduced to a solid concentration of 50% to 50%. 80
%, A step of separating the mixture of water to be treated and water into three parts of a floating oil, a solid phase, and a suspension phase, and a step of separately separating the floating oil and the solid phase. And a method of purifying oil-contaminated soil.
【請求項3】 油で汚染された土壌を浄化する方法であ
って、水平面に対し周面部が5〜30゜の範囲で傾斜を
つけて設置され、かつ周面部に開孔部を持たず、かつ容
器内側に容器内径の1/15以上の高さを有する、回転
軸に平行な複数の攪拌羽根を持ち、かつ容器内側に土壌
を容器の円筒軸方向に向かって搬送する羽根を複数持つ
回転円筒容器中で、処理対象汚染土壌と水を土壌の固体
濃度にて50%〜80%の範囲で混合・撹拌する工程
と、処理汚染対象物と水の混合物を浮上油分と固相と懸
濁液相との3部に分離する工程と、分離した浮上油分と
固相とを各々に回収する工程を有する油汚染土壌の浄化
方法。
3. A method for purifying soil contaminated with oil, wherein the peripheral surface is installed at an angle of 5 to 30 ° with respect to a horizontal plane, and the peripheral surface has no opening, A rotation having a plurality of stirring blades having a height of 1/15 or more of the inner diameter of the container inside the container and parallel to the rotation axis, and having a plurality of blades inside the container for transporting soil toward the cylindrical axis of the container. Mixing and agitating the contaminated soil and water to be treated in a cylindrical container in a solid concentration range of 50% to 80% in a solid concentration of the soil; and suspending the mixture of the contaminated soil and water to be treated with a floating oil component and a solid phase. A method for purifying oil-contaminated soil, comprising a step of separating into three parts of a liquid phase and a step of recovering the separated floating oil component and solid phase, respectively.
【請求項4】 回転円筒容器中内にある土壌を容器の円
筒軸方向に向かって搬送する羽根の向きを、周面底部の
傾斜方向とは逆の向きに付けることを特徴とする請求項
3記載の油汚染土壌の浄化方法。
4. A blade for transporting soil in a rotating cylindrical container in a cylindrical axis direction of the container is oriented in a direction opposite to an inclination direction of a bottom portion of a peripheral surface. The method for purifying oil-contaminated soil according to the above.
【請求項5】 回転円筒状容器内にある土壌を容器の円
筒軸方向に向かって搬送する羽根の長さを中心角として
60〜270゜であり、かつ隣り合った羽根の個々の間
隔を中心角として30〜60゜開けることを特徴とする
請求項1および3ないし4のいずれか1項記載の油汚染
土壌の浄化方法。
5. The length of a blade for transporting soil in a rotating cylindrical container in the cylindrical axis direction of the container is 60 to 270 ° as a central angle, and the distance between adjacent blades is centered. The method for purifying oil-contaminated soil according to any one of claims 1 and 3 to 4, wherein the corner is opened by 30 to 60 degrees.
【請求項6】 浮上油と固相と懸濁液相との3部に分離
する前に汚染土壌と水の混合物を振動篩、可動棒篩、サ
イクロン分級機、水力分級機の何れかを用いて一定粒径
以上の土壌と粒径以下のスラリーに分離することを特徴
とする請求項1ないし5のいずれか1項記載の油汚染土
壌の浄化方法。
6. A method for separating a mixture of contaminated soil and water using a vibrating sieve, a movable rod sieve, a cyclone classifier, or a hydraulic classifier before separating the mixture into three parts, a floating oil, a solid phase, and a suspension phase. The method for purifying oil-contaminated soil according to any one of claims 1 to 5, wherein the soil is separated into a soil having a certain particle size or more and a slurry having a particle size not more than a predetermined particle size.
【請求項7】 分離後の固相は、回転円筒状容器に返送
することを特徴とする請求項1ないし6のいずれか1項
記載の油汚染土壌の浄化方法。
7. The method for purifying oil-contaminated soil according to claim 1, wherein the separated solid phase is returned to a rotating cylindrical container.
【請求項8】 懸濁液相中の懸濁成分に付着している油
分を、pH調整もしくは超音波処理を行うことにより分
離・浮上させること特徴とする請求項1ないし7のいず
れか1項記載の油汚染土壌の浄化方法。
8. The method according to claim 1, wherein the oil adhering to the suspended components in the suspension phase is separated and floated by performing pH adjustment or ultrasonic treatment. The method for purifying oil-contaminated soil according to the above.
【請求項9】 浮上油分と固相から分離した液相は、循
環させて回転円筒状容器内で処理対象汚染土壌と混合す
る水として再利用することを特徴とする請求項1ないし
8のいずれか1項記載の油汚染土壌の浄化方法。
9. The method according to claim 1, wherein the floating oil and the liquid phase separated from the solid phase are circulated and reused as water mixed with the contaminated soil to be treated in the rotary cylindrical container. The method for purifying oil-contaminated soil according to claim 1.
【請求項10】 水は循環時に30〜50℃の温度範囲
に加温することを特徴とする請求項9記載の油汚染土壌
の浄化方法。
10. The method according to claim 9, wherein the water is heated to a temperature range of 30 to 50 ° C. during circulation.
JP2001096595A 2001-03-29 2001-03-29 Purification method of oil contaminated soil Withdrawn JP2002282837A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001096595A JP2002282837A (en) 2001-03-29 2001-03-29 Purification method of oil contaminated soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001096595A JP2002282837A (en) 2001-03-29 2001-03-29 Purification method of oil contaminated soil

