JP4586592B2 - Purification system for oil-contaminated soil - Google Patents

Purification system for oil-contaminated soil Download PDF

Info

Publication number
JP4586592B2
JP4586592B2 JP2005078622A JP2005078622A JP4586592B2 JP 4586592 B2 JP4586592 B2 JP 4586592B2 JP 2005078622 A JP2005078622 A JP 2005078622A JP 2005078622 A JP2005078622 A JP 2005078622A JP 4586592 B2 JP4586592 B2 JP 4586592B2
Authority
JP
Japan
Prior art keywords
oil
contaminated soil
contaminated
concentration
rotary kiln
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.)
Active
Application number
JP2005078622A
Other languages
Japanese (ja)
Other versions
JP2006255633A (en
Inventor
尚哉 高田
浩基 緒方
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.)
Obayashi Corp
Original Assignee
Obayashi Corp
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 Obayashi Corp filed Critical Obayashi Corp
Priority to JP2005078622A priority Critical patent/JP4586592B2/en
Publication of JP2006255633A publication Critical patent/JP2006255633A/en
Application granted granted Critical
Publication of JP4586592B2 publication Critical patent/JP4586592B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Processing Of Solid Wastes (AREA)

Description

本発明は、主として掘削土に含まれる油分を除去して汚染土壌を浄化する油汚染土壌の浄化システムに関する。 The present invention relates to an oil-contaminated soil purification system that mainly purifies contaminated soil by removing oil contained in excavated soil.

工場跡地の土壌が油分で汚染されている場合、かかる油分が環境に拡散して周辺住民の生活に支障を来すことがなきよう、また、地下水に混入して水質を汚濁させることがなきよう、適切な浄化対策が必要となる。   If the soil of the factory site is contaminated with oil, the oil will not diffuse into the environment and interfere with the lives of the residents in the surrounding area. Appropriate purification measures are required.

油分で汚染された汚染土については、従来さまざまな方法で浄化処理が行われており、その代表的なものとして加熱処理がある。   The contaminated soil contaminated with oil has been subjected to purification treatment by various methods in the past, and a typical example is heat treatment.

かかる処理方法においては、油汚染土を加熱することによって該汚染土に含まれている油分を除去する。   In such a treatment method, oil contained in the contaminated soil is removed by heating the oil-contaminated soil.

そして、加熱を行う手段として、ロータリーキルンと呼ばれる回転型の加熱炉が知られており、かかる加熱炉を用いて油汚染土を加熱すれば、油分を効率よく除去することができる。   As a means for heating, a rotary heating furnace called a rotary kiln is known. If oil-contaminated soil is heated using such a heating furnace, oil can be efficiently removed.

特開2003−266058JP 2003-266058 A

ここで、汚染土壌は、通常、汚染源を中心として放射状に地盤内に拡散するため、汚染源のみならず、その周囲に拡がる相応範囲の土壌を掘削し、その掘削土を回転炉で加熱処理しなければならない。   Here, since contaminated soil usually diffuses into the ground in a radial pattern with the contamination source as the center, not only the contamination source but also a corresponding range of soil spreading around it must be excavated, and the excavated soil must be heated in a rotary furnace. I must.

そのため、回転炉も大量の汚染土を処理できる規模にしなければならず、油除去処理に膨大なコストが必要になるという問題を生じていた。   For this reason, the rotary furnace must also have a scale capable of treating a large amount of contaminated soil, which causes a problem that enormous costs are required for the oil removal treatment.

また、軽質油で汚染された区域と重質油で汚染された区域とが汚染土壌内に混在している場合があり、かかる場合にも上述したと同様の問題が生じる。   Moreover, the area contaminated with light oil and the area contaminated with heavy oil may be mixed in the contaminated soil, and in this case, the same problem as described above occurs.

