JP4540445B2 - Soil purification equipment - Google Patents

Soil purification equipment Download PDF

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JP4540445B2
JP4540445B2 JP2004309086A JP2004309086A JP4540445B2 JP 4540445 B2 JP4540445 B2 JP 4540445B2 JP 2004309086 A JP2004309086 A JP 2004309086A JP 2004309086 A JP2004309086 A JP 2004309086A JP 4540445 B2 JP4540445 B2 JP 4540445B2
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soil
superheated steam
soil purification
contaminated
purification apparatus
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JP2006116482A (en
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道祐 佐藤
宏 中村
真紀 河口
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Toray Engineering Co Ltd
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Toyo Construction Co Ltd
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本発明は、油、有機溶剤、その他の有機化合物からなる汚染物質で汚染された汚染土壌から該汚染物質を除去して該汚染土壌を浄化する土壌浄化装置に関する。   The present invention relates to a soil purification apparatus that removes contaminants from contaminated soil contaminated with contaminants composed of oil, organic solvents, and other organic compounds to purify the contaminated soil.

例えば、工場の跡地、ガソリンスタンドの跡地等は種々の油や有機溶剤等の汚染物質で汚染されている場合が多く、そのまま放置しておくと地下水を汚染したり、地表から拡散して地域住民の健康を害する虞があるので、土地の所有者は社会的又は法的責任から汚染物質を除去する必要に迫られている。   For example, factory sites, gas station sites, etc. are often contaminated with various pollutants such as oil and organic solvents. Land owners are being forced to remove contaminants from their social or legal responsibilities as they may harm the health of the community.

汚染物質で汚染されている土地から汚染物質を除去する方法としては、その土地の土壌を水流及び混気ジェット水にて洗浄することにより土壌中の汚染物質を分離除去する方法、土壌中の汚染物質を吸着剤により吸着除去させる方法、土壌をロータリーキルンにより焼却して汚染物質を燃焼除去させる方法、土壌中の汚染物質を微生物により分解除去させる方法(バイオレミディエーション)等が知られている。
特開2003−94038号公報
Contaminants can be removed from soil contaminated with pollutants by separating and removing soil contaminants by washing the soil with water flow and mixed jet water. There are known a method of adsorbing and removing substances with an adsorbent, a method of incinerating soil with a rotary kiln to burn and remove pollutants, a method of decomposing and removing pollutants in soil with microorganisms (bioremediation), and the like.
JP 2003-94038 A

しかし、汚染土壌を水流及び混気ジェット水にて洗浄することにより土壌中の汚染物質を分離除去する方法では、粒径の小さな土砂に付着した有機化合物を除去することができないので、粒径の小さな土砂を回収して焼却及び固化処理し、管理型埋立て地処分をしなければならないし、また、汚染土壌を洗浄するのに使用した水の排水処理をしなければならないという問題がある。   However, the method of separating and removing contaminants in the soil by washing the contaminated soil with a water stream and mixed-air jet water cannot remove organic compounds adhering to the soil with a small particle size. There is a problem that small sediment must be collected, incinerated and solidified, disposed of in a managed landfill, and drained from the water used to clean the contaminated soil.

また、土壌中の汚染物質を吸着剤により吸着除去させる方法では、汚染物質を吸着させた吸着剤を焼却するか、最終処分場に埋め立て処分しなければならなし、しかも、吸着剤等の残留による二次汚染の虞があるという問題がある。   Also, in the method of adsorbing and removing pollutants in the soil with the adsorbent, the adsorbent that has adsorbed the pollutant must be incinerated or disposed of in the final disposal site, and also due to residual adsorbent etc. There is a problem that there is a risk of secondary contamination.

また、汚染物質を含む土壌をロータリーキルンにより焼却して汚染物質を燃焼除去させる方法では、ダイオキシン等の有害物質が発生する虞があり、しかも、焼却のために多量の熱エネルギーが必要となるし、ロータリーキルンという大規模な設備が必要になるという問題もある。   In addition, the method of incinerating soil containing pollutants with a rotary kiln to remove the pollutants by burning may cause harmful substances such as dioxins, and a large amount of heat energy is required for incineration. There is also a problem that a large-scale facility called a rotary kiln is required.

また、土壌中の汚染物質を微生物により分解除去させる方法では、微生物の土中への注入方法及び活性化方法が必要となるし、汚染物質の分解に時間を要し、しかも高濃度の汚染には対応出来ないという問題がある。   In addition, the method of decomposing and removing contaminants in the soil with microorganisms requires a method of injecting microorganisms into the soil and an activation method, and it takes time to decompose the contaminants, and also to a high concentration of contamination. There is a problem that can not cope.

本発明はこのような問題を解決するものであって、有害物質で汚染された土地の土壌を、現位置において、効率良く、確実に浄化することができる土壌浄化装置を提供することを目的とする。   This invention solves such a problem, and it aims at providing the soil purification apparatus which can clean the soil of the land contaminated with the harmful substance efficiently and reliably in the present position. To do.

本発明に係る土壌浄化装置は、汚染物質を含む汚染土壌を供給する土壌供給装置と、過熱水蒸気を生成して供給する過熱水蒸気生成供給装置と、該土壌供給装置から供給された該汚染土壌を該過熱水蒸気生成供給装置から供給された過熱水蒸気に曝して、汚染土壌中に含まれていた汚染物質を過熱水蒸気中に移動させる土壌浄化炉と、該土壌浄化炉から排出された過熱水蒸気を冷却して該過熱水蒸気から汚染物質を分離させる汚染物質分離装置とを備えていることを特徴とするものである。   A soil purification apparatus according to the present invention includes a soil supply device that supplies contaminated soil containing a pollutant, a superheated steam generation and supply device that generates and supplies superheated steam, and the contaminated soil that is supplied from the soil supply device. A soil purification furnace that exposes the superheated steam supplied from the superheated steam generation and supply device to move pollutants contained in the contaminated soil into the superheated steam, and cools the superheated steam discharged from the soil purification furnace. And a contaminant separator for separating contaminants from the superheated steam.

