JP2002263633A - Cleaning device for contaminated soil - Google Patents

Cleaning device for contaminated soil

Info

Publication number
JP2002263633A
JP2002263633A JP2001064738A JP2001064738A JP2002263633A JP 2002263633 A JP2002263633 A JP 2002263633A JP 2001064738 A JP2001064738 A JP 2001064738A JP 2001064738 A JP2001064738 A JP 2001064738A JP 2002263633 A JP2002263633 A JP 2002263633A
Authority
JP
Japan
Prior art keywords
contaminated soil
rotary kiln
dust
exhaust gas
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.)
Granted
Application number
JP2001064738A
Other languages
Japanese (ja)
Other versions
JP4617010B2 (en
Inventor
Kazuhiro Yamada
和寛 山田
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.)
Nikko Co Ltd
Nikko KK
Original Assignee
Nikko Co Ltd
Nikko 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 Nikko Co Ltd, Nikko KK filed Critical Nikko Co Ltd
Priority to JP2001064738A priority Critical patent/JP4617010B2/en
Publication of JP2002263633A publication Critical patent/JP2002263633A/en
Application granted granted Critical
Publication of JP4617010B2 publication Critical patent/JP4617010B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/25Process efficiency

Abstract

PROBLEM TO BE SOLVED: To provide a cleaning device for contaminated soil which suitably performs heating/cleaning of the contaminated soil. SOLUTION: A rotary kiln 1 of a parallel flow heating type which heat-treats contaminated soil is provided with a soil supplying means 5 for supplying contaminated soil at a burner 6 arrangement side. An exhaust duct 8 of the rotary kiln 1 is provided with a gas temperature sensor 17. Amount of burner combustion is controlled by a burner combustion controller 18 so that the detected value of the gas temperature sensor 17 may become equal to or more than the boiling point of volatile contaminant in the contaminated soil, or the prescribed value near the boiling point. Thereby, the volatile contaminant in the dust entrained with the waste gas and scattered is exposed to high temperature atmosphere, and is subjected to volatilization-separation or decomposition during the period until the contaminant reaches a dust collector or during the period it is being captured by the dust collector 9.

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、油分などの揮発性
有機化合物や水銀類などの揮発性のある汚染物質を含ん
だ汚染土壌を加熱して浄化処理する装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for purifying contaminated soil containing volatile organic compounds such as oil and volatile contaminants such as mercury by heating.

【0002】[0002]

【従来の技術】近年、産業活動に伴って各事業所の敷地
内やその周辺地域の土壌が油等の揮発性汚染物質の廃液
によって汚染され、その土壌の地下を流れる地下水にま
で汚染が及んでいるといったことが取り沙汰されて問題
となっている。このように汚染された土壌を処理するた
めに、その土壌を掘削して加熱用ロータリーキルンへ投
入し、土壌を揮発性汚染物質の沸点温度以上、例えば、
揮発性汚染物質が灯油であれば沸点180〜300℃、
重油であれば沸点350℃以上または近くまで加熱昇温
させて土壌にしみ込んでいる揮発性汚染物質を揮発分離
または分解させて土壌の浄化処理を行っている。
2. Description of the Related Art In recent years, soil in the premises of each business site and the surrounding area has been contaminated with wastewater of volatile contaminants such as oil due to industrial activities, and the groundwater flowing under the soil has been contaminated. It has been a problem that it has been talked about. In order to treat soil contaminated in this way, the soil is excavated and thrown into a rotary kiln for heating, and the soil is heated above the boiling point of volatile contaminants, for example,
If the volatile contaminant is kerosene, the boiling point is 180-300 ° C,
In the case of heavy oil, the soil is purified by heating and raising the temperature up to or near the boiling point of 350 ° C. to volatilize and separate or decompose volatile contaminants permeating the soil.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、ロータ
リーキルンにて油分を含む汚染土壌を沸点以上に加熱し
て飛散するダストの汚染濃度を測定したところ、例え
ば、汚染濃度500ppmの汚染土壌の加熱浄化処理時
に、ロータリーキルン下流の慣性集塵機にて捕捉したダ
ストが1000ppm、またバグフィルターにて捕捉し
たダストが3000ppmの高濃度となっているのが測
定され、揮発性汚染物質の多くがロータリーキルンのガ
ス流に同伴して飛散してしまっていることがわかった。
したがって、特に高沸点の重油などを含んだ土壌を従来
のように沸点以上に加熱昇温させて浄化処理するのは経
済的な面を含めて問題があるのではないかと考えた。
However, when the contaminated soil containing oil was heated to a boiling point or higher in a rotary kiln and the contaminated concentration of the scattered dust was measured, for example, the contaminated soil having a contaminated concentration of 500 ppm was heated and purified. It was measured that the dust trapped by the inertial dust collector downstream of the rotary kiln had a high concentration of 1000 ppm, and the dust trapped by the bag filter had a high concentration of 3000 ppm. Most of the volatile pollutants were entrained in the gas flow of the rotary kiln. And found that it had been scattered.
Therefore, it was thought that there would be a problem, including the economical aspect, that heating and raising the temperature of a soil containing a high-boiling fuel oil or the like to a temperature higher than the boiling point, as in the past, would be a problem.