本発明は、上述した事情を考慮してなされたもので、広い範囲に分布する油汚染土壌区域の浄化処理を効率よく行うことが可能な油汚染土壌の浄化システムを提供することを目的とする。 The present invention has been made in view of the above-described circumstances, and an object thereof is to provide an oil-contaminated soil purification system capable of efficiently performing purification processing of oil-contaminated soil areas distributed over a wide range. .

上記目的を達成するため、本発明に係る油汚染土壌の浄化システムは請求項に記載したように、油分を含む汚染土壌区域のうち、高濃度汚染区から掘削された高濃度汚染土を加熱処理することによって前記油分を除去する加熱炉と、前記高濃度汚染区の周囲に拡がる低濃度汚染区から掘削された低濃度汚染土を微生物分解処理することによって前記油分を除去する微生物分解処理手段とからなり、バイオパイルとして畝状に盛られた前記低濃度汚染土内に埋設され又はそれらの表面近傍に気密に配置される通気管を前記微生物分解処理手段に備えるとともに前記加熱炉を間接加熱式ロータリーキルンとし、該間接加熱式ロータリーキルンの排気口に連通接続された排ガス管と熱交換可能に配置され前記間接加熱式ロータリーキルンの外筒に連通接続された空気導入管を前記通気管に連通接続したものである。 In order to achieve the above-mentioned object, the oil-contaminated soil purification system according to the present invention heats highly-contaminated soil excavated from the highly-contaminated soil region among the contaminated soil regions containing oil as described in claim 1. A heating furnace that removes the oil component by processing, and a microbial decomposition treatment means that removes the oil component by microbially decomposing the low-concentration contaminated soil excavated from the low-concentration contaminated region spreading around the high-concentration contaminated region The microbial decomposition treatment means is provided with a ventilation pipe embedded in the low-concentration contaminated soil piled up in a bowl shape as a biopile or airtightly arranged near the surface thereof, and the heating furnace is indirectly heated. The rotary kiln is arranged so as to be able to exchange heat with the exhaust pipe connected to the exhaust port of the indirectly heated rotary kiln. Is the passing connected air inlet tube that connects communication with the vent pipe.

また、本発明に係る油汚染土壌の浄化システムは請求項に記載したように、油分を含む汚染土壌区域のうち、重質油汚染区から掘削された重質油汚染土を加熱処理することによって前記油分を除去する加熱炉と、軽質油汚染区から掘削された軽質油汚染土を微生物分解処理することによって前記油分を除去する微生物分解処理手段とからなり、バイオパイルとして畝状に盛られた前記軽質油汚染土内に埋設され又はそれらの表面近傍に気密に配置される通気管を前記微生物分解処理手段に備えるとともに前記加熱炉を間接加熱式ロータリーキルンとし、該間接加熱式ロータリーキルンの排気口に連通接続された排ガス管と熱交換可能に配置され前記間接加熱式ロータリーキルンの外筒に連通接続された空気導入管を前記通気管に連通接続したものである。 Moreover, the purification system of the oil-contaminated soil which concerns on this invention heat-treats the heavy oil-contaminated soil excavated from the heavy oil-contaminated area among the contaminated soil areas containing an oil component, as described in Claim 2. And a microbial decomposition treatment means for removing the oil by microbially decomposing light oil contaminated soil excavated from the light oil-contaminated area. In addition, the microbe decomposition treatment means includes a ventilation pipe embedded in the light oil-contaminated soil or air-tightly arranged near the surface thereof, and the heating furnace is an indirect heating rotary kiln, and an exhaust port of the indirect heating rotary kiln An air introduction pipe that is arranged to be able to exchange heat with an exhaust gas pipe that is connected to the exhaust pipe and that is connected to an outer cylinder of the indirectly heated rotary kiln is connected to the vent pipe. It is intended.