ここで、前記土壌浄化炉は、密閉されている縦型炉と、該縦型炉を貫通して略垂直に設けられている過熱水蒸気排出筒と、該縦型炉内の該過熱水蒸気排出筒の周囲にスパイラル状に設けられている流動炉床と、該流動炉床上に前記汚染土壌を供給する土壌供給装置と、該流動炉床上の該汚染土壌に過熱水蒸気を吹き付ける過熱水蒸気吹付手段と、前記流動炉床に振動を与える振動装置とで構成してもよい。   Here, the soil purification furnace includes a sealed vertical furnace, a superheated steam discharge tube provided substantially vertically through the vertical furnace, and the superheated steam discharge tube in the vertical furnace. A fluidized hearth provided in a spiral around the ground, a soil supply device for supplying the contaminated soil on the fluidized hearth, superheated steam spraying means for spraying superheated steam on the contaminated soil on the fluidized hearth, You may comprise with the vibration apparatus which gives a vibration to the said fluid hearth.

この場合、該過熱水蒸気排出筒には複数の貫通穴を設けて該過熱水蒸気排出筒内と該縦型炉内とを連通させ、該土壌投入装置は該縦型炉の上部に設け、該過熱水蒸気排出筒は前記汚染物質分離装置に連結し、該過熱水蒸気吹付手段は前記過熱水蒸気供給装置に連結することになる。   In this case, the superheated steam discharge cylinder is provided with a plurality of through holes to communicate the superheated steam discharge cylinder with the vertical furnace, and the soil charging device is provided at the top of the vertical furnace. The water vapor discharge cylinder is connected to the pollutant separation device, and the superheated steam spraying means is connected to the superheated steam supply device.

また、前記縦型炉は、上段のプレヒート部と、該プレヒート部の下部に連結部を介して連結されている本吹部とにより構成し、該連結部には汚染土壌を破砕する破砕装置を設けるようにしてもよい。   The vertical furnace is composed of an upper preheating part and a main blowing part connected to the lower part of the preheating part via a connecting part, and a crushing device for crushing contaminated soil is connected to the connecting part. You may make it provide.

また、前記流動炉床を、略リング状の仕切壁によって外側の領域と内側の領域に区画し、最下段の流動炉床の外側の領域と最上段の流動炉床の内側の領域をつなぐバケットコンベアを設けるようにしてもよい。   Further, the fluidized hearth is partitioned into an outer region and an inner region by a substantially ring-shaped partition wall, and a bucket that connects an outer region of the lowermost fluid hearth and an inner region of the uppermost fluidized hearth. A conveyor may be provided.

また、前記過熱水蒸気供給装置は、水蒸気を生成させる水蒸気生成装置と、該水蒸気生成装置によって生成された水蒸気を加熱して過熱水蒸気を生成する水蒸気過熱装置とで構成してもよい。また、この土壌浄化装置には、前記汚染物質分離装置において汚染物質が分離・除去された水蒸気を前記水蒸気過熱装置に導く水蒸気戻し機構を設けてもよい。   In addition, the superheated steam supply device may be constituted by a steam generating device that generates steam and a steam superheating device that generates superheated steam by heating the steam generated by the steam generating device. In addition, the soil purification apparatus may be provided with a water vapor return mechanism that guides the water vapor from which the pollutants have been separated and removed in the pollutant separation apparatus to the water vapor superheater.

また、この土壌浄化装置には、前記汚染土壌を掘削する掘削装置を設けてもよいし、この土壌浄化装置をトレーラーのような移動手段の上に設けて装置全体を任意の場所に自由に移動できるようにしてもよい。   The soil purification apparatus may be provided with a drilling device for excavating the contaminated soil, or the soil purification apparatus is provided on a moving means such as a trailer so that the entire apparatus can be freely moved to an arbitrary place. You may be able to do it.

また、前記汚染物質分離装置は、前記過熱水蒸気を段階的に冷却し、該過熱水蒸気から汚染物質を成分別に分離する機構にしてもよいし、前記汚染物質分離装置で回収される余熱を前記各装置又は該各装置をつなぐ配管の保温に利用する余熱利用機構を設けてもよい。   Further, the pollutant separation device may be a mechanism for cooling the superheated steam stepwise to separate the pollutants from the superheated steam by component, and the residual heat recovered by the pollutant separation device may be You may provide the residual heat utilization mechanism utilized for the heat insulation of the apparatus or piping which connects this apparatus.

この発明は、汚染現場に運んで設置することができる程度の大きさに土壌浄化装置を作ることができるので、汚染土壌を処理工場まで運ぶような余分なコストをかけることなく汚染現場で汚染土壌の浄化処理することができ、従って、汚染土壌を低コストで浄化処理することができるという効果がある。   Since the present invention can make the soil purification device large enough to be carried and installed at the contaminated site, the contaminated soil at the contaminated site without incurring the extra cost of transporting the contaminated soil to the treatment plant. Therefore, there is an effect that the contaminated soil can be purified at a low cost.

また、この発明は、汚染土壌を汚染現場で浄化処理し、浄化処理した土壌を汚染現場に戻すので、汚染現場に別の土壌を運んで来る場合に生ずる余分なコストをかけなくて済み、従って、汚染現場を低コストで修復することができるという効果がある。   In addition, the present invention purifies the contaminated soil at the contaminated site and returns the purified soil to the contaminated site, so that it is not necessary to incur an extra cost incurred when bringing another soil to the contaminated site. There is an effect that the contaminated site can be repaired at low cost.