【0004】本発明は上記の点に鑑み、加熱用ロータリ
ーキルンにて汚染土壌を好適に加熱浄化処理する汚染土
壌の浄化装置を提供することを課題とする。
SUMMARY OF THE INVENTION In view of the above, it is an object of the present invention to provide an apparatus for purifying contaminated soil by appropriately heating and purifying the contaminated soil with a rotary kiln for heating.

【0005】[0005]

【課題を解決するための手段】本発明者は、鋭意研究を
重ねた結果、加熱用ロータリーキルンにて揮発性汚染物
質を含む汚染土壌を汚染物質の沸点以上の温度となるよ
うに段階的に加熱しても集塵機にて捕捉するダストの汚
染濃度の変化が少ないこと、また、この理由としてロー
タリーキルン内の風速が速くて微粒子に含まれる揮発性
汚染物質が揮発分離または分解されないまま飛散してし
まうために集塵機にて捕捉されるダストが十分浄化され
ていないことを知見し、汚染土壌、特に沸点の高い重油
などを含む土壌を沸点以上またはその付近まで加熱昇温
させることに拘るより飛散するダスト中の揮発性汚染物
質を効果的に浄化処理させる方を優先すべきであるとの
結論に至った。
Means for Solving the Problems As a result of intensive studies, the present inventor has conducted a stepwise heating of a contaminated soil containing volatile contaminants to a temperature higher than the boiling point of the contaminants using a heating rotary kiln. Even if the dust concentration in the dust collector is small, the wind speed in the rotary kiln is so high that the volatile contaminants contained in the fine particles are scattered without being separated or decomposed. In the dust collected by the dust collector is not sufficiently purified, and contaminated soil, especially soil containing high boiling point heavy oil, is heated up to or near the boiling point. It was concluded that priority should be given to effectively purifying volatile contaminants.

【0006】そこで、従来のように汚染土壌の加熱温度
よりロータリーキルンの排ガス温度に重要な意味がある
と考え、排ガス温度を揮発性汚染物質の沸点以上または
その付近の高温に維持しておけば飛散したダスト分が集
塵機に至るまでの間、更に集塵機にて捕捉されている間
にも加熱されてダスト中の揮発性汚染物質を揮発分離さ
せることができると共に、揮発した汚染物質を集塵機内
にて凝固させることもなく、ダストの汚染濃度を低減で
きると考えた。また、排ガス温度を高温に維持し、かつ
排ガス温度にてバーナ燃焼量を制御するためには、ロー
タリーキルンでの加熱方式が向流加熱方式より汚染土壌
と熱風を並行して流す並流加熱方式の方が好ましいと考
えた。
Therefore, it is considered that the exhaust gas temperature of the rotary kiln is more important than the heating temperature of the contaminated soil as in the prior art, and if the exhaust gas temperature is maintained at a high temperature equal to or higher than the boiling point of the volatile contaminants, scattering will occur. During the time that the collected dust reaches the dust collector and is further trapped by the dust collector, it is heated to volatilize and separate volatile pollutants in the dust, and the volatilized pollutants are collected in the dust collector. It was thought that the dust concentration could be reduced without coagulation. In addition, in order to maintain the exhaust gas temperature at a high temperature and control the burner combustion amount at the exhaust gas temperature, the heating method in the rotary kiln uses a cocurrent heating method in which contaminated soil and hot air flow in parallel from the countercurrent heating method. I thought it was better.

【0007】即ち、本発明は上記の課題を解決するため
に、請求項1記載の汚染土壌の浄化装置にあっては、汚
染土壌を加熱処理するバーナを備えた加熱用ロータリー
キルンと、該加熱用ロータリーキルンから導出される排
ガス中のダストを捕捉する集塵機を備えると共に、該加
熱用ロータリーキルンのバーナ配置側に汚染土壌を供給
する土壌供給手段を配設する一方、加熱用ロータリーキ
ルンの排ガス排出部には排ガス温度を検出するガス温度
センサーを備え、該ガス温度センサーにより検出した排
ガス温度に基づいてバーナの燃焼量を制御するバーナ燃
焼量制御器を備えたことを特徴としている。
That is, in order to solve the above-mentioned problems, the present invention relates to a contaminated soil purification apparatus according to claim 1, wherein a heating rotary kiln provided with a burner for heat-treating the contaminated soil is provided. A dust collector for capturing dust in exhaust gas derived from the rotary kiln is provided, and a soil supply means for supplying contaminated soil is provided on the burner arrangement side of the heating rotary kiln. A gas temperature sensor for detecting the temperature is provided, and a burner combustion amount controller for controlling the burner combustion amount based on the exhaust gas temperature detected by the gas temperature sensor is provided.

【0008】また、請求項2記載の汚染土壌の浄化装置
にあっては、前記バーナ燃焼量制御器はガス温度センサ
ーによって検出する排ガス温度が汚染土壌に含まれる揮
発性汚染物質の沸点以上となるようにバーナの燃焼量を
制御するように構成したことを特徴としている。
Further, in the apparatus for purifying contaminated soil according to claim 2, the exhaust gas temperature detected by the burner combustion amount controller by a gas temperature sensor is equal to or higher than the boiling point of volatile contaminants contained in the contaminated soil. In this manner, the burner combustion amount is controlled.

