JP2000343072A - Treatment of granule to which pollutant is stuck - Google Patents

Treatment of granule to which pollutant is stuck

Info

Publication number
JP2000343072A
JP2000343072A JP11161611A JP16161199A JP2000343072A JP 2000343072 A JP2000343072 A JP 2000343072A JP 11161611 A JP11161611 A JP 11161611A JP 16161199 A JP16161199 A JP 16161199A JP 2000343072 A JP2000343072 A JP 2000343072A
Authority
JP
Japan
Prior art keywords
particles
liquid
treated water
tank
particulate matter
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
JP11161611A
Other languages
Japanese (ja)
Other versions
JP4132413B2 (en
Inventor
Akio Tango
堯雄 反後
Hiroshi Ito
洋 伊藤
Yutaka Shinoda
豊 信太
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.)
Shinroku Seiki KK
Yoyu Shigen KK
Kumagai Gumi Co Ltd
Original Assignee
Shinroku Seiki KK
Yoyu Shigen KK
Kumagai Gumi Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Shinroku Seiki KK, Yoyu Shigen KK, Kumagai Gumi Co Ltd filed Critical Shinroku Seiki KK
Priority to JP16161199A priority Critical patent/JP4132413B2/en
Priority to SG1999005288A priority patent/SG73677A1/en
Priority to US09/422,782 priority patent/US6402064B1/en
Priority to EP99120904A priority patent/EP0997202A3/en
Priority to CN99123287A priority patent/CN1256977A/en
Priority to KR1019990047392A priority patent/KR20000052354A/en
Priority to CA002287958A priority patent/CA2287958A1/en
Priority to BR9904989A priority patent/BR9904989A/en
Priority to IDP991005D priority patent/ID25768A/en
Priority to AU57154/99A priority patent/AU5715499A/en
Publication of JP2000343072A publication Critical patent/JP2000343072A/en
Priority to US09/950,936 priority patent/US20020079392A1/en
Application granted granted Critical
Publication of JP4132413B2 publication Critical patent/JP4132413B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
  • Processing Of Solid Wastes (AREA)
  • Crushing And Grinding (AREA)
  • Disintegrating Or Milling (AREA)

Abstract

PROBLEM TO BE SOLVED: To separate the granule free from a pollutant and large in particle size while adding water from the granule subjected to granulating treatment and to which the pollutant is stuck. SOLUTION: In the treating method, the water to be treated and containing the granule to which a pollutant is stuck is classified by using a liq. cyclone 51 after temporarily storing the water to be treated in a feed sump 40. Moreover, the treated water discharged from the upper part of the liq. cyclone 51 and containing the granule low in particle size and the treated water obtained by separating the granule large in particle size from the soil water containing the granule separated at the liq. cyclone 51 and large in particle size by a dehydrating vibrating screen 53 are returned again to the feed sump 40.

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、重金属類や油性分
等で汚染された土壌や焼却炉から搬出された焼却灰など
の汚染物質の付着した粒状体を細粒化し、上記細粒化さ
れた粒状体から汚染物質を含まないあるいは大部分を除
去した粒状体を分離する方法に関するものである。
BACKGROUND OF THE INVENTION The present invention relates to a method for reducing the size of granules adhering to contaminants such as soil contaminated with heavy metals and oily substances, and incineration ash discharged from an incinerator, and the above-mentioned fine granulation. The present invention relates to a method for separating a granular material containing no or most of contaminants from the granular material.

【0002】[0002]

【従来の技術】近年、化学工場や金属精錬工場等の工場
近辺の土壌は、重金属類や有機塩素化合物あるいは油性
分等で汚染されていることが問題視されている。また、
海難事故等により海に流出した原油で汚染された海浜の
土壌や、原油存在地盤のトンネル掘削に伴い搬出される
掘削土には原油が付着しているため、その処理が困難と
なることがしばしばある。更には、産業廃棄物やリサイ
クルができない生ゴミ等の可燃物は焼却炉にて焼却さ
れ、焼却灰として廃棄物処分場に搬出されて埋設される
が、このような焼却灰には、重金属類や焼却過程で生じ
たダイオキシン等の汚染物質が付着している。そこで、
上記汚染土壌から上記汚染物質を除去した後、石,砂,
微粒分等を抽出して再利用する技術や、焼却灰から汚染
物質を除去した後有効利用できる固体粒子を抽出すると
ともに、処分場に廃棄する焼却灰の減容化を図る技術の
確立が望まれている。
2. Description of the Related Art In recent years, it has been considered that soil near factories such as chemical factories and metal refining factories is contaminated with heavy metals, organic chlorine compounds, oily components, and the like. Also,
Crude oil is often attached to seashore soil contaminated with crude oil spilled into the sea due to a marine accident or excavated soil carried out due to the excavation of a tunnel in a crude oil-existing ground. is there. Furthermore, combustible materials such as industrial waste and non-recyclable garbage are incinerated in an incinerator and transported to a waste disposal site as incinerated ash for burial. And contaminants such as dioxin generated during the incineration process. Therefore,
After removing the contaminants from the contaminated soil, stone, sand,
It is hoped that there will be a technology to extract and reuse fine particles, etc., and a technology to extract solid particles that can be used effectively after removing contaminants from incineration ash and to reduce the volume of incineration ash that is disposed of at the disposal site. It is rare.

【0003】一般に、焼却灰は、粒径の小さな粒子同士
が団粒状態となった粒状体であり、重金属類やダイオキ
シン類等の汚染物質は上記粒状体の表面だけでなく、個
々の粒子の表面に付着していると考えられている。ま
た、汚染土壌については、塊状になってはいるものの団
粒化している部分が少なく、汚染物質は個々の粒子の表
面に付着していると考えられている。そこで、本出願人
は、焼却灰のような団粒化された粒状体を種々の大きさ
の粒子に細粒化するとともに、上記各粒子の表面に付着
している重金属類等の汚染物質を効率的に離脱し分離す
ることのできる細粒化装置を提案している(特願平10
−310429号)。これは、投入した処理材料を、処
理空隙内で加水しながら、圧縮及び粒状体相互間の擦り
合わせの力を作用させて、上記焼却灰を独立した粒子に
分離するとともに、上記粒状体や粒子の表面に付着して
いる異物を分離する細粒化手段を複数段に渡って設け、
焼却灰が各細粒化手段を順次通過するようにするととも
に、上記細粒化手段の処理空隙を下流段において次第に
狭く設定し、上流段においては主に団粒状の粒状体を、
個々の粒子を破壊することなくほぼ独立した粒子に分離
して粒状化する解砕処理を行い、下流段においては主に
上記粒状化された個々の粒子に対して、主に各粒子相互
間の擦り合わせの力を作用させて、粒子同士の摩擦によ
る相互研磨を行わせ、上記個々の粒子の表面に付着して
いる異物を分離する解膠処理を行うようにしたもので、
処理材料は上記焼却灰に限らず、上記汚染土壌であって
も同様の処理によって上記土壌に付着した汚染物質を分
離ことができる。なお、上記分離された重金属類等の汚
染物質は処理水中に浮遊または溶解するので、上記処理
後の粒状体の内汚染物質を含まない粒径の大きな粒状体
には上記汚染物質がほとんど付着されていない。
[0003] Generally, incinerated ash is a granular material in which particles having a small particle size are aggregated, and contaminants such as heavy metals and dioxins are not only present on the surface of the granular material but also on individual particles. It is believed that it is attached to the surface. Contaminated soil, although clumped, has few aggregated portions, and contaminants are considered to be attached to the surface of individual particles. Accordingly, the present applicant has reduced the aggregated granular material such as incineration ash into particles of various sizes, and has eliminated contaminants such as heavy metals adhering to the surface of each particle. A grain refiner capable of separating and separating efficiently has been proposed (Japanese Patent Application No. Hei.
-310429). This is to apply the processing material that has been charged, while adding water within the processing space, and to apply the force of compression and rubbing between the granular materials to separate the incinerated ash into independent particles, and to separate the granular materials and the particles. A fine-graining means for separating foreign substances adhering to the surface is provided over a plurality of stages,
As the incineration ash passes through each of the granulating means sequentially, the processing gap of the above-mentioned granulating means is set gradually narrower in the downstream stage, and mainly in the upstream stage, aggregated granules are formed.
Performs a crushing process in which the individual particles are separated into almost independent particles without breaking, and granulated, and in the downstream stage, the above-mentioned granulated individual particles are mainly treated, mainly between the respective particles. By applying the force of the rubbing, the mutual polishing by the friction between the particles is performed, and the deflocculation process for separating the foreign substances attached to the surface of the individual particles is performed.
The material to be treated is not limited to the incinerated ash, and even in the case of the contaminated soil, the contaminants attached to the soil can be separated by the same treatment. Since the separated contaminants such as heavy metals float or dissolve in the treatment water, the contaminants are almost adhered to the large-sized particles that do not contain the contaminants in the treated particles. Not.