また、この発明は、過熱水蒸気は冷却されると水になり、過熱水蒸気中の汚染物質(油分や有機溶媒)は水とは親和性がなく水から容易に分離するので、過熱水蒸気中から汚染物質を濃縮した状態で容易に分離・回収することができ、従って、汚染物質のその後の処理や利用が容易になるという効果がある。   Further, according to the present invention, when the superheated steam is cooled, it becomes water, and the contaminants (oil and organic solvent) in the superheated steam have no affinity for water and are easily separated from the water. The substance can be easily separated and collected in a concentrated state, and therefore, there is an effect that the subsequent treatment and utilization of the pollutant becomes easy.

また、この発明は、処理装置から抜き出した過熱水蒸気の温度を段階的に下げて冷却して行けば、汚染物質を成分毎に分離・回収し、その後の処理や利用を更に容易ならしめるという効果がある。   In addition, the present invention has an effect of separating and recovering pollutants for each component and further facilitating the subsequent processing and utilization if the temperature of the superheated steam extracted from the processing apparatus is lowered and cooled in stages. There is.

また、この発明は、汚染土壌に過熱水蒸気を非酸化性雰囲気中又は低酸素雰囲気中で触れさせれば、発火が無く、酸化反応をほとんど起こさず、ダイオキシン等の有害物質の発生を抑制した状態で、汚染土壌から汚染物質を分離・除去することができるという効果がある。   In addition, in the present invention, if superheated steam is brought into contact with contaminated soil in a non-oxidizing atmosphere or a low-oxygen atmosphere, there is no ignition, little oxidation reaction occurs, and generation of harmful substances such as dioxin is suppressed. Thus, it is possible to separate and remove pollutants from the contaminated soil.

また、この発明は、熱量を多量に保有している過熱水蒸気を使用するので、汚染土壌を効率良く浄化処理することができ、従って、コンパクトな設備で汚染土壌を短時間に浄化処理することができるという効果がある。   In addition, since the present invention uses superheated steam having a large amount of heat, the contaminated soil can be efficiently purified, and therefore the contaminated soil can be purified in a short time with a compact facility. There is an effect that can be done.

また、この発明は、特殊な化学薬剤や微生物を用いないので、土壌を二次汚染させるおそれがなく、安全性が高く、従って、汚染土壌を安心して浄化処理することができるという効果がある。   In addition, since the present invention does not use a special chemical agent or microorganism, there is no risk of secondary contamination of the soil, and the safety is high. Therefore, there is an effect that the contaminated soil can be purified without anxiety.

また、この発明は、汚染土壌を水で洗う場合のように排水が出ないので、排水処理の必要がなく、従って、土壌を浄化するための設備をコンパクトにすることができるという効果がある。   Moreover, since this invention does not discharge | emit drainage like the case where contaminated soil is washed with water, there is no need for wastewater treatment, and therefore there is an effect that the equipment for purifying the soil can be made compact.

また、この発明は、有害成分を吸着した吸着剤を焼却したり、最終処分場で処分する必要がないし、吸着剤等の残留(二次汚染)を心配しなくて済むという効果がある。   In addition, the present invention has the effect that it is not necessary to incinerate the adsorbent adsorbing harmful components or dispose of it at the final disposal site, and there is no need to worry about residual adsorbent (secondary contamination).

また、この発明は、汚染土壌を浄化処理する際にダイオキシン等の有害物質を大気中に発生させないので、汚染土壌の有る周囲に危険を及ぼすことなく、汚染土壌を安全に処理することができるという効果がある。   Moreover, since this invention does not generate | occur | produce harmful substances, such as dioxin, in air | atmosphere at the time of purification processing of contaminated soil, it can safely process contaminated soil, without giving danger to the surrounding with contaminated soil. effective.

また、この発明は、土壌を浄化するのに使用した水蒸気を再利用するので、水処理のような手間をかけなくて済み、しかもボイラーで作る水蒸気の量も少なくできるという効果がある。   In addition, since the present invention reuses the water vapor used to purify the soil, there is an effect that it is not necessary to take time and effort like water treatment, and the amount of water vapor produced by the boiler can be reduced.

図1はこの発明の一実施の形態に係る土壌浄化装置の概念図、図2はこの発明の一実施の形態に係る土壌浄化装置の土壌浄化炉(浄化土砂内部貯留時)の説明図、図3は図2のA部拡大図、図4はこの発明の一実施の形態に係る土壌浄化装置の土壌浄化炉(浄化土砂外部排出時)の説明図、図5はこの発明の他の実施の形態に係る土壌浄化装置の土壌浄化炉の説明図、図6は実機の土壌浄化装置の平面配置を示す説明図、図7は実機の土壌浄化装置の側面配置を示す説明図である。   FIG. 1 is a conceptual diagram of a soil purification apparatus according to an embodiment of the present invention, and FIG. 2 is an explanatory diagram and a diagram of a soil purification furnace (at the time of internal storage of the purified soil) of the soil purification apparatus according to an embodiment of the present invention. 3 is an enlarged view of part A of FIG. 2, FIG. 4 is an explanatory view of a soil purification furnace (at the time of external discharge of the purified soil) of the soil purification apparatus according to one embodiment of the present invention, and FIG. 5 is another embodiment of the present invention. FIG. 6 is an explanatory view showing a planar arrangement of the actual soil purification apparatus, and FIG. 7 is an explanatory view showing a side arrangement of the actual soil purification apparatus.