【0009】また、請求項3記載の汚染土壌の浄化装置
にあっては、前記集塵機にて捕捉したダストを加熱用ロ
ータリーキルン内に投入して高温雰囲気に晒すように構
成したことを特徴としている。
Further, in the apparatus for purifying contaminated soil according to claim 3, the dust collected by the dust collector is thrown into a heating rotary kiln and exposed to a high-temperature atmosphere.

【0010】[0010]

【発明の実施の形態】本発明の請求項1記載の汚染土壌
の浄化装置によれば、加熱用ロータリーキルンに送り込
むバーナの熱風と並行して汚染土壌を供給して汚染土壌
を加熱する。この並流加熱方式では、加熱用ロータリー
キルンに供給される汚染土壌が初期の加熱段階で高温の
熱風と接触し、汚染土壌中の微粒分がガス流に同伴して
飛散する前に汚染土壌中の揮発性汚染物質を効果的に揮
発分離または分解することができる。
According to the apparatus for purifying contaminated soil according to the first aspect of the present invention, the contaminated soil is heated by supplying the contaminated soil in parallel with the hot air from the burner fed to the rotary kiln for heating. In this co-current heating method, the contaminated soil supplied to the heating rotary kiln comes into contact with high-temperature hot air in the initial heating stage, and fine particles in the contaminated soil are scattered before being scattered along with the gas flow. Volatile pollutants can be effectively separated off or decomposed.

【0011】また、加熱用ロータリーキルンから排出さ
れる排ガスの温度をガス温度センサーにて検出してバー
ナ燃焼制御器に取り込み、該バーナ燃焼制御器によって
予め設定した排ガス温度となるようにバーナの燃焼量を
制御するので、排ガス温度を揮発性汚染物質を揮発分離
させることができる温度またはその付近温度に適宜維持
すれば、排ガス中のダスト分が集塵機に至るまでの間、
更に集塵機にて捕捉されている間も加熱されてダスト中
の揮発性汚染物質を揮発分離させることができると共
に、揮発した汚染物質を集塵機内にて凝固させることも
なく、集塵機にて捕捉するダストの汚染濃度を低減する
ことができる。
Further, the temperature of the exhaust gas discharged from the heating rotary kiln is detected by a gas temperature sensor and taken into a burner combustion controller, and the burner combustion amount is controlled by the burner combustion controller so that the exhaust gas temperature is preset. If the exhaust gas temperature is appropriately maintained at or near the temperature at which volatile pollutants can be volatilized and separated, if the dust content in the exhaust gas reaches the dust collector,
In addition, while being trapped by the dust collector, the dust is heated to volatilize and separate volatile contaminants in the dust, and the volatilized contaminants do not solidify in the dust collector. Contamination concentration can be reduced.

【0012】また、本発明の請求項2記載の汚染土壌の
浄化装置によれば、排ガス温度を汚染土壌に含まれる揮
発性汚染物質の沸点以上となるようにバーナ燃焼制御を
行うので、排ガスに同伴して飛散するダスト中の汚染物
質を沸点以上の高温雰囲気に晒して揮発分離または分解
させることができ、ダストの汚染濃度を低減できて汚染
土壌の浄化に好適な装置となる。
Further, according to the apparatus for purifying contaminated soil according to the second aspect of the present invention, burner combustion control is performed so that the temperature of the exhaust gas is equal to or higher than the boiling point of volatile pollutants contained in the contaminated soil. The contaminants in the dust scattered along with it can be exposed to a high-temperature atmosphere having a boiling point or higher to be volatilized and separated or decomposed, so that the concentration of the dust can be reduced, and the apparatus is suitable for purifying the contaminated soil.

【0013】また、本発明の請求項3記載の汚染土壌の
浄化装置によれば、集塵機にて捕捉したダストを加熱用
ロータリーキルン内に供給してロータリーキルン内の高
温雰囲気に晒すことによってダストに付着残留した汚染
物質を揮発分離または分解させる。これによって、別途
の加熱装置がなくてもダストの汚染濃度を更に低減する
ことができる。
[0013] According to the apparatus for purifying contaminated soil according to claim 3 of the present invention, the dust captured by the dust collector is supplied to the rotary kiln for heating and exposed to the high-temperature atmosphere in the rotary kiln, thereby remaining on the dust. Volatiles are separated or decomposed. This makes it possible to further reduce the dust contamination concentration without a separate heating device.

【0014】[0014]

【実施例】以下、本発明の実施例を図面に基づいて説明
する。
Embodiments of the present invention will be described below with reference to the drawings.

