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JPH11347533A - Bioremediation apparatus for dioxins - Google Patents

Bioremediation apparatus for dioxins

Info

Publication number
JPH11347533A
JPH11347533A JP10193548A JP19354898A JPH11347533A JP H11347533 A JPH11347533 A JP H11347533A JP 10193548 A JP10193548 A JP 10193548A JP 19354898 A JP19354898 A JP 19354898A JP H11347533 A JPH11347533 A JP H11347533A
Authority
JP
Japan
Prior art keywords
dioxin
soil
microorganism
contaminated
pcb
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.)
Pending
Application number
JP10193548A
Other languages
Japanese (ja)
Inventor
Motoo Kanke
基夫 管家
Norio Kono
典男 河野
Atsushi Nagatomi
淳 永冨
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP10193548A priority Critical patent/JPH11347533A/en
Publication of JPH11347533A publication Critical patent/JPH11347533A/en
Pending legal-status Critical Current

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  • Fire-Extinguishing Compositions (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To treat stably a soil contaminated by a PCB and dioxin by applying a microorganism of a bacillus subtilis or the like to a place contaminated by the PCB.dioxin of a low concentration over a wide area. SOLUTION: Microorganism decomposition by a thermophinlic bacteria microorganism such as a bacillus subtilis or the like is accelerated by irradiating a soil and an incimeration ash which contain PCB and dioxin with ultraviolet rays. Further, in order to accelerate further the microorganism decomposition, a more effective aerobic fermentation is enabled by using a transfer type rotary roller and a stirring paddle. In execution, treatment material is entered about 100 cm from a surface soil, stirred by cutting back 20 to 80 cm part from the surface soil to make ventilation of air good, and an apparatus which executes efficiently the aerobic fermentation is used. The dioxin becomes thereby decomposable by microorganism by allowing a thermophilic bacteria to act thereon in the place without carrying the contaminated soil to an apparatus assembled at another place, and a dioxin concentration existing in the soil is reduced.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本技術は、焼却炉等によってダイ
オキシンの様な化学物質に汚染、荒廃された土壌に微生
物を使用することで、本来の安全な基準に回復させるこ
とを目的として使用されるものであり、本発明は広範囲
に渡って低濃度のPCB・ダイオキシンに汚染された場
所にバイオレメディエーションを効果的に実施すること
を目的とする。
This technology is used for the purpose of restoring the original safe standard by using microorganisms on soil degraded or contaminated with chemical substances such as dioxin by incinerators and the like. SUMMARY OF THE INVENTION It is an object of the present invention to effectively perform bioremediation in a site that is contaminated with a low concentration of PCB / dioxin over a wide range.

【0002】[0002]

【従来の技術】ダイオキシン類汚染土壌の浄化は、掘削
又はスラリー状にした上で固化技術や超臨界水等の物理
化学手法を用いたり焼却するのが一般的である。但し、
費用対効果の上からこの方法は、狭い範囲の高濃度の場
所に適しているが広い範囲に分布した低濃度の場所には
不適切である。また、焼却は炉の構造が難しく、住民の
説得が困難であるという問題がある。これらを解決する
ために様々なバイオレメディエーションをうたった分解
方法が考案されている。
2. Description of the Related Art In general, dioxin-contaminated soil is generally excavated or slurried and then solidified using a technique such as supercritical water or incinerated. However,
From a cost-effective point of view, this method is suitable for small areas of high concentration, but not for low concentration of widely distributed areas. Also, incineration has a problem that the structure of the furnace is difficult and it is difficult for the residents to persuade. In order to solve these problems, various bioremediation degradation methods have been devised.