これらの図において、10は縦型の土壌浄化炉であり、土壌浄化炉10は、上段のプレヒート部12と、下段の本吹部14と、プレヒート部12及び本吹部14を連結・連通させている連結部16とからなる。   In these drawings, reference numeral 10 denotes a vertical soil purification furnace. The soil purification furnace 10 connects and communicates an upper preheating section 12, a lower main blowing section 14, a preheating section 12 and a main blowing section 14. Connecting portion 16.

プレヒート部12及び本吹部14の内部空間には、例えば0.2mmメッシュ程度の金網からなる流動炉床18がスパイラル状に設けられ、流動炉床18の上面は傾斜している。流動炉床18には蒸気吐出管20が配設され、過熱水蒸気が下方に向けて吐出するような構造になっている。また、流動炉床18は図示しない振動装置によって微振動をするようになっている。   In the internal space of the preheating part 12 and the main blowing part 14, a fluidized hearth 18 made of, for example, a wire mesh of about 0.2 mm mesh is provided in a spiral shape, and the upper surface of the fluidized hearth 18 is inclined. A steam discharge pipe 20 is disposed on the fluidized hearth 18 so that superheated steam is discharged downward. The fluidized hearth 18 is vibrated slightly by a vibration device (not shown).

流動炉床18の中心には過熱水蒸気排出筒22がプレヒート部12及び本吹部14を貫通・連結するようにして立設されている。プレヒート部12の内部空間及び本吹部14の内部空間は過熱水蒸気排出筒22の内部空間と連通している。過熱水蒸気排出筒22の下端部は閉塞され、過熱水蒸気排出筒22の上端部には過熱水蒸気排出管24が設けられている。   In the center of the fluidized hearth 18, a superheated steam discharge cylinder 22 is erected so as to penetrate and connect the preheating part 12 and the main blowing part 14. The internal space of the preheating unit 12 and the internal space of the main blowing unit 14 communicate with the internal space of the superheated steam discharge cylinder 22. The lower end portion of the superheated steam discharge tube 22 is closed, and the superheated steam discharge tube 24 is provided with the upper end portion of the superheated steam discharge tube 22.

プレヒート部12の上部には土壌供給装置である土壌ホッパー26が設けられ、土壌ホッパー26とプレヒート部12の間には連続供給装置30が設けられ、土壌ホッパー26に入れられた汚染土壌28がプレヒート部12の内部、流動炉床18の上に連続的に供給されるようになっている。   A soil hopper 26, which is a soil supply device, is provided above the preheating unit 12, and a continuous supply device 30 is provided between the soil hopper 26 and the preheating unit 12, and the contaminated soil 28 placed in the soil hopper 26 is preheated. The inside of the section 12 is continuously supplied onto the fluidized hearth 18.

連結部16の内部には汚染土壌を破砕する破砕装置32が設けられている。プレヒート部12で浄化された汚染土壌28は破砕装置32で破砕され、破砕された汚染土壌28は本吹部14の内部、流動炉床18の上に供給されるようになっている。   A crushing device 32 for crushing contaminated soil is provided inside the connecting portion 16. The contaminated soil 28 purified by the preheating unit 12 is crushed by the crushing device 32, and the crushed contaminated soil 28 is supplied to the inside of the main blowing unit 14 and onto the fluidized hearth 18.

本吹部14の底部には過熱水蒸気によって浄化された土壌を貯留するための貯留タンク34が設けられ、本吹部14と貯留タンク34との間には開閉蓋36が開閉可能に設けられ、貯留タンク34の底部は浄化土壌排出口35になっており、浄化土壌排出口35には排出蓋38が開閉可能に設けられている。   A storage tank 34 for storing soil purified by superheated steam is provided at the bottom of the main blowing unit 14, and an open / close lid 36 is provided between the main blowing unit 14 and the storage tank 34 so as to be openable and closable. The bottom of the storage tank 34 is a purified soil discharge port 35, and a discharge lid 38 is provided at the purified soil discharge port 35 so as to be openable and closable.

流動炉床18に設けられた蒸気吐出管20は過熱水蒸気供給管42を介して水蒸気加熱装置である過熱器40に接続されている。また、過熱水蒸気排出筒22の上部は水蒸気戻し機構である過熱水蒸気排出管24及び水蒸気回収管44を介して汚染物質分離装置48に接続されている。   The steam discharge pipe 20 provided on the fluidized hearth 18 is connected to a superheater 40 which is a steam heating device via a superheated steam supply pipe 42. Further, the upper portion of the superheated steam discharge cylinder 22 is connected to a pollutant separation device 48 via a superheated steam discharge pipe 24 and a steam recovery pipe 44 which are steam return mechanisms.

過熱器40はボイラー46に接続され、ボイラー46から過熱器40に水蒸気が供給されるようになっている。ボイラー46には水タンク50が接続され、水タンク50からボイラー46に水が供給されるようになっている。   The superheater 40 is connected to a boiler 46 so that steam is supplied from the boiler 46 to the superheater 40. A water tank 50 is connected to the boiler 46, and water is supplied from the water tank 50 to the boiler 46.

汚染物質分離装置48は過熱水蒸気の温度を下げて100℃の水蒸気と汚染物質とに分離させるようになっており、汚染物質を除去された水蒸気は過熱器40に戻されるようになっており、分離された汚染物質は隣接して設けられた貯油タンク52に貯留されるようになっている。   The pollutant separation device 48 is configured to lower the temperature of the superheated steam to separate the steam at 100 ° C. and the pollutant, and the steam from which the pollutant has been removed is returned to the superheater 40. The separated contaminants are stored in an oil storage tank 52 provided adjacent thereto.