また、本発明に係る油汚染土壌の浄化システムは請求項に記載したように、油分を含む汚染土壌区域のうち、高濃度汚染区から掘削された高濃度汚染土を加熱処理することによって前記油分を除去する加熱炉と、前記高濃度汚染区の周囲に拡がる低濃度汚染区から掘削された低濃度汚染土を微生物分解処理することによって前記油分を除去する微生物分解処理手段とからなり、バイオパイルとして畝状に盛られた前記低濃度汚染土内に埋設され又はそれらの表面近傍に気密に配置される通気管を前記微生物分解処理手段に備えるとともに前記加熱炉を直接加熱式ロータリーキルンとし、該直接加熱式ロータリーキルンの加熱空気排出口に連通接続された排ガス管と熱交換可能に配置され前記直接加熱式ロータリーキルンの筒体内部空間に連通接続された空気導入管を前記通気管に連通接続したものである。 In addition, the oil-contaminated soil purification system according to the present invention is, as described in claim 3 , by heat-treating high-concentration contaminated soil excavated from the high-concentration contaminated region among the contaminated soil regions containing oil. A heating furnace for removing oil, and microbial decomposition treatment means for removing the oil by microbially decomposing low-concentration contaminated soil excavated from the low-concentration contaminated area spreading around the high-concentration contaminated area, The microbe decomposition treatment means includes a ventilation pipe embedded in the low-concentration contaminated soil piled up as a pile or airtightly arranged near the surface thereof, and the heating furnace is a direct heating rotary kiln, The exhaust pipe connected to the heated air discharge port of the direct heating rotary kiln is arranged so as to be able to exchange heat and communicates with the inner space of the cylinder of the direct heating rotary kiln. Is connected air inlet tube that connects communication with the vent pipe.

また、本発明に係る油汚染土壌の浄化システムは請求項に記載したように、油分を含む汚染土壌区域のうち、重質油汚染区から掘削された重質油汚染土を加熱処理することによって前記油分を除去する加熱炉と、軽質油汚染区から掘削された軽質油汚染土を微生物分解処理することによって前記油分を除去する微生物分解処理手段とからなり、バイオパイルとして畝状に盛られた前記軽質油汚染土内に埋設され又はそれらの表面近傍に気密に配置される通気管を前記微生物分解処理手段に備えるとともに前記加熱炉を直接加熱式ロータリーキルンとし、該直接加熱式ロータリーキルンの加熱空気排出口に連通接続された排ガス管と熱交換可能に配置され前記直接加熱式ロータリーキルンの筒体内部空間に連通接続された空気導入管を前記通気管に連通接続したものである。 Moreover, the purification system of the oil-contaminated soil which concerns on this invention heat-treats the heavy oil-contaminated soil excavated from the heavy oil-contaminated area among the contaminated soil areas containing an oil component, as described in Claim 4. And a microbial decomposition treatment means for removing the oil by microbial decomposition treatment of the light oil contaminated soil excavated from the light oil contaminated area, and is accumulated in a bowl shape as a biopile. In addition, the microbe decomposition treatment means includes a ventilation pipe embedded in the light oil-contaminated soil or arranged in the vicinity of the surface thereof, and the heating furnace is a direct heating rotary kiln, and the heating air of the direct heating rotary kiln An air introduction pipe which is arranged so as to be able to exchange heat with an exhaust gas pipe connected to an exhaust port and connected to an inner space of a cylinder of the direct heating type rotary kiln is connected to the passage. It is obtained by communicatively connected to the tube.

本出願人は、油汚染土壌が、ホットスポットと呼ばれる高濃度汚染区とその周囲に拡がる低濃度汚染区とに大別され、処理しなければならない土量は、低濃度汚染区の方が圧倒的に多いことに着眼し、さまざまな研究を行った結果、高濃度汚染区から掘削された高濃度汚染土を加熱処理するとともに、低濃度汚染区から掘削された低濃度汚染土を微生物分解処理すれば、大量の油汚染土を効率よく処理することができるという産業上きわめて有益な知見を得るにいたったものである。   The applicant has roughly classified oil-contaminated soil into high-concentration contaminated areas called hot spots and low-concentration contaminated areas spreading around the area, and the amount of soil to be treated is overwhelming in the low-concentrated contaminated areas. As a result of conducting various researches, the high-concentration contaminated soil excavated from the high-concentration contaminated area is heat-treated, and the low-concentrated contaminated soil excavated from the low-concentrated contaminated area is subjected to microbial decomposition treatment. In this way, we have obtained very useful knowledge in the industry that a large amount of oil-contaminated soil can be treated efficiently.