【0004】この細粒化装置で処理された粒状体を含む
処理水は、液体供給槽に一時貯蔵された後、液体サイク
ロン等の分級手段によって種々の大きさの粒状体に分級
される。このとき、汚染物質を含まない粒径の大きな粒
状体は重金属類やダイオキシン類が分離され無害化され
ているので、セメント用の骨材等に再利用される。ま
た、重金属やダイオキシン類等の微粒片を多く含む有害
な汚泥は溶融固化等の処理を施し廃棄し、重金属類が溶
解あるいは浮遊している汚水はキレート剤等の添加によ
って上記重金属類の不溶化塩を形成させ重金属類を不溶
化することにより、上記重金属類を上記処理液から分離
することで無害化し、再利用あるいは廃棄する。
[0004] Treated water containing the granular material treated by the fine-granulating apparatus is temporarily stored in a liquid supply tank and then classified into various-sized granular materials by a classification means such as a hydrocyclone. At this time, since the heavy particles and dioxins are separated and made harmless, the granular material having a large particle size that does not contain pollutants is reused as aggregate for cement and the like. In addition, harmful sludge containing a large amount of fine particles such as heavy metals and dioxins is subjected to a treatment such as melting and solidification and discarded, and the sewage in which the heavy metals are dissolved or suspended is added with a chelating agent or the like to insolubilize the heavy metals. Is formed, and the heavy metals are insolubilized, thereby detoxifying the heavy metals by separating them from the treatment liquid, and reused or discarded.

【0005】[0005]

【発明が解決しようとする課題】ところで、液体サイク
ロンは、上部からは粒径の小さな粒子を含む処理水を排
出し、下部排出口からは泥水状となった粒径の大きな粒
子を排出するものであるが、実際には、1回の分級処理
では、上記液体サイクロン上部からは粒径の大きな粒子
の一部が排出されてしまう場合があり、粒径の大きな粒
状体を確実に分離することが困難であった。
The liquid cyclone discharges treated water containing small-sized particles from the upper part and discharges muddy large-sized particles from the lower discharge port. However, in practice, in a single classification process, a part of the particles having a large particle diameter may be discharged from the upper part of the hydrocyclone. Was difficult.

【0006】本発明は、従来の問題点に鑑みてなされた
もので、加水しながら細粒化処理された汚染物質が付着
した粒状体中から、汚染物質を含まないあるいは大部分
を除去した粒径の大きな粒状体を確実に分離する方法を
提供することを目的とする。
SUMMARY OF THE INVENTION The present invention has been made in view of the problems in the prior art, and has been made in such a manner that particles containing no or most of contaminants are removed from granules adhering to contaminants which have been subjected to graining treatment while adding water. It is an object of the present invention to provide a method for reliably separating a granular material having a large diameter.

【0007】[0007]

【課題を解決するための手段】本発明の請求項1に記載
の汚染物質が付着した粒状体の処理方法は、汚染物質が
付着した粒状体を加水しながら細粒化した後、液体サイ
クロンの液体供給槽に貯蔵し、上記液体供給槽の下部か
ら送られてきた上記粒状体を含む処理水を液体サイクロ
ンを用いて分級するとともに、上記液体サイクロンの上
部から排出された粒径の小さな粒状体を含む処理水を、
上記液体供給槽に戻すようにしたことを特徴とする。
According to a first aspect of the present invention, there is provided a method for treating particulate matter to which contaminants have adhered, comprising the steps of: The treated water containing the granular material stored in the liquid supply tank and sent from the lower part of the liquid supply tank is classified using a liquid cyclone, and the granular material having a small particle diameter discharged from the upper part of the liquid cyclone Treated water containing
The liquid supply tank is returned to the liquid supply tank.

【0008】請求項2に記載の汚染物質が付着した粒状
体の処理方法は、液体サイクロンの下部から排出された
泥水から粒径の大きな粒状体を分離した処理水も、上記
液体供給槽に戻すようにしたことを特徴とする。
[0010] In the method for treating particulate matter to which contaminants adhere, the treated water obtained by separating the particulate matter having a large particle diameter from the muddy water discharged from the lower part of the liquid cyclone is returned to the liquid supply tank. It is characterized by doing so.

【0009】請求項3に記載の汚染物質が付着した粒状
体の処理方法は、上記細粒化された粒状体を貯蔵する液
体供給槽の本体と、その上部及び下部で連通するシール
タンクを設けるとともに、上記液体サイクロンの上部か
ら排出された粒径の小さな粒状体を含む処理水を、上記
シールタンクに送るようにしたことを特徴とする。
According to a third aspect of the present invention, there is provided a method for treating particulate matter to which contaminants adhere, comprising a main body of a liquid supply tank for storing the finely divided particulate matter, and a seal tank communicating with upper and lower parts of the liquid supply tank. In addition, treated water containing particulate matter having a small particle diameter discharged from the upper part of the liquid cyclone is sent to the seal tank.

【0010】請求項4に記載の汚染物質が付着した粒状
体の処理方法は、内周面に複数の外羽根を有する円筒状
の回転ドラムと、外周面に複数の内羽根を有し上記回転
ドラムの内部に回転ドラムに対し偏心して取付けられた
ロータとを備えた細粒化装置の上記回転ドラムと上記ロ
ータとの処理空間に、汚染物質が付着した粒状体を投入
し、加水しながら細粒化した後、液体サイクロンの液体
供給槽に貯蔵ようにしたことを特徴とする。
According to a fourth aspect of the present invention, there is provided a method for treating particulate matter to which contaminants are adhered, wherein the rotary drum includes a cylindrical rotary drum having a plurality of outer blades on an inner peripheral surface and a plurality of inner blades on an outer peripheral surface. The granular material to which the contaminants are attached is charged into the processing space between the rotary drum and the rotor of the fine-graining apparatus, which includes a rotor eccentrically mounted on the rotary drum inside the drum, and finely mixes with water. After granulation, the liquid is stored in a liquid supply tank of a liquid cyclone.