汚染物質分離装置48には余熱回収装置54が設けられ、余熱回収装置54は汚染物質分離装置48から出てくる余熱を回収して前記各装置又は該各装置をつなぐ配管の保温に利用するように構成されている。   The pollutant separation device 48 is provided with a residual heat recovery device 54. The residual heat recovery device 54 recovers the residual heat emitted from the pollutant separation device 48 and uses it to keep the devices or pipes connecting the devices together. It is configured.

これらの各装置や配管はトレーラー56の上に設置され、汚染土壌の有る場所まで自力で移動又は走行し、その場所で汚染土壌の浄化処理ができるようになっている。   Each of these devices and pipes is installed on a trailer 56, and moves or travels by itself to a place where contaminated soil is present, and the contaminated soil can be purified at that place.

次に、本発明に係る土壌浄化装置の動作について説明する。   Next, the operation of the soil purification apparatus according to the present invention will be described.

まず、本発明に係る土壌浄化装置を汚染物質で汚染された場所までトレーラー56で搬送させるか、自走装置を備えている場合は自走させ、汚染物質で汚染された場所の適宜位置に止め、その位置に設置・固定する。   First, the soil purification apparatus according to the present invention is transported by a trailer 56 to a place contaminated with a pollutant or, if equipped with a self-propelled apparatus, is self-propelled and stopped at an appropriate position in a place contaminated with a pollutant. Install and fix in that position.

次に、ボイラー46及び過熱器40の運転を始める。水タンク50から供給された水はボイラー46で加熱されて100℃の水蒸気となり、過熱器40で更に加熱されて500℃の過熱水蒸気となる。過熱水蒸気は過熱水蒸気供給管42を介して土壌浄化炉10に供給され、蒸気吐出管20から流動炉床18に向けて連続的に吐出する。   Next, the operation of the boiler 46 and the superheater 40 is started. The water supplied from the water tank 50 is heated by the boiler 46 to become 100 ° C. steam, and further heated by the superheater 40 to become 500 ° C. superheated steam. The superheated steam is supplied to the soil purification furnace 10 through the superheated steam supply pipe 42 and is continuously discharged from the steam discharge pipe 20 toward the fluidized hearth 18.

次に、汚染物質を含む土壌を掘削装置(図示せず)で掘削して堀取り、堀取った汚染土壌28を土壌ホッパー26の中に順次投入する。土壌ホッパー26の中に投入された汚染土壌28は連続供給装置30によってプレヒート部12の流動炉床18の上に供給される。   Next, the soil containing the pollutant is excavated by a drilling device (not shown), and the excavated contaminated soil 28 is sequentially put into the soil hopper 26. The contaminated soil 28 introduced into the soil hopper 26 is supplied onto the fluidized hearth 18 of the preheating unit 12 by the continuous supply device 30.

流動炉床18は傾斜し、且つ図示しない振動装置によって振動しているので、流動炉床18上の汚染土壌28は移動しながらプレヒート部12の中を低い方へ順次下がって行く。   Since the fluidized hearth 18 is inclined and vibrated by a vibration device (not shown), the contaminated soil 28 on the fluidized hearth 18 moves down in the preheating portion 12 while moving.

流動炉床18には蒸気吐出管20から過熱水蒸気が吐出しており、過熱水蒸気は流動炉床18の上を移動しながら順次下がって行く汚染土壌28に吹き付けられる。汚染土壌28の表面は過熱水蒸気の熱を貰って高熱になり、汚染土壌28の表面に付着していた汚染物質は気化して過熱水蒸気中に混入し、汚染物質を混入させた過熱水蒸気はプレヒート部12から過熱水蒸気排出筒22に入る。   The superheated steam is discharged from the steam discharge pipe 20 to the fluidized hearth 18, and the superheated steam is sprayed onto the contaminated soil 28 that is gradually lowered while moving on the fluidized hearth 18. The surface of the contaminated soil 28 becomes hot due to the heat of the superheated steam, and the contaminant adhering to the surface of the contaminated soil 28 is vaporized and mixed in the superheated steam, and the superheated steam mixed with the contaminant is preheated. The superheated steam discharge cylinder 22 is entered from the section 12.

プレヒート部12の内部の流動炉床18を移動し終わった汚染土壌28はプレヒート部12の底部から連結部16に入り、破砕装置32で破砕されて細かくなるとともに、内部を露出させられ、本吹部14の内部の流動炉床18の上に供給される。   The contaminated soil 28 that has finished moving through the fluidized hearth 18 inside the preheating section 12 enters the connecting section 16 from the bottom of the preheating section 12 and is crushed by the crushing device 32 to become fine, and the inside is exposed, and the main blow It is supplied on a fluidized hearth 18 inside the section 14.

本吹部14の中の流動炉床18も図示しない振動装置によって振動しており、汚染土壌28は流動炉床18の上を移動しながら本吹部14の中を順次下がって行く。汚染土壌28は流動炉床18の上で過熱水蒸気によって更に加熱され、露出させられた内部に付着していた汚染物質は気化して過熱水蒸気中に混入し、汚染物質を混入させた過熱水蒸気は本吹部14から過熱水蒸気排出筒22に入る。   The fluidized hearth 18 in the main blowing unit 14 is also vibrated by a vibration device (not shown), and the contaminated soil 28 sequentially moves down the main blowing unit 14 while moving on the fluidized hearth 18. The contaminated soil 28 is further heated by the superheated steam on the fluidized hearth 18, the pollutant adhering to the exposed interior is vaporized and mixed into the superheated steam, and the superheated steam mixed with the pollutant is The superheated steam discharge cylinder 22 is entered from the main blowing section 14.