すなわち、第1の参考発明に係る油汚染土壌の浄化方法においては、まず、油分を含む汚染土壌区域を高濃度汚染区とその周囲に拡がる低濃度汚染区とに分け、前記高濃度汚染区から掘削された高濃度汚染土を加熱処理することによって油分を除去するとともに、低濃度汚染区から掘削された低濃度汚染土を微生物分解処理することによって油分を除去する。 That is, in the method for purifying oil-contaminated soil according to the first reference invention , first, the contaminated soil area containing oil is divided into a high-concentration contaminated area and a low-concentrated contaminated area extending around it. The oil content is removed by heat-treating the excavated high-concentration contaminated soil, and the oil content is removed by microbial decomposition treatment of the low-concentration contaminated soil excavated from the low-concentration contaminated area.

このようにすると、油分濃度は低いが大量に発生する低濃度汚染土を、微生物分解処理という比較的安価な処理方法で油分を除去することができるとともに、土量は少ないが汚染濃度が高い高濃度汚染土を、加熱処理という処理方法で油分を確実に除去することができる。   In this way, low-concentration contaminated soil that has a low oil concentration but is generated in large quantities can be removed by a relatively inexpensive treatment method called microbial decomposition, and the soil concentration is small but the contamination concentration is high. Oil content can be reliably removed from the contaminated soil by a treatment method called heat treatment.

そのため、汚染源とその周囲に拡がった油汚染土壌を効率よく浄化することが可能となる。   Therefore, it is possible to efficiently purify the pollution source and the oil-contaminated soil that has spread around it.

また、本出願人は、油汚染土壌において重質油で汚染された区域と軽質油で汚染された区域とが混在するとともに、軽質油汚染土の処理量が少なくないことに着眼し、さまざまな研究を行った結果、重質油汚染区から掘削された重質油汚染土を加熱処理するとともに、軽質油汚染区から掘削された軽質油汚染土を微生物分解処理すれば、大量の油汚染土を効率よく処理することができるという産業上きわめて有益な知見を得るにいたったものである。   In addition, the Applicant is aware that areas contaminated with heavy oil and areas contaminated with light oil are mixed in oil-contaminated soil, and that the amount of light oil-contaminated soil is not limited, As a result of the research, if the heavy oil contaminated soil excavated from the heavy oil contaminated area is heat treated and the light oil contaminated soil excavated from the light oil contaminated area is subjected to microbial decomposition treatment, a large amount of oil contaminated soil will be obtained. It has been the result of obtaining very useful knowledge in the industry that can be processed efficiently.

すなわち、第2の参考発明に係る油汚染土壌の浄化方法においては、まず、油分を含む汚染土壌区域を重質油汚染区と軽質油汚染区とに分け、重質油汚染区から掘削された重質油汚染土を加熱処理することによって油分を除去するとともに、軽質油汚染区から掘削された軽質油汚染土を微生物分解処理することによって油分を除去する。 That is, in the method for purifying oil-contaminated soil according to the second reference invention , first, the contaminated soil area containing oil was divided into a heavy oil-contaminated area and a light oil-contaminated area, and excavated from the heavy oil-contaminated area. The oil is removed by heat-treating the heavy oil-contaminated soil, and the light oil-contaminated soil excavated from the light oil-contaminated area is microbially decomposed to remove the oil.