【0011】[0011]

【発明の実施の形態】以下、本発明の実施の形態につい
て、図面に基づき説明する。図1は、本発明の実施の形
態に係わる汚染土壌の処理システムの概要を示す図で、
同図において、18は汚染土壌を投入する受入ホッパ、
19は上記汚染土壌を搬送するベルトコンベア、20は
上記ベルトコンベア19で送られてきた汚染土壌に対し
て加水しつつ解砕・解膠処理を行い汚染土壌をスラリー
化して排出する細粒化装置、30は細粒化装置20から
排出された汚染土壌から5mm以上の粒子を選別し分離
する振動スクリーン、40は上記振動スクリーン30を
通過した5mm以下の粒子含む泥状の汚染土壌を一時貯
蔵するとともに、液体サイクロン51に処理水を供給す
るための液体供給槽であるフィードサンプ、50は上記
液体サイクロン51を備え、フィードサンプ40から送
られた汚染土壌を種々の大きさの粒子に分級するための
分級手段、60は上記細粒化装置20及び上記フィード
サンプ40に処理水を供給する給水部、70は上記分級
手段50から排出される処理水を浄化する汚水処理部で
ある。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a diagram showing an outline of a system for treating contaminated soil according to an embodiment of the present invention.
In the figure, 18 is a receiving hopper for charging contaminated soil,
Reference numeral 19 denotes a belt conveyor that conveys the contaminated soil, and reference numeral 20 denotes a fine-granulating device that disintegrates and pulverizes the contaminated soil sent by the belt conveyor 19 while slurrying and discharging the contaminated soil. , 30 is a vibrating screen for selecting and separating particles of 5 mm or more from the contaminated soil discharged from the grain refiner 20, and 40 is a temporary storage of mud-like contaminated soil containing particles of 5 mm or less passing through the vibrating screen 30. A feed sump, which is a liquid supply tank for supplying treated water to the liquid cyclone 51, is provided with the liquid cyclone 51, and is used to classify contaminated soil sent from the feed sump 40 into particles of various sizes. Is a water supply section for supplying treated water to the granulating device 20 and the feed sump 40, and 70 is discharged from the classification means 50. A wastewater treatment unit for purifying the treated water.

【0012】細粒化装置20は、図示しない排出口に設
けられた約30mm以上の大型の金属類や挟雑物等の固
形物を捕獲するための分級用の網21aを備え、ベルト
コンベア19により搬送された汚染土壌に加水し、上記
汚染土壌に対して粗い解砕処理を行う一次細粒化機21
と、この一次細粒化機21で解砕された汚染土壌から1
0mm以上の粒状体を選別し分離する振動スクリーン2
2と、一次細粒化機21で解砕され振動スクリーン22
を通過した10mm以下の粒状体となった汚染土壌に加
水し、上記汚染土壌に対して更に解砕・解膠処理を行う
ための二次細粒化機23と、上記振動スクリーン22と
二次細粒化機23との間に設けられ、上記振動スクリー
ン22を通過した粒状体含む処理水の水切り処理を行う
水切装置24とを備えている。分級手段50は、上記フ
ィードサンプ40に貯蔵された5mm以下の粒子を含ん
だ泥状の汚染土壌から約50μm以下の粒子を処理水中
に浮遊させて分離する液体サイクロン51と、この液体
サイクロン51の底部から排出されスピゴットタンク5
2に一次貯蔵されたスラリーから約50μm以上の砂分
を主体とした細粒砂等の粒子を分離する脱水振動スクリ
ーン53と、上記フィードサンプ40の上部から供給さ
れた微粒片が浮遊した処理水中の固形物を凝集沈殿させ
るシックナータンク54と、上記シックナータンク54
の底部に沈殿したスラリーを貯蔵するスラリー槽55
と、上記スラリー槽55に貯蔵されたスラリーに脱水処
理を施すための脱水機56とを備えている。また、汚水
処理部70は、処理水中に溶解あるいは浮遊している重
金属類を不溶化する処理水槽71と、この処理水槽71
で不溶化された重金属類等や油性分を吸着材で濾過し上
記処理水を浄化する液体濾過装置72とを備えている。
The grain refining apparatus 20 includes a classifying net 21a provided at a discharge port (not shown) for catching solids such as large metals and contaminants of about 30 mm or more. Primary grinder 21 that hydrates contaminated soil conveyed by the above and performs coarse crushing treatment on the contaminated soil.
From the contaminated soil crushed by the primary granulator 21
Vibrating screen 2 for sorting and separating granular materials of 0 mm or more
2 and a vibrating screen 22 which is crushed by the primary
A secondary granulator 23 for adding water to contaminated soil that has become a granular material of 10 mm or less that has passed through the filter, and further performing crushing and peptizing treatment on the contaminated soil; A draining device 24 is provided between the refining device 23 and drains treated water including the granular material that has passed through the vibrating screen 22. The classification means 50 includes a liquid cyclone 51 for separating particles of about 50 μm or less from the mud-like contaminated soil containing the particles of 5 mm or less stored in the feed sump 40 by suspending the particles in the treatment water and separating the liquid cyclone 51. Spigot tank 5 discharged from the bottom
A dewatering vibrating screen 53 for separating particles such as fine-grained sand mainly composed of sand of about 50 μm or more from the slurry primarily stored in Step 2, and treated water in which fine particles supplied from the upper part of the feed sump 40 are floating A thickener tank 54 for coagulating and sedimenting the solid matter of
Tank 55 for storing the slurry precipitated at the bottom of the tank
And a dehydrator 56 for dehydrating the slurry stored in the slurry tank 55. The sewage treatment section 70 includes a treatment water tank 71 for insolubilizing heavy metals dissolved or floating in the treatment water,
And a liquid filtration device 72 for filtering the treated water by filtering heavy metals and the like or oily components insolubilized with the adsorbent.

【0013】図2は、上記一次細粒化機21の構成を示
す図で、(a)図は側面図、(b)図は(a)図のA−
A断面図である。一次細粒化機21は、内周面に軸方向
に沿って取付けられ、中心方向に突出する複数の外羽根
11Wを有する円筒状の回転ドラム11と、外周面に軸
方向に沿って取付けられ径方向に突出する複数の内羽根
12Wを有し、上記回転ドラム11の内部に偏心して取
付けられたロータ12とを備え、回転ドラム11の外周
に設けられた環状歯車13をモータ14により、ロータ
12の回転軸15を駆動機構16により、それぞれ互い
に逆方向に回転させ、材料投入口17から投入された処
理材料S(図(b)の斜線部)に圧縮及びせん断応力を
作用させて上記処理材料Sを解砕したり解膠したりする
もので、上記処理材料に作用する応力の大きさは、主に
回転ドラム11とロータ12との間隔(ロータ12の偏
心度)と、回転ドラム11及びロータ12のそれぞれの
回転速度とにより調整するようにしている。また、二次
細粒化機23の構成は、上記一次細粒化機21とほぼ同
様である。
FIGS. 2A and 2B show the structure of the primary granulator 21. FIG. 2A is a side view, and FIG.
It is A sectional drawing. The primary grain refiner 21 is attached to the inner peripheral surface in the axial direction, and has a cylindrical rotating drum 11 having a plurality of outer blades 11W protruding in the center direction, and attached to the outer peripheral surface in the axial direction. A rotor 12 having a plurality of radially projecting inner blades 12W and eccentrically mounted inside the rotary drum 11; and an annular gear 13 provided on the outer circumference of the rotary drum 11 The rotating shaft 15 is rotated in opposite directions to each other by a drive mechanism 16 to apply compressive and shear stress to the processing material S (hatched portion in FIG. 8B) input from the material input port 17 to perform the above-described processing. The material S is crushed or deflocculated. The magnitude of the stress acting on the processing material mainly depends on the distance between the rotating drum 11 and the rotor 12 (the eccentricity of the rotor 12) and the rotating drum 11 And low It is to be adjusted by the respective rotational speeds of 12. The configuration of the secondary granulator 23 is almost the same as that of the primary granulator 21 described above.