【0003】これらバイオレメディエーションには環境
中の分解菌に酸素や栄養分を与えて活性化させる方法。
分解能の高い菌を選別して散布する方法があるがPCB
やダイオキシンを分解処理するには能力が不十分であ
る。最適条件や分解処理する方法や装置は確立されてい
ない
[0003] These bioremediation is a method in which oxygen and nutrients are given to decomposing bacteria in the environment to activate them.
There is a method to select and spray bacteria with high resolution, but PCB
And the ability to decompose dioxins is insufficient. Optimum conditions and methods and equipment for decomposition have not been established

【0004】[0004]

【本発明が解決しようとする課題】ベトナム戦争で使用
されたダイオキシンが数十年を経た今もまだ残ってお
り、ベトナムの人々を苦しめているのはニュースでも報
道されている。また、その一方でダイオキシンが年々徐
々に分解されているのも事実である。これは暑い地域に
生息する自然界の微生物による分解が行われている為で
ある。これらの高温度下で活発に働く高温菌を図1のよ
うな構造を持つ建屋で汚染土壌を紫外線照射させた後に
混入し(1)のような装置で攪拌させることでPCB・
ダイオキシンを効率よく分解することを目的とする。
[Problems to be Solved by the Invention] Dioxins used in the Vietnam War are still present after decades, and it is reported in the news that they are afflicting the people of Vietnam. On the other hand, it is true that dioxin is gradually decomposed year by year. This is because natural microorganisms that live in hot areas are decomposing. These high-temperature bacteria active at high temperatures are mixed in the building having the structure as shown in FIG.
It aims to decompose dioxin efficiently.

【0005】[0005]

【課題を解決する手段1】PCB・ダイオキシンを含む
土壌や焼却灰に紫外線照射を当てることによって、微生
物が活発に分解できるようにする。
Means for Solving the Problems 1) Microorganisms can be actively decomposed by irradiating ultraviolet rays to soil or incineration ash containing PCB / dioxin.

【作用1】本発明に於いて、図1のように紫外線ランプ
を当てることで表面を親水化した高分子化合物に対して
高温菌を付着させると微生物分解を促進することは確認
されている。
Action 1 In the present invention, it has been confirmed that when a high-temperature bacterium adheres to a polymer compound whose surface has been hydrophilized by irradiating an ultraviolet lamp as shown in FIG. 1, microbial decomposition is promoted.

【0006】[0006]

【課題を解決する手段2】好気性高温の微生物をPCB
・ダイオキシンを含む土壌に加えることで分解能力を高
め、反応速度を早める。
Means for Solving the Problems 2) Aerobic and high-temperature microorganisms are converted to PCB
・ By adding to dioxin-containing soil, the decomposition ability is enhanced and the reaction speed is increased.

【作用2】本発明で使用するバチラス・スブチルス等の
高温菌微生物は凍結融解装置を用いて発泡化したゴムに
対して高温で微生物分解をおこさせることが実証されて
いる。
[Action 2] It has been demonstrated that thermophilic microorganisms such as Bacillus subtilis used in the present invention can decompose rubber foamed at a high temperature using a freeze-thaw apparatus.

【0007】[0007]

【課題を解決する手段3】微生物分解を更に促進させる
為に、移動式回転ローラや攪拌パドルを用いることでよ
り効率の良い好気性発酵を行うことができる。
Means for Solving the Problems 3 In order to further promote microbial decomposition, more efficient aerobic fermentation can be performed by using a movable rotary roller or a stirring paddle.

【作用3】本発明に於いて図1のように処理物を表土か
ら100cm程度入れ、表土から20〜80cmの部分
を切り返すことでかき混ぜ、空気の通気を良くし、好気
性発酵を効率よく行う装置を作ることを実現した。
[Function 3] In the present invention, as shown in FIG. 1, a treated material is put in about 100 cm from the topsoil, and a portion of 20 to 80 cm from the topsoil is cut back to stir to improve air ventilation and efficiently perform aerobic fermentation. The device was realized.

【0008】[0008]

【課題を解決する手段4】PCB・ダイオキシンに汚染
された土壌を現地で処理するようにする。
Means for Solving the Problems 4 Soil contaminated with PCB and dioxin is to be treated on site.

【作用4】図1のような組立式反応槽を製作し用いるこ
とで微生物分解を行い、汚染された土壌を安全な土壌に
戻すことができる。これによって汚染土壌を他場所で組
み立てた装置まで運び入れることなく、その場で高温菌
を作用させダイオキシンを微生物分解することが可能に
なり、土壌にあるダイオキシン濃度を低減する。
[Function 4] By constructing and using a prefabricated reaction tank as shown in FIG. 1, microorganisms can be decomposed and contaminated soil can be returned to safe soil. As a result, the dioxin can be microbially decomposed by the action of thermophilic bacteria on the spot without transporting the contaminated soil to a device assembled elsewhere, thereby reducing the dioxin concentration in the soil.