このようにすると、軽質油ゆえ処理はしやすいが大量に発生する軽質油汚染土を、微生物分解処理という比較的安価な処理方法で油分を除去することができるとともに、微生物では分解処理しにくい重質油汚染土を、加熱処理という処理方法で油分を確実に除去することができる。   In this way, light oil-contaminated soil that is easy to treat because of light oil but can be removed in large quantities can be removed by a relatively inexpensive treatment method called microbial decomposition treatment, and heavy oil that is difficult to decompose with microorganisms can be removed. Oil content can be reliably removed from the quality oil contaminated soil by a treatment method called heat treatment.

そのため、重質油汚染区と軽質油汚染区とが混在している油汚染土壌を効率よく浄化することが可能となる。   Therefore, it becomes possible to efficiently purify oil-contaminated soil in which heavy oil-contaminated areas and light oil-contaminated areas are mixed.

第1の参考発明及び第2の参考発明において、前記加熱処理で生じた加熱空気を用いて前記微生物分解処理を行うようにすれば、加熱処理の廃熱を微生物分解処理で有効利用することが可能となり、浄化コストをさらに下げることが可能となる。 In the first reference invention and the second reference invention, if the microbial decomposition treatment is performed using the heated air generated by the heat treatment, the waste heat of the heat treatment can be effectively used in the microbial decomposition treatment. This makes it possible to further reduce the purification cost.

第3の参考発明に係る油汚染土壌の浄化システムにおいては、油分を含む汚染土壌区域を高濃度汚染区とその周囲に拡がる低濃度汚染区とに分け、前記高濃度汚染区から掘削された高濃度汚染土を加熱炉で加熱処理することによって油分を除去するとともに、低濃度汚染区から掘削された低濃度汚染土を微生物分解処理手段で微生物分解処理することによって油分を除去する。 In the system for purifying oil-contaminated soil according to the third reference invention , the contaminated soil area containing oil is divided into a high-concentration contaminated area and a low-concentrated contaminated area extending around the high-concentrated contaminated area. Oil concentration is removed by heat-treating the concentration-contaminated soil in a heating furnace, and oil concentration is removed by microbially decomposing the low-concentration contaminated soil excavated from the low-concentration contaminated area using a microbial decomposition treatment means.

このようにすると、油分濃度は低いが大量に発生する低濃度汚染土を、微生物分解処理という比較的安価な処理で油分を除去することができるとともに、土量は少ないが汚染濃度が高い高濃度汚染土を、加熱炉を用いた加熱処理で油分を確実に除去することができる。   In this way, it is possible to remove low-concentration contaminated soil that has a low oil concentration but a large amount by a relatively inexpensive treatment called microbial decomposition treatment, and a high concentration with a small amount of soil but high contamination concentration. Oil can be reliably removed from the contaminated soil by heat treatment using a heating furnace.

そのため、汚染源とその周囲に拡がった油汚染土壌を効率よく浄化することが可能となる。   Therefore, it is possible to efficiently purify the pollution source and the oil-contaminated soil that has spread around it.

第4の参考発明に係る油汚染土壌の浄化システムにおいては、油分を含む汚染土壌区域を重質油汚染区と軽質油汚染区とに分け、重質油汚染区から掘削された重質油汚染土を加熱炉で加熱処理することによって油分を除去するとともに、軽質油汚染区から掘削された軽質油汚染土を微生物分解処理手段で微生物分解処理することによって油分を除去する。 In the purification system for oil-contaminated soil according to the fourth reference invention , the contaminated soil area containing oil is divided into a heavy oil-contaminated area and a light oil-contaminated area, and heavy oil contamination excavated from the heavy oil-contaminated area Oil is removed by heat-treating the soil in a heating furnace, and light oil-contaminated soil excavated from the light oil-contaminated area is subjected to microbial decomposition treatment by a microbial decomposition treatment means.