【0014】汚染土壌の粗い解砕を行う一次細粒化機2
1は、図3(a)に示すように、ロータ12の偏心量を
小さくすることにより回転ドラム11とロータ12との
間隔D1を比較的広くするとともに、回転速度を低速と
している。また、汚染土壌の解膠処理を主体とする二次
細粒化機23は、図3(b)に示すように、ロータ12
の偏心量を大きくして回転ドラム11とロータ12との
間隔D2を狭くし、更に、回転速度を上記一次細粒機2
1の速度よりも高速にするとともに、図4に示すよう
に、下流側のロータ径を上流側のロータ径よりも大きく
し、汚染土壌の処理空隙が下流方向において不連続にか
つ狭くなるように構成されている。
A primary refining machine 2 for coarsely crushing contaminated soil
1, as shown in FIG. 3 (a), with a relatively wide spacing D 1 of the the rotary drum 11 and the rotor 12 by reducing the eccentricity of the rotor 12, and the rotational speed and low speed. Further, as shown in FIG. 3B, the secondary fine-granulating machine 23 mainly for peptizing the contaminated soil is
The eccentric amount is increased to narrow the distance D 2 between the rotary drum 11 and the rotor 12, further, a rotational speed said primary granules machine 2
As shown in FIG. 4, the rotor diameter on the downstream side is made larger than the rotor diameter on the upstream side so that the treatment gap of the contaminated soil becomes discontinuous and narrow in the downstream direction. It is configured.

【0015】一次細粒化機21,二次細粒化機23中で
は、図5に示すように、処理空隙である回転ドラム11
とロータ12との間隙に投入された汚染土壌Pは、回転
ドラム11の外羽根11Wによって上方に掻き上げられ
るとともに、ロータ12の内羽根12Wによって下方に
引き下げられるので、汚染土壌Pには圧縮応力とともに
せん断応力が作用し、上記汚染土壌の団粒状の各粒状体
は解砕・解膠される。すなわち、図6(a)に示すよう
に、粒子p同士が固着面rで固着されて団粒状態となっ
ている汚染土壌の団粒状の各粒状体Pあるいは粒子同士
が固着してはいないが大きさの大きい粒子pに対して圧
縮応力及びせん断応力が作用すると、上記団粒状の各粒
状体Pが上記固着面rのところから分かれてほぼ独立し
た細かな粒子pに粒状化される(解砕作用)とともに、
上記各粒状体Pの表面に比較的弱く付着されていた重金
属類等の汚染物質qが分離される。また、図6(b)に
示すように、粒状体あるいは粒子同士に擦り合わせ方向
の力が作用すると、各粒子pの表面に付着された重金属
類等の汚染物質qが剥離され粒子pから分離され(解膠
作用)、上記分離された汚染物質qは処理水中に浮遊ま
たは溶解する。なお、汚染土壌の処理においては、土粒
子が団粒化していることが少ないと思われるので、一次
細粒化機21,二次細粒化機23ともに、上記図6
(b)に示す解膠作用が主となる。
As shown in FIG. 5, the rotary drum 11, which is a processing gap,
Soil P introduced into the gap between the rotor and the rotor 12 is lifted up by the outer blades 11W of the rotating drum 11 and pulled down by the inner blades 12W of the rotor 12, so that the contaminated soil P has compressive stress. At the same time, a shear stress acts, and the aggregated granular material of the contaminated soil is pulverized and peptized. That is, as shown in FIG. 6A, the aggregated granular materials P or the particles of the contaminated soil in which the particles p are fixed to each other on the fixing surface r and are in the aggregated state are not fixed. When compressive stress and shear stress act on the large-sized particles p, each of the aggregated granular materials P is separated from the fixing surface r and granulated into almost independent fine particles p (solution). Crushing action)
The contaminants q such as heavy metals that are relatively weakly attached to the surface of each of the granular materials P are separated. Further, as shown in FIG. 6B, when a force in the direction of rubbing acts on the granular material or the particles, the contaminants q such as heavy metals attached to the surface of each particle p are separated and separated from the particle p. (Peptizing action), and the separated contaminants q float or dissolve in the treated water. In the treatment of the contaminated soil, it is considered that the soil particles are less likely to be agglomerated. Therefore, both the primary granulator 21 and the secondary granulator 23 shown in FIG.
The peptizing action shown in FIG.

【0016】液体サイクロン51は、図7に示すよう
に、筒状の本体51aの内壁に、種々の大きさの粒状体
を含んだ液体を高速で噴射し、この液体が一次回転流と
呼ばれる渦V1を形成しながら本体51aの内壁に沿っ
て下部方向に移動する時に、本体51aの中央部の気圧
が減少し、上記液体が二次回転流と呼ばれる渦V2を形
成しながら上記一次回転流V1の内側から本体51aを
上昇する現象を利用した分級装置である。液体サイクロ
ン51に導入された液体に含まれている粒径の大きな粒
子は、上記一次回転流V1により本体51aの内壁に衝
突しながら下方に移動させられ、液体の一部とともに排
出口管51bから排出される。一方、粒径の小さな粒子
は上記二次回転流V2に運ばれて本体の上部方向に移動
し、上昇管51cに吸い込まれて本体51aの上部から
排出され、移送管51dを通って図示しないフィードサ
ンプ40に戻される。この場合、粒径の大きな粒子が上
昇管51cに吸い込まれて液体サイクロン51の上部か
ら排出されることがある。
As shown in FIG. 7, the liquid cyclone 51 injects liquid containing various-sized particles at high speed onto the inner wall of a cylindrical main body 51a, and the liquid is swirled by a vortex called a primary rotational flow. When moving downward along the inner wall of the main body 51a while forming V1, the pressure in the center of the main body 51a decreases, and the liquid forms a vortex V2 called a secondary rotational flow while forming the primary rotational flow V1. This is a classifier utilizing the phenomenon that the body 51a is lifted from the inside of the body. The particles having a large particle diameter contained in the liquid introduced into the hydrocyclone 51 are moved downward while colliding with the inner wall of the main body 51a by the primary rotation flow V1, and are discharged from the outlet pipe 51b together with a part of the liquid. Is discharged. On the other hand, the particles having a small particle diameter are carried by the secondary rotation flow V2 and move upward of the main body, are sucked into the rising pipe 51c, are discharged from the upper part of the main body 51a, and are fed through a transfer pipe 51d. Returned to sump 40. In this case, particles having a large particle diameter may be sucked into the rising pipe 51c and discharged from the upper part of the liquid cyclone 51.

【0017】また、図8(a)は、本発明に関わる液体
供給装置であるフィードサンプ40の一構成例を示す模
式図で、フィードサンプ40は、振動スクリーン30等
から送られてくる5mm以下の粒子含む泥状の汚染土壌
を貯蔵するフィードサンプ本体41と、上部及び下部で
上記フィードサンプ本体41と連通する隔壁42を有
し、液体サイクロン51の上部から排出される粒径の小
さな粒子を貯蔵するシールタンク43と、フィードサン
プ本体41の底部の粒径の大きな粒子を含む処理水を液
体サイクロン51に圧送するポンプ40Pと、上記シー
ルタンク43の上澄み液をシックナータンク54に送る
ための導入通路44とを備えている。ここで、42aは
隔壁42の上部連絡口で、図8(b)に示すように、フ
ィードサンプ本体41の上澄み液は、上記上部連絡口4
2aからシールタンク43に移動し、上記シールタンク
43の上澄み液は、上記導入通路44を通ってシックナ
ータンク54に送られる。また、フィードサンプ本体4
1の底部の粒径の大きな粒子を含んだスラリーは、ポン
プ40Pにより液体サイクロン51に送られ再び分級さ
れる。
FIG. 8A is a schematic diagram showing an example of the configuration of a feed sump 40 which is a liquid supply device according to the present invention. The feed sump 40 is 5 mm or less sent from the vibrating screen 30 or the like. A feed sump main body 41 for storing mud-like contaminated soil containing particles, and a partition wall 42 communicating with the feed sump main body 41 at upper and lower portions, and having a small particle diameter discharged from the upper part of the liquid cyclone 51. A seal tank 43 for storage, a pump 40P for pumping treated water containing large-diameter particles at the bottom of the feed sump body 41 to the liquid cyclone 51, and an introduction for sending the supernatant of the seal tank 43 to the thickener tank 54. And a passage 44. Here, reference numeral 42a denotes an upper connection port of the partition wall 42, and as shown in FIG.
From 2a, the liquid moves to the seal tank 43, and the supernatant liquid of the seal tank 43 is sent to the thickener tank 54 through the introduction passage 44. Also, the feed sump body 4
The slurry containing the large-diameter particles at the bottom of 1 is sent to the hydrocyclone 51 by the pump 40P and classified again.