本吹部14内の流動炉床18を移動し終わった汚染土壌は本吹部14の底部に溜まる。適当な量の浄化土壌が溜まったところで、開閉蓋36を開けると浄化土壌は貯留タンク34に入る。   The contaminated soil that has finished moving through the fluidized hearth 18 in the main blowing section 14 is accumulated at the bottom of the main blowing section 14. When an appropriate amount of purified soil is collected, the purified soil enters the storage tank 34 when the opening / closing lid 36 is opened.

適当な時期及び場所において、排出蓋38を開くと、貯留タンク34内の浄化土壌は排出され、汚染土壌を堀取った元の場所に浄化土壌が埋め戻され、汚染土壌の浄化処理が完了する。開閉蓋36でなく、連続排出装置を使用してもよい。   When the discharge lid 38 is opened at an appropriate time and place, the purified soil in the storage tank 34 is discharged, the purified soil is backfilled in the original place where the contaminated soil was dug, and the contaminated soil purification process is completed. . Instead of the opening / closing lid 36, a continuous discharge device may be used.

過熱水蒸気排出筒22に入った過熱水蒸気は水蒸気回収管44を通って汚染物質分離装置48に入り、汚染物質分離装置48で100℃まで冷却され、汚染物質である油等を析出させ、100℃の水蒸気は過熱器40に送られる。回収された油等は適宜、貯油タンク52に送られて貯留される。   The superheated steam that has entered the superheated steam discharge cylinder 22 enters the pollutant separation device 48 through the steam recovery pipe 44, is cooled to 100 ° C. by the pollutant separation device 48, and precipitates oil or the like that is a pollutant. The steam is sent to the superheater 40. The recovered oil or the like is appropriately sent to the oil storage tank 52 for storage.

なお、この発明の実施の形態に係る土壌浄化装置の土壌浄化炉10は上述した通りであるが、土壌浄化炉10は上述の構造のものに限られず、図4に示すような別の構造のものを採用してもよい。   In addition, although the soil purification furnace 10 of the soil purification apparatus which concerns on embodiment of this invention is as above-mentioned, the soil purification furnace 10 is not restricted to the thing of the above-mentioned structure, Another structure as shown in FIG. A thing may be adopted.

すなわち、この別の構造の土壌浄化炉10は、基本的な構造は上述した土壌浄化炉10と略同じであるが、炉が1段で構成され、土壌浄化炉10の外側にはバケットコンベア58が設けられ、流動炉床18はリング状の仕切壁60によって外側の領域62と内側の領域64に区画されている点が相違している。   That is, the soil purification furnace 10 having another structure is basically the same as the soil purification furnace 10 described above, but the furnace is configured in one stage, and a bucket conveyor 58 is provided outside the soil purification furnace 10. The flow hearth 18 is different in that it is divided into an outer region 62 and an inner region 64 by a ring-shaped partition wall 60.

この土壌浄化炉10における汚染土壌28の動きは、後述するように、上述した土壌浄化炉10における汚染土壌28の動きとは若干相違している。   The movement of the contaminated soil 28 in the soil purification furnace 10 is slightly different from the movement of the contaminated soil 28 in the soil purification furnace 10 described above, as will be described later.

すなわち、土壌ホッパー26の中に投入された汚染土壌28は連続供給装置30によって流動炉床18の最上段に供給され、過熱水蒸気によって浄化されながら流動炉床18の外側の領域62に徐々に移動して行く。   That is, the contaminated soil 28 introduced into the soil hopper 26 is supplied to the uppermost stage of the fluidized hearth 18 by the continuous supply device 30 and gradually moves to the region 62 outside the fluidized hearth 18 while being purified by superheated steam. Go.

流動炉床18の外側の領域62に移動した汚染土壌28は過熱水蒸気によって浄化されながら、流動炉床18の外側の領域62を流動し、下降して行く。流動炉床18の最下段に到達した汚染土壌28はバケットコンベア58によって流動炉床18の上段まで掻き揚げられ、流動炉床18の内側の領域64に供給される。   The contaminated soil 28 that has moved to the region 62 outside the fluidized hearth 18 flows through the region 62 outside the fluidized hearth 18 and descends while being purified by superheated steam. The contaminated soil 28 that has reached the lowest level of the fluidized hearth 18 is scraped up to the upper level of the fluidized hearth 18 by the bucket conveyor 58 and supplied to the region 64 inside the fluidized hearth 18.

流動炉床18の内側の領域64に供給された汚染土壌28は過熱水蒸気によって更に浄化されながら、流動炉床18の内側の領域64を流動し、下降して行く。土壌浄化炉10の底まで到達した汚染土壌28は貯留タンク34に貯留される。   The contaminated soil 28 supplied to the region 64 inside the fluidized hearth 18 flows and descends in the region 64 inside the fluidized hearth 18 while being further purified by superheated steam. Contaminated soil 28 reaching the bottom of the soil purification furnace 10 is stored in a storage tank 34.

まず、油等で汚染されていない乾燥した土壌と、成分組成の分かっている廃潤滑油を準備し、土壌100重量部に対して2重量部の廃潤滑油を混ぜ、充分に混合して汚染土壌を人工的に作った。   First, prepare dry soil that is not contaminated with oil, etc. and waste lubricating oil with a known component composition, mix 2 parts by weight of waste lubricating oil with 100 parts by weight of soil, and mix thoroughly to contaminate Soil was made artificially.

次に、この汚染土壌を浄化装置に入れ、500℃の常圧過熱水蒸気を5分間吹き付け、この汚染土壌を取り出して粉砕し、浄化装置に戻して再び500℃の過熱水蒸気を10分間吹き付けた。   Next, this contaminated soil was put into a purification device, sprayed with 500 ° C. atmospheric superheated steam for 5 minutes, taken out of this contaminated soil and ground, returned to the purification device, and again sprayed with 500 ° C. superheated steam for 10 minutes.