このようにすると、軽質油ゆえ処理はしやすいが大量に発生する軽質油汚染土を、微生物分解処理という比較的安価な処理方法で油分を除去することができるとともに、微生物では分解処理しにくい重質油汚染土を、加熱処理という処理方法で油分を確実に除去することができる。   In this way, light oil-contaminated soil that is easy to treat because of light oil but can be removed in large quantities can be removed by a relatively inexpensive treatment method called microbial decomposition treatment, and heavy oil that is difficult to decompose with microorganisms can be removed. Oil content can be reliably removed from the quality oil contaminated soil by a treatment method called heat treatment.

そのため、重質油汚染区と軽質油汚染区とが混在している油汚染土壌を効率よく浄化することが可能となる。   Therefore, it becomes possible to efficiently purify oil-contaminated soil in which heavy oil-contaminated areas and light oil-contaminated areas are mixed.

微生物分解処理手段を構成するにあたっては、微生物による分解活性が高くなるように水分及び空気を供給可能に構成するとともに温度を適切に維持することができるように構成すればよいが、本願発明においては、バイオパイルとして畝状に盛られた前記低濃度汚染土若しくは前記軽質油汚染土内に埋設され又はそれらの表面近傍に気密に配置される通気管を前記微生物分解処理手段に備えるとともに前記加熱炉を間接加熱式ロータリーキルンとし、該間接加熱式ロータリーキルンの排気口に連通接続された排ガス管と熱交換可能に配置され前記間接加熱式ロータリーキルンの外筒に連通接続された空気導入管を前記通気管に連通接続したので、加熱処理の廃熱を微生物分解処理で有効利用することが可能となり、浄化コストをさらに下げることが可能となる。 In configuring the microbial decomposition treatment means, it may be configured to be able to supply moisture and air so as to increase the decomposition activity by microorganisms and to be able to maintain the temperature appropriately, in the present invention, The microbial decomposition treatment means includes a ventilation pipe embedded in the low-concentration contaminated soil or light oil-contaminated soil piled up as a biopile or airtightly disposed near the surface thereof, and the heating furnace Is an indirect heating rotary kiln, and an air introduction pipe connected to the outer cylinder of the indirect heating rotary kiln is connected to the exhaust pipe connected to the exhaust port of the indirect heating rotary kiln and connected to the outer cylinder of the indirect heating rotary kiln. since communicatively connected, the waste heat of the heat treatment it is possible to effectively use in microbial degradation process, further lowering the purification costs It becomes possible.

同様に、バイオパイルとして畝状に盛られた前記低濃度汚染土若しくは前記軽質油汚染土内に埋設され又はそれらの表面近傍に気密に配置される通気管を前記微生物分解処理手段に備えるとともに前記加熱炉を直接加熱式ロータリーキルンとし、該直接加熱式ロータリーキルンの加熱空気排出口に連通接続された排ガス管と熱交換可能に配置され前記直接加熱式ロータリーキルンの筒体内部空間に連通接続された空気導入管を前記通気管に連通接続したので、加熱処理の廃熱を微生物分解処理で有効利用することが可能となり、浄化コストをさらに下げることが可能となる。 Similarly, the microbial decomposition treatment means includes a ventilation pipe embedded in the low-concentration contaminated soil or the light oil-contaminated soil piled up as a biopile or airtightly arranged near the surface of the soil. The heating furnace is a direct heating rotary kiln, and the air introduction is arranged so as to be able to exchange heat with the exhaust gas pipe connected to the heated air discharge port of the direct heating rotary kiln, and connected to the cylindrical internal space of the direct heating rotary kiln. since the tube is connected in communication with the vent tube, the waste heat of the heat treatment it is possible to effectively use in microbial degradation process, it is possible to further reduce the cleaning cost.

以下、本発明に係る油汚染土壌の浄化システムの実施の形態について、添付図面を参照して説明する。なお、従来技術と実質的に同一の部品等については同一の符号を付してその説明を省略する。 Embodiments of a purification system for oil-contaminated soil according to the present invention will be described below with reference to the accompanying drawings. Note that components that are substantially the same as those of the prior art are assigned the same reference numerals, and descriptions thereof are omitted.