【0018】次に、本発明の汚染土壌の処理方法につい
て説明する。受入ホッパ18に投入された汚染土壌はベ
ルトコンベア19により搬送され、細粒化装置20の一
次細粒化機21に投入される。一次細粒化機21では、
投入された汚染土壌に対して比較的広い処理空間内で加
水しながら粗い解砕を行い、汚染土壌を個々の粒子を破
壊することなく分離させつつ、上記汚染土壌を一次細粒
化機21の下流側に移動させ、図示しない排出口から排
出する。このとき、汚染土壌の表面に弱く付着している
重金属類等の微粒片は剥離されて処理水中に浮遊する。
また、容易に溶解する重金属類は上記処理水中に溶解す
る。一次細粒化機21から排出された大型の金属類や挟
雑物等の固形物は約30mmの分級用の網21aにより
捕獲されて除去され、約30mm以下の粒状体となった
汚染土壌は振動スクリーン22に送られ篩い分けされ1
0〜30mmの粒状体が分離される。振動スクリーン2
2を通過した10mm以下の粒状体を含む処理水は、水
切装置24で水切り処理された後、二次細粒化機23に
送られる。上記水切装置24から排出される微粒子を含
んだ排水はフィードサンプ40に送られ一時貯蔵され
る。
Next, the method for treating contaminated soil according to the present invention will be described. The contaminated soil put into the receiving hopper 18 is conveyed by the belt conveyor 19 and put into the primary granulator 21 of the granulator 20. In the primary refining machine 21,
The introduced contaminated soil is coarsely crushed while being hydrated in a relatively large processing space, and the contaminated soil is separated without destruction of individual particles, and the contaminated soil is separated by the primary fine-granulating machine 21. It is moved downstream, and discharged from a discharge port (not shown). At this time, fine particles such as heavy metals that are weakly attached to the surface of the contaminated soil are peeled off and float in the treated water.
Also, heavy metals that are easily dissolved dissolve in the above treated water. Solid matter such as large metals and contaminants discharged from the primary granulator 21 is captured and removed by a classifying net 21a of about 30 mm, and contaminated soil that has become a granular body of about 30 mm or less is removed. It is sent to the vibrating screen 22 and sieved.
Granules of 0-30 mm are separated. Vibrating screen 2
The treated water containing the granular material of 10 mm or less that has passed through 2 is subjected to a draining treatment by a draining device 24, and then sent to a secondary fine-granulating machine 23. The wastewater containing fine particles discharged from the draining device 24 is sent to the feed sump 40 and temporarily stored.

【0019】二次細粒化機23は、上述したように、一
次細粒化機1よりも汚染土壌に作用する応力が大きいの
で、主に、汚染土壌の個々の粒子間の相互摩擦による解
膠作用により、粘性の大きなカーボンや油性分や汚染土
壌の個々の粒子に強く付着している重金属類の微粒片を
離脱させることができる。このとき、二次細粒化機23
では、水切り処理された処理材料に対して、上記汚染土
壌の個々の粒子が互いに擦り合わせが行えるような適度
の水を加水して上記解膠処理を行う。また、上記処理に
おいて、容易に溶解する重金属類は上記処理水中に溶解
するとともに、汚染土壌の個々の粒子に強く付着してい
カーボンや油性分や重金属類等の汚染物質は上記粒子か
ら分離されて処理水中に浮遊し、上記解砕・解膠処理さ
れた汚染土壌とともに二次細粒化機23の排出口から排
出される。また、二次細粒化機23は、下流側のロータ
径を上流側のロータ径よりも大きくし、汚染土壌の処理
空隙が下流方向において不連続にかつ狭く構成されてい
るので、処理材料はスムーズには下流側に流れず一部の
処理材料は上流側に戻されて滞留するので、処理材料の
解膠処理が更に進行する。
As described above, since the secondary granulator 23 has a higher stress acting on the contaminated soil than the primary granulator 1, the solution mainly due to the mutual friction between the individual particles of the contaminated soil is used. By the glue action, fine particles of heavy metals that are strongly attached to highly viscous carbon, oily components, or individual particles of contaminated soil can be released. At this time, the secondary refiner 23
In the method, the peptizing treatment is performed by adding appropriate water to the drained treatment material so that the individual particles of the contaminated soil can rub against each other. In addition, in the above treatment, heavy metals that are easily dissolved are dissolved in the above treated water, and contaminants such as carbon, oily components, and heavy metals that strongly adhere to individual particles of the contaminated soil are separated from the particles. It floats in the treated water, and is discharged from the outlet of the secondary granulator 23 together with the crushed and peptized contaminated soil. In addition, the secondary grain refiner 23 is configured such that the rotor diameter on the downstream side is larger than the rotor diameter on the upstream side, and the processing gap of the contaminated soil is discontinuous and narrow in the downstream direction. Some of the processing material does not flow smoothly to the downstream side, and some of the processing material is returned to the upstream side and stays there, so that the peptizing treatment of the processing material further proceeds.

【0020】二次細粒化機23から排出された汚染土壌
のスラリーと砂や砂礫等の粒子は、振動スクリーン30
により5mm以上の粒子が篩い分され、5mm以下の粒
状体はフィードサンプ40に一時貯蔵された後分級手段
50に送られ、種々の大きさの粒状体に分級される。フ
ィードサンプ40に貯蔵された5mm以下の粒子を含ん
だ泥状の汚染土壌の内、フィードサンプ40の底部の粒
径の大きな粒子を含んだスラリーは、分級手段50の液
体サイクロン51に送られ分級される。液体サイクロン
51では、約50μm以下の微粒子を処理水中に浮遊さ
せて分離し、上記微粒片を含んだ処理水を、移送管51
dを介して、フィードサンプ40に戻すとともに、液体
サイクロン51の底部のスピゴットノズル4から排出さ
れる粒径の大きな粒子からなる固形分の多いスラリーは
スピゴットタンク52に送られ一時貯蔵される。上記ス
ラリーは、脱水振動スクリーン53により約50μm以
上の砂分を主体とした粒子(細粒砂)が分離された後、
フィードサンプ40のシールタンク43に戻される。こ
のシールタンク43の上澄み液は、導入通路44を通っ
てシックナータンク54に送られる。このように、液体
サイクロン51で分級された微粒片を含んだ処理水と、
脱水振動スクリーン53により細粒砂が分離された処理
水とは、ともにフィードサンプ40に戻され、フィード
サンプ40の底部の粒径の大きな粒子を含んだスラリー
が再び液体サイクロン51で分級され、フィードサンプ
40の上澄み液はシックナータンク54に送られる。し
たがって、シックナータンク54へは微粒片のみを含ん
だ処理水を供給することができる。
The slurry of the contaminated soil and the particles such as sand and gravel discharged from the secondary grain refiner 23
The particles having a size of 5 mm or more are sieved, and the granules having a size of 5 mm or less are temporarily stored in a feed sump 40 and then sent to a classification means 50 to be classified into granules having various sizes. Among the mud-like contaminated soil containing particles of 5 mm or less stored in the feed sump 40, the slurry containing the large-diameter particles at the bottom of the feed sump 40 is sent to the liquid cyclone 51 of the classification means 50 and classified. Is done. In the hydrocyclone 51, fine particles having a particle size of about 50 μm or less are floated and separated in the treated water, and the treated water containing the fine particles is transferred to the transfer pipe 51.
While returning to the feed sump 40 via d, the slurry containing a large amount of solids and having a large particle diameter discharged from the spigot nozzle 4 at the bottom of the hydrocyclone 51 is sent to the spigot tank 52 and temporarily stored. After the particles (fine-grained sand) mainly composed of sand of about 50 μm or more are separated by the dehydrating vibrating screen 53,
It is returned to the seal tank 43 of the feed sump 40. The supernatant liquid of the seal tank 43 is sent to the thickener tank 54 through the introduction passage 44. Thus, treated water containing fine particles classified by the liquid cyclone 51,
The treated water from which the fine-grained sand has been separated by the dewatering vibrating screen 53 is returned to the feed sump 40, and the slurry containing large particles at the bottom of the feed sump 40 is classified again by the liquid cyclone 51, The supernatant of the sump 40 is sent to a thickener tank 54. Therefore, the treated water containing only the fine particles can be supplied to the thickener tank 54.