【0015】図中の1は、汚染された土壌を掘削したも
のを加熱するロータリーキルンであって、内部に多数の
掻上げ羽根を周設した円筒状のドラム2を回転自在に傾
斜支持し、駆動装置(図示せず)により所定の速度で回
転させている。前記ドラム2の一端には投入ホッパ3
を、他端には排出ホッパ4を配設しており、投入ホッパ
3側に配置した土壌供給手段であるコンベヤ5によって
汚染土壌をドラム2内に投入し、掻上げ羽根で掻上げな
がらドラム2内を転動流下させる間に、投入ホッパ3側
に配設したバーナ6から供給する熱風によって汚染土壌
を加熱して土壌中に含まれる揮発性汚染物質を揮発分離
または分解し、浄化された土壌を排出ホッパ4の排出口
7から排出するようにしている。
In the figure, reference numeral 1 denotes a rotary kiln that heats excavated contaminated soil. The rotary kiln rotatably supports a cylindrical drum 2 having a large number of raising blades provided therein. It is rotated at a predetermined speed by a device (not shown). A charging hopper 3 is provided at one end of the drum 2.
At the other end, a discharge hopper 4 is provided. Contaminated soil is charged into the drum 2 by a conveyor 5 which is a soil supply means disposed on the input hopper 3 side. While rolling down the inside, the contaminated soil is heated by hot air supplied from the burner 6 disposed on the input hopper 3 side to volatilize or decompose volatile contaminants contained in the soil, thereby purifying the soil. Is discharged from the discharge port 7 of the discharge hopper 4.

【0016】ロータリーキルン1の排出ホッパ4上部に
は排ガスを導出する排気ダクト8を連結しており、該排
気ダクト8はその途中に排ガス中のダスト分を除去する
バグフィルタ等の集塵機9を介在させると共に、その下
流に排ガスを吸引する排風機10を介在させて脱臭炉1
1の入口側に連結している。
An exhaust duct 8 for discharging exhaust gas is connected to the upper part of the discharge hopper 4 of the rotary kiln 1, and a dust collector 9 such as a bag filter for removing dust in the exhaust gas is interposed in the exhaust duct 8. At the same time, an exhaust fan 10 for sucking exhaust gas is interposed downstream of the deodorizing furnace 1.
1 is connected to the entrance side.

【0017】脱臭炉11には炉内温度を所定値に維持す
るためのバーナ12を備えており、炉内に導入される排
ガスを高温雰囲気に晒すことによって排ガス中の揮発性
汚染物質を燃焼分解するようにしている。なお、脱臭炉
11は揮発性汚染物質が完全に燃焼分解できるように、
炉内温度を例えば、略750℃以上の高温を維持するよ
うにバーナ12の燃焼量をコントロールすると共に、排
ガスが炉内を通過するのに少なくとも1乃至2秒以上か
かる程度の炉長さを確保することが好ましい。
The deodorizing furnace 11 is provided with a burner 12 for maintaining the temperature in the furnace at a predetermined value. By exposing the exhaust gas introduced into the furnace to a high temperature atmosphere, the volatile pollutants in the exhaust gas are burned and decomposed. I am trying to do it. The deodorizing furnace 11 is designed to completely burn and decompose volatile pollutants.
The combustion amount of the burner 12 is controlled so as to maintain the furnace temperature at, for example, a high temperature of about 750 ° C. or more, and the furnace length is secured such that it takes at least 1 to 2 seconds or more for exhaust gas to pass through the furnace. Is preferred.

【0018】前記脱臭炉11から排出される排ガスは高
温であり、この排ガス熱を有効に利用するために、脱臭
炉11の出口側には熱交換器13を配設している。そし
て、熱交換器13には脱臭炉11のバーナ12に燃焼用
空気を供給するファン14の供給ダクト15を連結して
いる。熱交換器13を通過した脱臭炉11の排ガスは煙
突16より大気中に放出される。
The exhaust gas discharged from the deodorizing furnace 11 has a high temperature, and a heat exchanger 13 is disposed at the outlet side of the deodorizing furnace 11 in order to effectively use the heat of the exhaust gas. The heat exchanger 13 is connected to a supply duct 15 of a fan 14 for supplying combustion air to the burner 12 of the deodorizing furnace 11. Exhaust gas from the deodorizing furnace 11 that has passed through the heat exchanger 13 is released into the atmosphere from a chimney 16.

【0019】ロータリーキルン1出口の排気ダクト8に
はガス温度センサー17を取り付けると共に、該ガス温
度センサー17をバーナ燃焼量制御器18に接続してい
る。バーナ燃焼量制御器18には排ガス温度設定手段を
備えており、該排ガス温度設定手段にて設定された温度
設定値と前記ガス温度センサー17にて取り込んだ検出
値を比較し、その差値量に基づいてバーナ6の燃焼量を
制御して排ガス温度を設定値に維持するようにしてい
る。
A gas temperature sensor 17 is attached to the exhaust duct 8 at the outlet of the rotary kiln 1, and the gas temperature sensor 17 is connected to a burner combustion controller 18. The burner combustion amount controller 18 is provided with exhaust gas temperature setting means, and compares a temperature set value set by the exhaust gas temperature setting means with a detection value taken in by the gas temperature sensor 17 to obtain a difference value. , The combustion amount of the burner 6 is controlled to maintain the exhaust gas temperature at a set value.

【0020】また、集塵機9にて捕捉したダストはスク
リューフィーダ19によってロータリーキルン1の排出
ホッパ4内に供給し、ダストをドラム2内の高温雰囲気
に晒すことができるようにしている。
The dust captured by the dust collector 9 is supplied to the discharge hopper 4 of the rotary kiln 1 by the screw feeder 19, so that the dust can be exposed to the high temperature atmosphere in the drum 2.