【0009】[0009]

【課題を解決する手段5】PCB・ダイオキシンに汚染
された土壌をより安定して処理するために副資剤や発酵
促進剤を投与する。
Means for Solving the Problems 5 In order to more stably treat soil contaminated with PCB / dioxin, a secondary material or a fermentation promoter is administered.

【作用5】補助剤としてリグニンを主体とするものを投
入することで微生物が分解速度を上げる。
[Function 5] By adding a substance mainly composed of lignin as an auxiliary, the microorganisms increase the decomposition rate.

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

【図1】本発明の簡単な構成図FIG. 1 is a simple configuration diagram of the present invention.

【符号の説明】[Explanation of symbols]

(1)紫外線ランプ(夜間用) (2)紫外線透過シートまたはガラス (3)排気口 (3)排気口 (4)攪拌パドル(自送式またはチェーン駆動) (1) Ultraviolet lamp (for night use) (2) Ultraviolet transparent sheet or glass (3) Exhaust port (3) Exhaust port (4) Stirring paddle (self-feeding type or chain drive)

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 バチラス・スブチルス菌等の微生物をP
CB・ダイオキシンの分解に利用する。
1. A microorganism such as Bacillus subtilis bacterium is
Used for decomposition of CB / dioxin.
【請求項2】 請求項1に記載の処理に於いて、図1に
示す反応装置を作成、使用することで汚染土壌を移動さ
せずに処理することを目的とする。
2. A process according to claim 1, wherein the reaction device shown in FIG. 1 is prepared and used so that the contaminated soil is processed without moving.
【請求項3】 請求項1に記載の処理に於いて、図1に
示す装置を使用することで微量に含むPCB・ダイオキ
シンを満遍なく処理することができる。
3. In the treatment according to claim 1, PCBs and dioxins containing trace amounts can be uniformly treated by using the apparatus shown in FIG.
【請求項4】 請求項1に記載の処理に於いて、図1
(2)に示す紫外線透過シートまたはガラス使用をする
ことで太陽からの紫外線を透過し、有効に利用する。ま
た夜間や雨天の日は図1(1)に示す紫外線ランプを使
用する。
4. The processing according to claim 1, wherein
By using an ultraviolet ray transmitting sheet or glass shown in (2), ultraviolet rays from the sun are transmitted and used effectively. At night or on rainy days, an ultraviolet lamp shown in FIG. 1A is used.
【請求項5】 請求項1に記載の処理に於いて、図1に
示す装置を使用することで焼却炉から出た、焼却灰を処
理することも可能である。
5. In the treatment according to claim 1, it is possible to treat incineration ash discharged from the incinerator by using the apparatus shown in FIG.
JP10193548A 1998-06-03 1998-06-03 Bioremediation apparatus for dioxins Pending JPH11347533A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10193548A JPH11347533A (en) 1998-06-03 1998-06-03 Bioremediation apparatus for dioxins

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10193548A JPH11347533A (en) 1998-06-03 1998-06-03 Bioremediation apparatus for dioxins

Publications (1)

Publication Number Publication Date
JPH11347533A true JPH11347533A (en) 1999-12-21

Family

ID=16309902

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10193548A Pending JPH11347533A (en) 1998-06-03 1998-06-03 Bioremediation apparatus for dioxins

Country Status (1)

Country Link
JP (1) JPH11347533A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2003101472A1 (en) * 2002-05-31 2003-12-11 Calpis Co., Ltd. Dioxin elimination promoter

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2003101472A1 (en) * 2002-05-31 2003-12-11 Calpis Co., Ltd. Dioxin elimination promoter
JPWO2003101472A1 (en) * 2002-05-31 2005-09-29 カルピス株式会社 Dioxin exclusion promoter
JP4652050B2 (en) * 2002-05-31 2011-03-16 カルピス株式会社 Dioxin extermination accelerator
US8877483B2 (en) 2002-05-31 2014-11-04 Calpis Co., Ltd. Dioxin elimination promoter

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