【0021】シックナータンク54では、フィードサン
プ40の導入通路44から供給された微粒片を含んだ処
理水をタンク内でゆっくりと回転させ、上記処理水中の
固形物を凝集沈殿させる固液分離を行う。上記シックナ
ータンク54の上澄み液には、上述したように、汚染土
壌から分離された重金属類や油性分が溶解あるいは浮遊
しているので、汚水処理部70の処理水槽71に送られ
処理される。この処理水槽71では、キレート剤等の添
加によって上記重金属類の不溶化塩を形成させ重金属類
を不溶化することにより、上記重金属類を上記処理液か
ら分離する。一方、シックナータンク54の底部に沈殿
したスラリー状の汚染土壌は、スラリー槽55に一時貯
蔵された後脱水機56に送り脱水し、図示しないフィル
タプレスにより脱水ケーキを作製する。また、脱水機5
6で脱水された処理水も上記処理水槽71に送られ、重
金属類を不溶化した後、液体濾過装置72に送られる。
液体濾過装置72では、上記処理水を活性炭等の吸着材
で濾過して重金属類を除去して浄化し、上記重金属類を
捕獲した吸着材は最終処分場に送られ処理される。
In the thickener tank 54, the treated water containing the fine particles supplied from the introduction passage 44 of the feed sump 40 is slowly rotated in the tank to perform solid-liquid separation for coagulating and sedimenting solids in the treated water. . As described above, heavy metals and oily components separated from the contaminated soil are dissolved or suspended in the supernatant liquid of the thickener tank 54, so that the supernatant liquid is sent to the treatment water tank 71 of the sewage treatment section 70 for treatment. In the treatment water tank 71, the heavy metals are separated from the treatment liquid by adding a chelating agent or the like to form an insolubilizing salt of the heavy metals and insolubilize the heavy metals. On the other hand, the slurry-like contaminated soil settled at the bottom of the thickener tank 54 is temporarily stored in a slurry tank 55 and then sent to a dehydrator 56 to be dehydrated, and a dewatered cake is prepared by a filter press (not shown). Dehydrator 5
The treated water dehydrated in Step 6 is also sent to the treated water tank 71 to insolubilize heavy metals, and then sent to the liquid filtration device 72.
In the liquid filtration device 72, the treated water is filtered with an adsorbent such as activated carbon to remove and purify heavy metals, and the adsorbent capturing the heavy metals is sent to a final disposal site for treatment.

【0022】このように、本実施の形態では、汚染物質
が付着した粒状体を含む処理水をフィードサンプ40に
一時貯蔵した後、液体サイクロン51を用いて分級する
とともに、上記液体サイクロン51の上部から排出され
る粒径の小さな粒状体を含む処理水と、上記液体サイク
ロン51で分離された粒径の大きな粒状体を含む泥水か
ら脱水振動スクリーン53で上記粒径の大きな粒状体を
分離した処理水とを、再びフィードサンプ40に戻し、
上記フィードサンプ40の底部の粒径の大きな粒子を含
んだスラリーを再び液体サイクロン51で分級するよう
にしたので、液体サイクロン51の上部から排出された
粒径の大きな粒状体を確実に分級することができる。ま
た、汚染土壌等の粒状体を、内周面に複数の外羽根11
Wを有する円筒状の回転ドラム11と、外周面に複数の
内羽根12Wを有し上記回転ドラム11の内部に偏心し
て取付けられたロータ12とを備えた一次細粒化機21
と二次細粒化機23とにより解砕・解膠処理したので、
上記粒状体を効率良く粒状化することができるとととも
に、上記粒状体の個々の粒子に付着している異物を確実
にかつ効率的に分離することができる。
As described above, in the present embodiment, the treated water containing the particulate matter to which the contaminants are attached is temporarily stored in the feed sump 40, and then classified using the liquid cyclone 51. Of separating the large-grained particles with dewatering vibration screen 53 from the treated water containing the small-grained particles discharged from the water and the muddy water containing the large-particles separated by the liquid cyclone 51 The water is returned to the feed sump 40 again,
Since the slurry containing the large-diameter particles at the bottom of the feed sump 40 is classified again by the hydrocyclone 51, the large-particles discharged from the upper part of the hydrocyclone 51 are reliably classified. Can be. Further, a granular material such as contaminated soil is provided on the inner peripheral surface with a plurality of outer blades 11.
W having a cylindrical rotary drum 11 having a plurality of inner blades 12W and a rotor 12 having a plurality of inner blades 12W on its outer peripheral surface and being eccentrically mounted inside the rotary drum 11;
And pulverization and pulverization by the secondary granulator 23,
Not only can the granules be efficiently granulated, but also foreign substances adhering to individual particles of the granules can be reliably and efficiently separated.

【0023】なお、上記実施の形態では、汚染土壌の処
理方法について説明したが、処理材料が焼却灰あるいは
焼却灰を含む汚染土壌である場合にも同様の処理システ
ムで処理することができる。この場合には、焼却灰が団
粒化しているので、一次細粒化機21と二次細粒化機2
3とは、上記図6(a),(b)に示すような解砕・解
膠作用を処理材料に対して行う。また、上記例では、一
次細粒化機21と二次細粒化機23とを備えた細粒化装
置20により解砕・解膠処理した汚染物質が付着した粒
状体を液体サイクロン51により分級したが、細粒化装
置20の構成はこれに限るものではない。例えば、上記
二次細粒化機23と同様の構成の、処理空隙が下流方向
において不連続にかつ狭くなるように構成された1台の
細粒化装置で細粒化処理を行ってもよいし、一般の破砕
機を使用し汚染物質が付着した粒状体を加水しながら細
粒化してもよい。
In the above embodiment, a method for treating contaminated soil has been described. However, even when the material to be treated is incinerated ash or contaminated soil containing incinerated ash, the same treatment system can be used. In this case, since the incinerated ash is agglomerated, the primary and secondary granulators 21 and 2
No. 3 performs the crushing and peptizing action as shown in FIGS. 6A and 6B on the processing material. Further, in the above example, the granular material to which the contaminants adhered after being pulverized and pulverized by the pulverizer 20 having the primary pulverizer 21 and the secondary pulverizer 23 is classified by the liquid cyclone 51. However, the configuration of the grain refiner 20 is not limited to this. For example, the grain refining process may be performed by one grain refining device having the same configuration as that of the secondary grain refining machine 23 and configured so that the processing gap is discontinuous and narrow in the downstream direction. Then, the granules to which the contaminants are attached may be refined while adding water using a general crusher.