以上の浄化処理をした土壌を分析し、廃潤滑油の有無を調べたところ、廃潤滑油は検出されなかった。   The soil subjected to the above purification treatment was analyzed and examined for the presence of waste lubricant. As a result, no waste lubricant was detected.

また、以上の浄化処理で使用した過熱水蒸気を冷却して得られた液体を放置したところ、上層が油、下層が水となった。そして、上層の油の成分を分析したところ、廃潤滑油と略同じ成分であった。また、油及び水にダイオキシンは含まれていなかった。   Further, when the liquid obtained by cooling the superheated steam used in the above purification treatment was allowed to stand, the upper layer became oil and the lower layer became water. And when the component of the oil of the upper layer was analyzed, it was a component substantially the same as a waste lubricating oil. Moreover, dioxin was not contained in oil and water.

なお、廃潤滑油の代わりにトリクロロエチレンを使用して上記と同様の実験をしたところ、廃潤滑油の場合とほぼ同様の結果が得られた。   In addition, when an experiment similar to the above was performed using trichlorethylene instead of the waste lubricant, a result almost the same as that of the waste lubricant was obtained.

この発明は陸上の油汚染土壌、海洋の油汚染土及び底泥、閉鎖性水域における油汚染底泥、油以外の有機化合物で汚染された土砂全般の浄化に適用できる。   The present invention can be applied to the purification of terrestrial oil-contaminated soil, marine oil-contaminated soil and bottom mud, oil-contaminated bottom mud in closed waters, and general soil contaminated with organic compounds other than oil.

この発明の一実施の形態に係る土壌浄化装置の概念図である。It is a conceptual diagram of the soil purification apparatus which concerns on one embodiment of this invention. この発明の一実施の形態に係る土壌浄化装置の土壌浄化炉(浄化土砂内部貯留時)の説明図である。It is explanatory drawing of the soil purification furnace (at the time of internal storage of purification soil) of the soil purification apparatus which concerns on one embodiment of this invention. 図2のA部拡大図である。It is the A section enlarged view of FIG. この発明の一実施の形態に係る土壌浄化装置の土壌浄化炉(浄化土砂外部排出時)の説明図である。It is explanatory drawing of the soil purification furnace (at the time of external discharge | emission of purification soil) of the soil purification apparatus which concerns on one embodiment of this invention. この発明の他の実施の形態に係る土壌浄化装置の土壌浄化炉の説明図である。It is explanatory drawing of the soil purification furnace of the soil purification apparatus which concerns on other embodiment of this invention. 実機の土壌浄化装置の平面配置を示す説明図である。It is explanatory drawing which shows the planar arrangement | positioning of the actual soil purification apparatus. 実機の土壌浄化装置の側面配置を示す説明図である。It is explanatory drawing which shows the side surface arrangement | positioning of the actual soil purification apparatus.

符号の説明Explanation of symbols

10 土壌浄化炉
12 プレヒート部
14 本吹部
16 連結部
18 流動炉床
20 蒸気吐出管
22 過熱水蒸気排出筒
24 過熱水蒸気排出管
26 土壌ホッパー
28 汚染土壌
30 連続供給装置
32 破砕装置
34 貯留タンク
36 開閉蓋
38 排出蓋
40 過熱器
42 過熱水蒸気供給管
44 水蒸気回収管
46 ボイラー
48 汚染物質分離装置
50 水タンク
52 貯油タンク
54 余熱回収装置
56 トレーラー
58 バケットコンベア
60 仕切壁
62 領域
64 領域
DESCRIPTION OF SYMBOLS 10 Soil purification furnace 12 Preheating part 14 Main blowing part 16 Connection part 18 Fluidized hearth 20 Steam discharge pipe 22 Superheated steam discharge pipe 24 Superheated steam discharge pipe 26 Soil hopper 28 Contaminated soil 30 Continuous supply apparatus 32 Crushing apparatus 34 Storage tank 36 Opening and closing Lid 38 Discharge lid 40 Superheater 42 Superheated steam supply pipe 44 Steam recovery pipe 46 Boiler 48 Contaminant separation device 50 Water tank 52 Oil storage tank 54 Residual heat recovery device 56 Trailer 58 Bucket conveyor 60 Partition wall 62 Area 64 Area

Claims (9)