【0021】ロータリーキルン1から排出される土壌や
ダストは高温かつ乾燥しているために取り扱いにくいの
で、土壌水冷装置20に供給して水を浴びせ、湿潤、冷
却させて取り扱いやすいようにする。この土壌水冷装置
20はケーシング21内に撹拌羽根22を適宜間隔で取
り付けた軸体23を貫通させて両端部を回転自在に軸支
し、駆動装置(図示せず)にて所定速度で回転させるよ
うにすると共に、ケーシング21の一端に土壌の供給口
24を、他端に排出口25を備えている。
Since the soil and dust discharged from the rotary kiln 1 are difficult to handle because they are hot and dry, the soil and dust are supplied to the soil water cooling device 20 to be immersed in water, wet and cooled to make them easy to handle. In the soil water cooling device 20, both ends are rotatably supported by penetrating a shaft 23 in which a stirring blade 22 is attached at an appropriate interval in a casing 21, and is rotated at a predetermined speed by a driving device (not shown). In addition, a casing supply port 24 is provided at one end of the casing 21 and a discharge port 25 is provided at the other end.

【0022】また、ケーシング21には水噴射ノズル2
6を取り付け、図示しない水供給源から供給される水を
加熱土壌に向けて噴射して加熱土壌を湿潤、冷却させる
ようにしている。この噴射ノズル26から噴射する水量
は供給される土壌の量と温度を計量コンベヤや温度セン
サーなどの適宜検出手段によって検出し、最適な水量を
決定して噴射すると、供給される土壌の量や温度が変化
しても加湿過多による付着や詰まりを防止できると共
に、加湿不足による粉塵の発生も防止できる。
The casing 21 has a water jet nozzle 2
6, water supplied from a water supply source (not shown) is sprayed toward the heated soil to wet and cool the heated soil. The amount of water to be injected from the injection nozzle 26 is determined by detecting the amount and temperature of the supplied soil by an appropriate detecting means such as a measuring conveyor or a temperature sensor, and determining the optimal amount of water to be injected. Even if is changed, it is possible to prevent adhesion and clogging due to excessive humidification and also to prevent generation of dust due to insufficient humidification.

【0023】しかして、上記装置にて汚染土壌を処理す
るときには、先ず、コンベヤ5によってロータリーキル
ン1の投入ホッパ3側から汚染土壌をドラム2内へ供給
し、汚染土壌がドラム2内を転動流下する間にバーナ6
により送り込んだ熱風と接触させる。このとき、汚染土
壌は熱風と並行に流れて加熱されるので、汚染土壌が初
期の加熱段階で高温の熱風と接触するために、汚染土壌
中の微粒分がドラム2内を通過するガス流に同伴して飛
散する前に汚染土壌中の揮発性汚染物質を効果的に揮発
分離または分解することができる。
When the contaminated soil is to be treated by the above apparatus, first, the contaminated soil is supplied into the drum 2 from the charging hopper 3 side of the rotary kiln 1 by the conveyor 5, and the contaminated soil is tumbled down the drum 2. Burner 6
And contact with the hot air sent. At this time, the contaminated soil flows in parallel with the hot air and is heated, so that the contaminated soil comes into contact with the high-temperature hot air in the initial heating stage, so that the fine particles in the contaminated soil are converted into a gas flow passing through the drum 2. Volatile pollutants in contaminated soil can be effectively volatilized or separated before being accompanied and scattered.

【0024】ロータリーキルン1から導出される排ガス
は排気ダクト8を介して集塵機9へと流れていく。この
排気ダクト8を流れる排ガスの温度はガス温度センサー
17によって検出されてバーナ燃焼制御器18に取り込
まれ、該バーナ燃焼制御器18の排ガス温度設定手段に
設定された排ガス設定値となるようにバーナ6の燃焼量
が制御される。
Exhaust gas discharged from the rotary kiln 1 flows through an exhaust duct 8 to a dust collector 9. The temperature of the exhaust gas flowing through the exhaust duct 8 is detected by a gas temperature sensor 17 and taken in by a burner combustion controller 18 so that the temperature of the exhaust gas is set to an exhaust gas set value set by an exhaust gas temperature setting means of the burner combustion controller 18. 6 is controlled.

【0025】前記排ガス温度設定値は、汚染土壌に含ま
れる揮発性汚染物質の沸点温度以上であれば飛散するダ
スト中の揮発性汚染物を揮発分離または分解を進行させ
ることができる。また、沸点温度付近であれば、揮発し
た汚染物質を集塵機9にて凝固させることもない。例え
ば、灯油の沸点は180〜300℃、重油の沸点は35
0℃以上であって幅があり、また土壌中にはこれら種々
の油類が混ざりあっていることが多いので、土壌中に含
まれる主な揮発性汚染物質の沸点に着目し、排ガス温度
をその沸点以上または沸点付近にコントロールしながら
テスト運転などを行って土壌またはダストの浄化度を見
極め、これに基づいて排ガス温度設定値を適宜決定する
と良い。
If the set value of the exhaust gas temperature is equal to or higher than the boiling point of the volatile contaminants contained in the contaminated soil, the volatile contaminants in the scattered dust can be volatilized or separated. If the temperature is around the boiling point, the volatile contaminants are not solidified by the dust collector 9. For example, kerosene has a boiling point of 180 to 300 ° C, and heavy oil has a boiling point of 35.
Since there is a wide range above 0 ° C and these various oils are often mixed in the soil, the boiling point of the main volatile contaminants contained in the soil is focused on and the exhaust gas temperature is adjusted. It is preferable to determine the degree of purification of soil or dust by performing a test operation or the like while controlling the temperature at or above the boiling point, and determine the exhaust gas temperature set value appropriately based on this.