【0024】[0024]

【発明の効果】以上説明したように、請求項1に記載の
発明によれば、汚染物質が付着した粒状体を加水しなが
ら細粒化した後、液体サイクロンの液体供給槽に貯蔵
し、上記液体供給槽の下部から送られてきた上記粒状体
を含む処理水を液体サイクロンを用いて分級するととも
に、上記液体サイクロンの上部から排出された粒径の小
さな粒状体を含む処理水を上記液体供給槽に戻すことに
より、上記粒径の小さな粒状体に混入されて戻された粒
径の大きな粒状体も、上記液体供給槽の下部から液体サ
イクロンに送って再度分級するようにしたので、粒径の
大きな粒状体を確実に分級することができる。
As described above, according to the first aspect of the present invention, the granular material to which the contaminant is attached is finely divided while adding water, and then stored in the liquid supply tank of the liquid cyclone. The treated water containing the particulate matter sent from the lower part of the liquid supply tank is classified using a liquid cyclone, and the treated water containing the particulate matter having a small particle diameter discharged from the upper part of the liquid cyclone is supplied to the liquid supply tank. By returning to the tank, the large particles having a large particle diameter mixed back into the small particles having the small particle diameter are also sent to the liquid cyclone from the lower part of the liquid supply tank and classified again. Can be reliably classified.

【0025】請求項2に記載の発明によれば、液体サイ
クロンの下部から排出された泥水から粒径の大きな粒状
体を分離した処理水も、上記液体供給槽に戻すようにし
たので、分級効果を更に向上させることができる。
According to the second aspect of the present invention, the treated water obtained by separating the particulate matter having a large particle diameter from the muddy water discharged from the lower part of the hydrocyclone is returned to the liquid supply tank. Can be further improved.

【0026】請求項3に記載の発明によれば、上記細粒
化された粒状体を貯蔵する液体供給槽の本体と、その上
部及び下部で連通するシールタンクを設けるとともに、
上記液体サイクロンの上部から排出された処理水を、上
記シールタンクに送るようにしたので、液体サイクロン
の上部から上記粒径の小さな粒状体に混入されて排出さ
れた粒径の大きな粒状体も再度分級することができ、粒
径の大きな粒状体を効率良く分級することができる。
According to the third aspect of the present invention, a liquid supply tank for storing the finely divided particles is provided with a seal tank communicating with upper and lower parts of the liquid supply tank.
Since the treated water discharged from the upper part of the hydrocyclone is sent to the seal tank, the large-particles discharged from the upper part of the liquid cyclone mixed with the small-particles having the above-mentioned particle diameter are also returned. Classification can be performed, and a granular material having a large particle size can be efficiently classified.

【0027】請求項4に記載の発明によれば、内周面に
複数の外羽根を有する円筒状の回転ドラムと、外周面に
複数の内羽根を有し上記回転ドラムの内部に回転ドラム
に対し偏心して取付けられたロータとを備えた細粒化装
置の上記回転ドラムと上記ロータとの処理空間に、汚染
物質が付着した粒状体を投入し、加水しながら細粒化し
た後、液体サイクロンの液体供給槽に貯蔵ようにしたの
で、液体サイクロンに投入する汚染土壌等の粒状体を効
率良く粒状化することができるととともに、上記粒状体
の個々の粒子に付着している異物を確実にかつ効率的に
分離することができる。
According to the fourth aspect of the present invention, a cylindrical rotary drum having a plurality of outer blades on an inner peripheral surface and a plurality of inner blades on an outer peripheral surface are provided inside the rotary drum. On the other hand, the granular material to which the contaminant is adhered is charged into the processing space between the rotary drum and the rotor of the granulating device having the rotor eccentrically mounted thereon, and fine particles are formed while adding water. Because the liquid is supplied to the liquid supply tank, the granular material such as contaminated soil to be charged into the liquid cyclone can be efficiently granulated, and the foreign matter adhering to the individual particles of the granular material can be surely removed. And it can separate efficiently.

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

【図1】 本発明の実施の形態に係わる汚染土壌の処理
システムの概要を示す図である。
FIG. 1 is a diagram showing an outline of a contaminated soil treatment system according to an embodiment of the present invention.

【図2】 本実施の形態に係わる一次細粒化機の構成を
示す図である。
FIG. 2 is a diagram showing a configuration of a primary grain refiner according to the present embodiment.

【図3】 一次細粒化機及び二次細粒化機の回転ドラム
とロータとの位置関係を示す図である。
FIG. 3 is a diagram showing a positional relationship between a rotating drum and a rotor of a primary grain refiner and a secondary grain refiner.

【図4】 本実施の形態に係わる二次細粒化機の構成を
示す図である。
FIG. 4 is a diagram showing a configuration of a secondary grain refiner according to the present embodiment.

【図5】 本実施の形態に係わる解砕・解膠処理を説明
する図である。
FIG. 5 is a diagram illustrating a crushing and peptizing process according to the present embodiment.

【図6】 本実施の形態に係わる解砕・解膠作用を説明
する図である。
FIG. 6 is a diagram for explaining a crushing / peptizing action according to the present embodiment.

【図7】 液体サイクロンの構成を示す模式図である。FIG. 7 is a schematic diagram illustrating a configuration of a hydrocyclone.

【図8】 本実施の形態に係わるフィードサンプの構成
を示す図である。
FIG. 8 is a diagram showing a configuration of a feed sump according to the present embodiment.

【符号の説明】[Explanation of symbols]

11 回転ドラム、11W 外羽根、12 ロータ、1
2W 内羽根、13 環状歯車、14 モータ、15
ロータの回転軸、16 駆動機構、17 材料投入口、
18 受入ホッパ、19 ベルトコンベア、20 細
粒化装置、21 一次細粒化機、22 振動スクリー
ン、23 二次細粒化機、24 水切装置、30 振動
スクリーン、40 フィードサンプ、50 分級手段、
51 液体サイクロン、52 スピゴットタンク、53
脱水振動スクリーン、54 シックナータンク、55
スラリー槽、56 脱水機、60 給水部、70 汚
水処理部、71 処理水槽、72 液体濾過装置。
11 rotating drum, 11W outer blade, 12 rotor, 1
2W inner blade, 13 ring gear, 14 motor, 15
Rotary axis of rotor, 16 drive mechanism, 17 material input port,
Reference Signs List 18 receiving hopper, 19 belt conveyor, 20 grain refiner, 21 primary grain refiner, 22 vibrating screen, 23 secondary grain refiner, 24 drainer, 30 vibrating screen, 40 feed sump, 50 classifier,
51 hydrocyclone, 52 spigot tank, 53
Dewatering vibration screen, 54 thickener tank, 55
Slurry tank, 56 dehydrator, 60 water supply section, 70 sewage treatment section, 71 treated water tank, 72 liquid filtration device.