汚染物質を含む土壌(以下、「汚染土壌」という。)を供給する土壌供給装置と、過熱水蒸気を生成して供給する過熱水蒸気生成供給装置と、該土壌供給装置から供給された該汚染土壌を該過熱水蒸気生成供給装置から供給された過熱水蒸気に曝して、該汚染土壌中に含まれていた汚染物質を過熱水蒸気中に移動させる土壌浄化炉と、該土壌浄化炉から排出された過熱水蒸気を冷却して該過熱水蒸気から汚染物質を分離させる汚染物質分離装置とを備え、前記土壌浄化炉が、密閉されている縦型炉と、該縦型炉を貫通して略垂直に設けられている過熱水蒸気排出筒と、該縦型炉内の該過熱水蒸気排出筒の周囲にスパイラル状に設けられている流動炉床と、該流動炉床上に前記汚染土壌を供給する土壌供給装置と、該流動炉床上の該汚染土壌に過熱水蒸気を吹き付ける過熱水蒸気吹付手段と、前記流動炉床に振動を与える振動装置とを備え、該過熱水蒸気排出筒は複数の貫通穴を備えて該過熱水蒸気排出筒内と該縦型炉内は連通し、該土壌投入装置は該縦型炉の上部に設けられ、該過熱水蒸気排出筒は前記汚染物質分離装置に連結され、該過熱水蒸気吹付手段は前記過熱水蒸気生成供給装置に連結されていることを特徴とする土壌浄化装置。 A soil supply device that supplies soil containing pollutants (hereinafter referred to as “contaminated soil”), a superheated steam generation and supply device that generates and supplies superheated steam, and the contaminated soil that is supplied from the soil supply device A soil purification furnace that exposes the superheated steam supplied from the superheated steam generation and supply device to move pollutants contained in the contaminated soil into the superheated steam, and superheated steam discharged from the soil purification furnace. A pollutant separation device that cools and separates the pollutants from the superheated steam , and the soil purification furnace is provided substantially vertically through the sealed vertical furnace and the vertical furnace A superheated steam discharge tube, a fluidized hearth provided in a spiral around the superheated steam discharge tube in the vertical furnace, a soil supply device for supplying the contaminated soil on the fluidized hearth, and the flow To the contaminated soil on the hearth Superheated steam spraying means for spraying hot steam and a vibration device for vibrating the fluidized hearth, the superheated steam discharge cylinder is provided with a plurality of through holes, the superheated steam discharge cylinder and the vertical furnace are The soil charging device is provided in the upper part of the vertical furnace, the superheated steam discharge tube is connected to the pollutant separation device, and the superheated steam spraying means is connected to the superheated steam generation and supply device . A soil purification apparatus characterized by that. 前記縦型炉が、上段のプレヒート部と、該プレヒート部の下部に連結部を介して連結されている本吹部とからなり、該連結部には前記汚染土壌を破砕する破砕装置が設けられていることを特徴とする請求項1に記載の土壌浄化装置。   The vertical furnace comprises an upper preheating part and a main blowing part connected to the lower part of the preheating part via a connecting part, and the connecting part is provided with a crushing device for crushing the contaminated soil. The soil purification apparatus of Claim 1 characterized by the above-mentioned. 前記流動炉床が、略リング状の仕切壁によって外側の領域と内側の領域に区画され、最下段の流動炉床の外側の領域と最上段の流動炉床の内側の領域をつなぐバケットコンベアを備えていることを特徴とする請求項1に記載の土壌浄化装置。   The fluidized hearth is partitioned into an outer region and an inner region by a substantially ring-shaped partition wall, and a bucket conveyor that connects the outer region of the lowermost fluid hearth and the inner region of the uppermost fluidized hearth. The soil purification apparatus according to claim 1, wherein the soil purification apparatus is provided. 前記過熱水蒸気供給装置が、水蒸気を生成させる水蒸気生成装置と、該水蒸気生成装置によって生成された水蒸気を加熱して過熱水蒸気を生成する水蒸気加熱装置とからなることを特徴とする請求項1又は2に記載の土壌浄化装置。   The said superheated steam supply apparatus consists of a steam generator which produces | generates water vapor | steam, and a steam heater which produces | generates superheated steam by heating the water vapor | steam produced | generated by this steam generator. The soil purification apparatus as described in. 前記汚染物質分離装置において汚染物質が分離・除去された水蒸気を前記水蒸気加熱装置に導く水蒸気戻し機構を備えていることを特徴とする請求項3又は4に記載の土壌浄化装置。   5. The soil purification apparatus according to claim 3, further comprising a water vapor return mechanism that guides the water vapor from which contaminants have been separated and removed in the pollutant separation apparatus to the water vapor heating apparatus. 前記汚染土壌を掘削する掘削装置を備えていることを特徴とする請求項1〜5のいずれかに記載の土壌浄化装置。   The soil purification apparatus according to any one of claims 1 to 5, further comprising a drilling device that drills the contaminated soil. 移動手段を備えていることを特徴とする請求項1〜6のいずれかに記載の土壌浄化装置。   The soil purification apparatus according to any one of claims 1 to 6, further comprising a moving means. 前記汚染物質分離装置が、前記過熱水蒸気を段階的に冷却し、該過熱水蒸気から汚染物質を成分別に分離する汚染物質分離装置を備えていることを特徴とする請求項1〜7のいずれかに記載の土壌浄化装置。   8. The pollutant separation device includes a pollutant separation device that cools the superheated steam stepwise and separates the pollutant from the superheated steam according to components. The soil purification apparatus as described. 前記汚染物質分離装置で回収される余熱を前記各装置又は該各装置をつなぐ配管の保温に利用する余熱回収利用機構を備えていることを特徴とする請求項1〜8のいずれかに記載の土壌浄化装置。   9. A residual heat recovery and utilization mechanism that uses the residual heat recovered by the pollutant separation device to keep the temperature of each of the devices or a pipe connecting the devices is provided. Soil purification device.
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JP2009178621A (en) * 2008-01-29 2009-08-13 Toyo Constr Co Ltd Purification method of oil-polluted soil and purifying device
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Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63500677A (en) * 1985-08-26 1988-03-10 マンチャック フランク ジュニア Hazardous waste on-site treatment equipment and how to use it
JP2003094038A (en) * 2001-09-27 2003-04-02 Kogi Corp Detoxification and activation process of contaminated soil, or the like
JP2004209314A (en) * 2002-12-27 2004-07-29 Kogi Corp Treatment method and treatment apparatus of waste or the like by superheated steam

Family Cites Families (1)

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Publication number Priority date Publication date Assignee Title
JPH0192291A (en) * 1987-10-02 1989-04-11 Kanagawa Pref Gov Dry distillation apparatus

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63500677A (en) * 1985-08-26 1988-03-10 マンチャック フランク ジュニア Hazardous waste on-site treatment equipment and how to use it
JP2003094038A (en) * 2001-09-27 2003-04-02 Kogi Corp Detoxification and activation process of contaminated soil, or the like
JP2004209314A (en) * 2002-12-27 2004-07-29 Kogi Corp Treatment method and treatment apparatus of waste or the like by superheated steam

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