Publications (1)

Publication Number Publication Date
JP2002282837A true JP2002282837A (en) 2002-10-02

Family

ID=18950495

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001096595A Withdrawn JP2002282837A (en) 2001-03-29 2001-03-29 Purification method of oil contaminated soil

Country Status (1)

Country Link
JP (1) JP2002282837A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003220382A (en) * 2002-01-31 2003-08-05 Sumitomo Metal Mining Co Ltd Apparatus and method for cleaning polluted soil
KR102251029B1 (en) * 2020-10-30 2021-05-13 주식회사 성원리사이클 A cleaning apparatus of a crushed used vinyl

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003220382A (en) * 2002-01-31 2003-08-05 Sumitomo Metal Mining Co Ltd Apparatus and method for cleaning polluted soil
KR102251029B1 (en) * 2020-10-30 2021-05-13 주식회사 성원리사이클 A cleaning apparatus of a crushed used vinyl

Similar Documents

Publication Publication Date Title
EP0460828B1 (en) Method and apparatus for treating contaminated particulate material
US5268128A (en) Method and apparatus for cleaning contaminated particulate material
KR101744849B1 (en) Purification system and purification method for contaminated soil
JP2006116397A (en) Washing method and washing apparatus of contaminated soil
US5223147A (en) Process of treating contaminated soils
US5303871A (en) Process for treating contaminated soil
JP7410245B2 (en) Dioxin-contaminated soil cleaning system and cleaning method
US5115986A (en) Process for treating contaminated soil
JP2005081247A (en) Apparatus for cleaning contaminated soil
JP2001149913A (en) Cleaning method of contaminated soil
JP2002248459A (en) Method for cleaning contaminated soil and apparatus for the same
KR100460629B1 (en) Soil Washing Apparatus and Soil Washing Device Using It
US5421527A (en) Apparatus and method of separating asbestos contaminants from soil
JP2003211129A (en) Method and apparatus for cleaning ash
US5824210A (en) Separation of minerals
JP2002254063A (en) Clarification method and separating equipment for polluted soil
US5779813A (en) Method and apparatus for decontamination of poly chlorinated biphenyl contaminated soil
JP2002282837A (en) Purification method of oil contaminated soil
US5514218A (en) Soil washing process using polymeric sorbents
CZ285832B6 (en) Method for removal of oil from fine solid substances, particularly the remainders of various productions containing metals and contaminated earth and apparatus for carrying out the same
JP6312016B2 (en) Contaminated soil treatment equipment
HU214349B (en) Method and device for continous washing granular substrates
JP4599766B2 (en) Soil cleaning method and apparatus
JP4640673B2 (en) Purification method for highly concentrated oil-contaminated soil
JP2004261795A (en) Method of removing nonvolatile contaminant in soil

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20070511

A761 Written withdrawal of application

Free format text: JAPANESE INTERMEDIATE CODE: A761

Effective date: 20080613