【0026】バーナ燃焼制御器18によるバーナ燃焼制
御によってロータリーキルン1出口の排ガス温度が所定
の高温に維持されると、排ガス中のダスト分に含まれる
揮発性汚染物質は揮発分離または分解されながら集塵機
9へと至り、集塵機9にて回収されるダスト分の汚染濃
度は低減される。
When the temperature of the exhaust gas at the outlet of the rotary kiln 1 is maintained at a predetermined high temperature by the burner combustion control by the burner combustion controller 18, the volatile contaminants contained in the dust in the exhaust gas are volatilized or separated while being separated. And the contamination concentration of the dust collected by the dust collector 9 is reduced.

【0027】集塵機9を通過した排ガスは脱臭炉11へ
と導入され、脱臭炉11内の高温ガスと接触してガス中
の揮発性汚染物質が完全に燃焼され、臭気やダイオキシ
ン等も分解されて無害となり、熱交換器13を通過して
煙突16より大気中に放出される。
The exhaust gas that has passed through the dust collector 9 is introduced into the deodorizing furnace 11, where it comes into contact with the high-temperature gas in the deodorizing furnace 11, whereby the volatile pollutants in the gas are completely burned, and the odor and dioxin are decomposed. It becomes harmless and is released into the atmosphere from the chimney 16 after passing through the heat exchanger 13.

【0028】また、ファン14から供給する燃焼用空気
は熱交換器13を通過する間に熱交換されて空気温度が
高められ、脱臭炉11のバーナ12に供給されて燃焼用
空気として有効使用される。なお、この熱交換器13を
通過した空気はロータリーキルン1のバーナ6に燃焼用
空気として供給しても良い。
The combustion air supplied from the fan 14 exchanges heat while passing through the heat exchanger 13 to increase the air temperature, and is supplied to the burner 12 of the deodorizing furnace 11 to be effectively used as combustion air. You. The air that has passed through the heat exchanger 13 may be supplied to the burner 6 of the rotary kiln 1 as combustion air.

【0029】集塵機9にて回収されたダストには揮発性
汚染物質がなおも残留しているが、これを浄化処理する
ために、スクリューフィーダ19によってロータリーキ
ルン1の排出ホッパ4に供給してドラム2内の高温雰囲
気に晒し、ダスト中に残留する揮発性汚染物質を更に揮
発分離または分解する。
Although the volatile contaminants still remain in the dust collected by the dust collector 9, the dust is supplied to the discharge hopper 4 of the rotary kiln 1 by a screw feeder 19 to purify the volatile contaminants. Exposed to the high-temperature atmosphere inside, and further volatile separation or decomposition of volatile contaminants remaining in the dust.

【0030】ロータリーキルン1から排出される加熱土
壌とダストは、土壌水冷装置20へと供給し、撹拌羽根
22によって混合しながら水噴射ノズル26から噴射す
る水を浴びせて湿潤、冷却し、温度を低下させると共に
含水率を高めて取り扱いやすい状態とする。このとき発
生する水蒸気は排気ダクト8に導くようにすると良い。
The heated soil and dust discharged from the rotary kiln 1 are supplied to a soil water cooling device 20, where the water is jetted from a water jet nozzle 26 while being mixed by a stirring blade 22, so that the soil is wetted and cooled to lower the temperature. And increase the water content to make it easy to handle. The water vapor generated at this time is preferably led to the exhaust duct 8.

【0031】このように、上記装置においては、並流加
熱方式の採用によってロータリーキルン1に供給される
汚染土壌が初期の加熱段階で高温の熱風と接触するため
に、汚染土壌中の微粒分がガス流に同伴して飛散する前
に汚染土壌中の揮発性汚染物質を効果的に揮発分離また
は分解することができる。また、並流加熱方式によって
排ガス温度を容易にコントロールでき、この排ガス温度
を高温に維持すると、排ガス中のダスト分が集塵機9に
至るまでの間も加熱されてダスト中の揮発性汚染物質を
揮発分離させることができると共に、揮発した汚染物質
を集塵機9内にて凝固させることもなく、ダストの汚染
濃度を低減できる。
As described above, in the above-described apparatus, since the contaminated soil supplied to the rotary kiln 1 is brought into contact with the high-temperature hot air in the initial heating stage by adopting the co-current heating method, fine particles in the contaminated soil are converted into gas. The volatile contaminants in the contaminated soil can be effectively volatilized or decomposed before being scattered in the stream. In addition, the exhaust gas temperature can be easily controlled by the co-current heating method. If the exhaust gas temperature is maintained at a high temperature, the dust in the exhaust gas is heated even before reaching the dust collector 9 to volatilize volatile pollutants in the dust. The dust can be separated, and the contaminants that have volatilized are not solidified in the dust collector 9, so that the dust contamination concentration can be reduced.