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) B09B 3/00 ZAB B09B 3/00 ZABZ (72)発明者 反後 堯雄 東京都新宿区新宿2丁目3番13号大橋ビル 7階 溶融資源株式会社内 (72)発明者 伊藤 洋 東京都新宿区津久戸町2番1号 株式会社 熊谷組東京本社内 (72)発明者 信太 豊 埼玉県大里郡寄居町桜沢265番地 新六精 機株式会社内 Fターム(参考) 4D004 AA36 AA41 AB02 AB03 AB06 AB07 AC05 BA02 CA01 CA04 CA10 CA13 CA50 CB09 CB11 CB44 CB50 4D063 EE06 EE11 EE21 GA10 GC01 GC07 GC16 GC27 GC36 GD27 4D067 EE01 EE12 EE16 EE42 GA03 GA20 4D071 AA05 AA53 AB13 AB14 AB25 CA01 CA05 DA20 Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat II (Reference) B09B 3/00 ZAB B09B 3/00 ZABZ (72) Inventor Takao Sachigo 2-3-13 Shinjuku, Shinjuku-ku, Tokyo The 7th floor of the Ohashi Building Melting Resources Co., Ltd. (72) Inventor Hiroshi Ito 2-1 Tsukudo-cho, Shinjuku-ku, Tokyo Headquarters, Kumagaya Gumi Tokyo headquarters (72) Inventor Yutaka Shinta 265 Sakurazawa, Yorii-cho, Osato-gun, Saitama New R-Seiki Co., Ltd. F-term (reference) 4D004 AA36 AA41 AB02 AB03 AB06 AB07 AC05 BA02 CA01 CA04 CA10 CA13 CA50 CB09 CB11 CB44 CB50 4D063 EE06 EE11 EE21 GA10 GC01 GC07 GC16 GC27 GC36 GD27 4D067 EE01 EE12 A05 GA16 AB13 AB14 AB25 CA01 CA05 DA20

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 汚染物質が付着した粒状体を加水しなが
ら細粒化した後、液体サイクロンの液体供給槽に貯蔵
し、上記液体供給槽の下部から送られてきた上記粒状体
を含む処理水を液体サイクロンを用いて分級するととも
に、上記液体サイクロンの上部から排出された粒径の小
さな粒状体を含む処理水を、上記液体供給槽に戻すよう
にしたことを特徴とする汚染物質が付着した粒状体の処
理方法。
1. A treated water containing the above-mentioned particulate matter which is stored in a liquid supply tank of a liquid cyclone, and is then sent from a lower part of the above-mentioned liquid supply tank. A liquid contaminant is characterized by using a liquid cyclone and classifying the treated water containing the particulate matter having a small particle diameter discharged from the upper part of the liquid cyclone back to the liquid supply tank. Processing method of granular material.
【請求項2】 液体サイクロンの下部から排出された泥
水から粒径の大きな粒状体を分離した処理水を、上記液
体供給槽に戻すようにしたことを特徴とする請求項1記
載の汚染物質が付着した粒状体の処理方法。
2. The method according to claim 1, wherein treated water obtained by separating particulate matter having a large particle diameter from muddy water discharged from a lower part of the liquid cyclone is returned to the liquid supply tank. A method for treating adhered particulate matter.
【請求項3】 上記細粒化された粒状体を貯蔵する液体
供給槽の本体と、その上部及び下部で連通するシールタ
ンクを設けるとともに、上記液体サイクロンの上部から
排出された粒径の小さな粒状体を含む処理水を、上記シ
ールタンクに送るようにしたことを特徴とする請求項1
記載の汚染物質が付着した粒状体の処理方法。
3. A main body of a liquid supply tank for storing the finely divided granules, a seal tank communicating with upper and lower portions of the main body, and a small particle having a small particle diameter discharged from an upper part of the liquid cyclone. 2. The processing water containing the body is sent to the seal tank.
A method for treating particulate matter to which the contaminant described above has adhered.
【請求項4】 内周面に複数の外羽根を有する円筒状の
回転ドラムと、外周面に複数の内羽根を有し上記回転ド
ラムの内部に回転ドラムに対し偏心して取付けられたロ
ータとを備えた細粒化装置の上記回転ドラムと上記ロー
タとの処理空間に、汚染物質が付着した粒状体を投入
し、加水しながら細粒化したことを特徴とする請求項1
記載の汚染物質が付着した粒状体の処理方法。
4. A cylindrical rotary drum having a plurality of outer blades on an inner peripheral surface, and a rotor having a plurality of inner blades on an outer peripheral surface and mounted eccentrically to the rotary drum inside the rotary drum. 2. A granular material to which a contaminant is adhered is introduced into a processing space between the rotary drum and the rotor of a grain refiner provided, and is granulated while adding water.
A method for treating particulate matter to which the contaminant described above has adhered.
JP16161199A 1998-10-30 1999-06-08 Method for treating particulate matter with contaminants attached Expired - Fee Related JP4132413B2 (en)

Priority Applications (11)

Application Number Priority Date Filing Date Title
JP16161199A JP4132413B2 (en) 1999-06-08 1999-06-08 Method for treating particulate matter with contaminants attached
SG1999005288A SG73677A1 (en) 1998-10-30 1999-10-20 Method and system for carrying out treatment of granular substances with pollutants adhered
US09/422,782 US6402064B1 (en) 1998-10-30 1999-10-21 Method and system for carrying out treatment of granular substances with pollutants adhered
CN99123287A CN1256977A (en) 1998-10-30 1999-10-29 Method and equipment for processing particle with pollutant
KR1019990047392A KR20000052354A (en) 1998-10-30 1999-10-29 Method and system for carrying out treatment of granular substances with pollutants adhered
CA002287958A CA2287958A1 (en) 1998-10-30 1999-10-29 Method and system for carrying out treatment of granular substances with pollutants adhered
EP99120904A EP0997202A3 (en) 1998-10-30 1999-10-29 Method and system for carrying out treatment of granular substances with pollutants adhered
BR9904989A BR9904989A (en) 1998-10-30 1999-10-29 Process for treating granular substances with adherent pollutants and medium and system for treating granular substances with adherent pollutants.
IDP991005D ID25768A (en) 1998-10-30 1999-10-29 METHODS AND SYSTEMS FOR IMPLEMENTING TREATMENT OF GRANTS SUBSTANCED BY POLLUTANTS
AU57154/99A AU5715499A (en) 1998-10-30 1999-10-29 Method and system for carrying out treatment of granular substances with pollutants adhered
US09/950,936 US20020079392A1 (en) 1998-10-30 2001-09-12 Method and system for carrying out treatment of granular substances with pollutants adhered

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16161199A JP4132413B2 (en) 1999-06-08 1999-06-08 Method for treating particulate matter with contaminants attached

Publications (2)

Publication Number Publication Date
JP2000343072A true JP2000343072A (en) 2000-12-12
JP4132413B2 JP4132413B2 (en) 2008-08-13

Family

ID=15738465

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16161199A Expired - Fee Related JP4132413B2 (en) 1998-10-30 1999-06-08 Method for treating particulate matter with contaminants attached

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Country Link
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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003103248A (en) * 2001-09-28 2003-04-08 Dowa Mining Co Ltd Method for treating contaminated soil
JP2007050347A (en) * 2005-08-18 2007-03-01 Shinroku Seiki Kk Crushing polishing apparatus and treating method of contaminated soil using it
JP2007175585A (en) * 2005-12-27 2007-07-12 Tokuyama Corp Treatment method of contaminated soil
JP2010029809A (en) * 2008-07-30 2010-02-12 Okumura Corp Polluted soil purifying method
JP2010029808A (en) * 2008-07-30 2010-02-12 Okumura Corp Polluted soil purifying method
JP2011255261A (en) * 2010-06-07 2011-12-22 Taihei Sangyo Co Ltd Treatment method of construction sludge and reclaimed sand from construction sludge

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003103248A (en) * 2001-09-28 2003-04-08 Dowa Mining Co Ltd Method for treating contaminated soil
JP2007050347A (en) * 2005-08-18 2007-03-01 Shinroku Seiki Kk Crushing polishing apparatus and treating method of contaminated soil using it
JP2007175585A (en) * 2005-12-27 2007-07-12 Tokuyama Corp Treatment method of contaminated soil
JP2010029809A (en) * 2008-07-30 2010-02-12 Okumura Corp Polluted soil purifying method
JP2010029808A (en) * 2008-07-30 2010-02-12 Okumura Corp Polluted soil purifying method
JP2011255261A (en) * 2010-06-07 2011-12-22 Taihei Sangyo Co Ltd Treatment method of construction sludge and reclaimed sand from construction sludge

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