【0032】また、汚染土壌自体を沸点以上に加熱昇温
させることに拘らなくとも良いので、重油のように沸点
温度が高いものを浄化処理する場合には燃料コストを抑
えることができ、好適な装置となる。
In addition, since it is not necessary to heat the contaminated soil itself to a temperature higher than the boiling point, it is possible to suppress the fuel cost when purifying a substance having a high boiling point, such as heavy oil, so that the fuel cost can be reduced. Device.

【0033】また、集塵機9にて捕捉した高濃度の揮発
性汚染物質を含むダストをロータリーキルン1に供給し
て加熱するようにすれば、別途の加熱装置が不要とな
り、低コストにて更なるダストの浄化処理を行える。
In addition, if the dust containing high-concentration volatile contaminants captured by the dust collector 9 is supplied to the rotary kiln 1 and heated, a separate heating device becomes unnecessary, and further dust can be produced at low cost. Purification process can be performed.

【0034】なお、上記実施例の装置は揮発性汚染物質
が油類の揮発性有機化合物であることを前提とした装置
であるが、汚染物質が水銀類であるときにも適用でき、
このときには、脱臭炉11に代えて湿式洗浄機を採用し
て水銀類を回収するようにすると良い。
Although the apparatus of the above embodiment is based on the premise that the volatile contaminants are volatile organic compounds of oils, the apparatus can also be applied when the contaminants are mercury.
At this time, it is preferable to employ a wet type washer instead of the deodorizing furnace 11 to recover mercury.

【0035】[0035]

【発明の効果】以上のように本発明の請求項1記載の汚
染土壌の浄化装置によれば、汚染土壌を加熱処理するバ
ーナを備えた加熱用ロータリーキルンと、該加熱用ロー
タリーキルンから導出される排ガス中のダストを捕捉す
る集塵機を備えると共に、該加熱用ロータリーキルンの
バーナ配置側に汚染土壌を供給する土壌供給手段を配設
する一方、加熱用ロータリーキルンの排ガス排出部には
排ガス温度を検出するガス温度センサーを備え、該ガス
温度センサーにより検出した排ガス温度に基づいてバー
ナの燃焼量を制御するバーナ燃焼量制御器を備えたの
で、加熱用ロータリーキルンに供給される汚染土壌が初
期の加熱段階で高温の熱風と接触し、汚染土壌中の微粒
分がガス流に同伴して飛散する前に汚染土壌中の揮発性
汚染物質を効果的に揮発分離または分解することができ
る。また、排ガス温度を高温にコントロールすることに
よって、排ガス中のダスト分が集塵機に至るまでの間、
更に集塵機にて捕捉されている間も加熱されてダスト中
の揮発性汚染物質を揮発分離させることができると共
に、揮発した汚染物質を集塵機内にて凝固させることも
なく、集塵機にて捕捉するダストの汚染濃度を低減でき
る。
As described above, according to the apparatus for purifying contaminated soil according to the first aspect of the present invention, a heating rotary kiln having a burner for heat-treating contaminated soil, and an exhaust gas derived from the heating rotary kiln A dust collector is provided for capturing dust inside, and a soil supply means for supplying contaminated soil is disposed on the burner side of the rotary kiln for heating. On the other hand, a gas temperature for detecting exhaust gas temperature is provided at an exhaust gas discharge section of the rotary kiln for heating. A contaminated soil supplied to the heating rotary kiln is provided with a high temperature in the initial heating stage because the sensor has a burner combustion amount controller for controlling the burner combustion amount based on the exhaust gas temperature detected by the gas temperature sensor. Effectively removes volatile pollutants in contaminated soil before coming into contact with hot air and causing fines in the contaminated soil to fly away with the gas stream It can be issued separation or decomposition. In addition, by controlling the exhaust gas temperature to a high temperature, until the dust in the exhaust gas reaches the dust collector,
In addition, while being trapped by the dust collector, the dust is heated to volatilize and separate volatile contaminants in the dust, and the volatilized contaminants do not solidify in the dust collector. Contamination concentration can be reduced.

【0036】また、請求項2記載の汚染土壌の浄化装置
によれば、バーナ燃焼量制御器はガス温度センサーによ
って検出する排ガス温度が汚染土壌に含まれる揮発性汚
染物質の沸点以上となるようにバーナの燃焼量を制御す
るように構成したので、排ガスと同伴して飛散するダス
ト中の揮発性汚染物質を沸点以上の雰囲気に晒して揮発
分離を促進させることができ、また、揮発した汚染物質
を集塵機内にて凝固させることもなく、集塵機にて捕捉
するダストの汚染濃度を低減でき、汚染土壌の浄化に好
適な装置となる。
Further, according to the apparatus for purifying contaminated soil according to the second aspect, the burner combustion controller controls the exhaust gas temperature detected by the gas temperature sensor to be equal to or higher than the boiling point of volatile contaminants contained in the contaminated soil. Since the burner combustion amount is controlled, volatile pollutants in dust scattered along with exhaust gas can be exposed to an atmosphere above the boiling point to promote volatilization and separation. Is not coagulated in the dust collector, the concentration of dust trapped by the dust collector can be reduced, and the apparatus is suitable for purifying contaminated soil.

【0037】また、請求項3記載の汚染土壌の浄化装置
によれば、集塵機にて捕捉したダストを加熱用ロータリ
ーキルン内に投入して高温雰囲気に晒すように構成した
ので、別途の加熱装置がなくても集塵機にて捕捉したダ
スト中の揮発性汚染物質を加熱して汚染濃度を更に低減
できる。
According to the apparatus for purifying contaminated soil according to the third aspect of the present invention, the dust captured by the dust collector is introduced into the heating rotary kiln and exposed to a high-temperature atmosphere. Even by heating the volatile contaminants in the dust captured by the dust collector, the contamination concentration can be further reduced.

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

【図1】本発明に係る汚染土壌の浄化装置の一実施例を
示す概略説明図である。
FIG. 1 is a schematic explanatory view showing one embodiment of a device for purifying contaminated soil according to the present invention.

【符号の説明】[Explanation of symbols]

1…加熱用ロータリーキルン 2…ドラム 5…コンベヤ(土壌供給手段) 6…バーナ 9…集塵機 11…脱臭炉 17…ガス温度センサー 18…バーナ燃焼
制御器 20…土壌水冷装置
DESCRIPTION OF SYMBOLS 1 ... Rotary kiln for heating 2 ... Drum 5 ... Conveyor (soil supply means) 6 ... Burner 9 ... Dust collector 11 ... Deodorizing furnace 17 ... Gas temperature sensor 18 ... Burner combustion controller 20 ... Soil water cooling 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) F27D 17/00 105 B09B 3/00 303P 303L Fターム(参考) 2E191 BA02 BA11 BA12 BB00 BB01 BD11 BD12 4D004 AA37 AA41 AB02 AB03 AB07 CA22 CB34 CB36 DA01 DA02 DA06 DA20 4K056 AA19 BB01 CA06 CA20 DB07 DB12 DB21 4K061 AA08 BA03 DA01 FA05 FA06 GA02 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat ゛ (Reference) F27D 17/00 105 B09B 3/00 303P 303L F-term (Reference) 2E191 BA02 BA11 BA12 BB00 BB01 BD11 BD12 4D004 AA37 AA41 AB02 AB03 AB07 CA22 CB34 CB36 DA01 DA02 DA06 DA20 4K056 AA19 BB01 CA06 CA20 DB07 DB12 DB21 4K061 AA08 BA03 DA01 FA05 FA06 GA02

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】汚染土壌を加熱処理するバーナを備えた加
熱用ロータリーキルンと、該加熱用ロータリーキルンか
ら導出される排ガス中のダストを捕捉する集塵機を備え
ると共に、該加熱用ロータリーキルンのバーナ配置側に
汚染土壌を供給する土壌供給手段を配設する一方、加熱
用ロータリーキルンの排ガス排出部には排ガス温度を検
出するガス温度センサーを備え、該ガス温度センサーに
より検出した排ガス温度に基づいてバーナの燃焼量を制
御するバーナ燃焼量制御器を備えたことを特徴とする汚
染土壌の浄化装置。
1. A heating rotary kiln having a burner for heat-treating contaminated soil, a dust collector for capturing dust in exhaust gas derived from the heating rotary kiln, and contamination on a side of the heating rotary kiln where a burner is disposed. While providing soil supply means for supplying soil, the exhaust gas discharge part of the heating rotary kiln is provided with a gas temperature sensor for detecting the temperature of the exhaust gas, and the combustion amount of the burner is determined based on the exhaust gas temperature detected by the gas temperature sensor. An apparatus for purifying contaminated soil, comprising a burner combustion amount controller for controlling.
【請求項2】前記バーナ燃焼量制御器はガス温度センサ
ーによって検出する排ガス温度が汚染土壌に含まれる揮
発性汚染物質の沸点以上となるようにバーナの燃焼量を
制御するように構成したことを特徴とする請求項1記載
の汚染土壌の浄化装置。
2. The burner combustion amount controller according to claim 1, wherein the burner combustion amount is controlled so that the exhaust gas temperature detected by a gas temperature sensor is equal to or higher than the boiling point of volatile pollutants contained in the contaminated soil. The apparatus for purifying contaminated soil according to claim 1.
【請求項3】前記集塵機にて捕捉したダストを加熱用ロ
ータリーキルン内に投入して高温雰囲気に晒すように構
成したことを特徴とする請求項1又は2記載の汚染土壌
の浄化装置。
3. The apparatus for purifying contaminated soil according to claim 1, wherein the dust trapped by said dust collector is thrown into a heating rotary kiln and exposed to a high-temperature atmosphere.
JP2001064738A 2001-03-08 2001-03-08 Purification equipment for contaminated soil Expired - Fee Related JP4617010B2 (en)

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