(第1実施形態) (First embodiment)

図1は、本実施形態に係る油汚染土壌の浄化システムを示した概略図である。同図でわかるように、本実施形態に係る油汚染土壌の浄化システム1は、加熱炉としての間接加熱式ロータリーキルン2と、微生物分解処理手段としてのバイオレメディエーションシステム3とから概ね構成してある。   FIG. 1 is a schematic diagram illustrating a purification system for oil-contaminated soil according to the present embodiment. As can be seen from the figure, the oil-contaminated soil purification system 1 according to the present embodiment is generally composed of an indirectly heated rotary kiln 2 as a heating furnace and a bioremediation system 3 as a microbial decomposition treatment means.

間接加熱式ロータリーキルン2は図2に示すように、油分を含む汚染土壌区域23のうち、ホットスポットとも称される高濃度汚染区21から掘削された油分濃度が高い高濃度汚染土を加熱処理するようになっている。   As shown in FIG. 2, the indirectly heated rotary kiln 2 heats high-concentration contaminated soil having a high oil concentration excavated from a high-concentration contaminated region 21, which is also called a hot spot, in the contaminated soil region 23 containing oil. It is like that.

間接加熱式ロータリーキルン2は図1でわかるように、高濃度汚染土が内部空間に保持される内筒4と該内筒が二重筒の形態で収容された外筒5とを備えるとともに該外筒の一端にバーナー6を取り付けてあり、外筒5に連通接続された空気導入管7を介して導入され熱交換器8から廃熱を受け取った空気をバーナー6で加熱して加熱空気とし、これを外筒5内に導入することによって、釜である内筒4を周囲から加熱することができるようになっている。   As shown in FIG. 1, the indirectly heated rotary kiln 2 includes an inner cylinder 4 in which high-concentration contaminated soil is held in an internal space, and an outer cylinder 5 in which the inner cylinder is accommodated in the form of a double cylinder. A burner 6 is attached to one end of the cylinder, and the air introduced through the air introduction pipe 7 connected to the outer cylinder 5 and receiving waste heat from the heat exchanger 8 is heated by the burner 6 to be heated air. By introducing this into the outer cylinder 5, the inner cylinder 4 as a hook can be heated from the surroundings.

内筒4は、両端部を除く中間部が筒体軸線廻りに回転自在となるように構成してあるとともに、一方の端部に高濃度汚染土を投入する投入口9及び排気口11を、他方の端部に給気口10及び処理土排出口13をそれぞれ設けてあり、内筒4の外側を流れる加熱空気によって該内筒内の高濃度汚染土を加熱処理するとともに、該加熱処理によって油分を揮発又は酸化分解し、その排ガスを給気口10から排気口11へと抜ける空気の流れに連行させて該排気口から排出することができるようになっている。ちなみに、油分が除去された処理済みの土は、処理土として処理土排出口13から排出される。   The inner cylinder 4 is configured such that an intermediate portion except for both end portions is rotatable around a cylinder axis, and an inlet 9 and an exhaust port 11 for introducing high-concentration contaminated soil into one end are provided. An air supply port 10 and a treated soil discharge port 13 are provided at the other end, respectively, and the high-concentration contaminated soil in the inner cylinder is heated by the heated air flowing outside the inner cylinder 4, and The oil component is volatilized or oxidatively decomposed, and the exhaust gas can be discharged from the exhaust port by being entrained in the flow of air passing from the supply port 10 to the exhaust port 11. Incidentally, the treated soil from which oil has been removed is discharged from the treated soil discharge port 13 as treated soil.

なお、内筒4の給気口10は、外筒5の端部であってバーナー6とは反対側に設置された加熱空気排出口12に連通接続してあり、加熱空気を内筒4内に導入するようになっている。すなわち、バーナー6で加熱された空気は、外筒5内に流入して内筒4を加熱するために利用された後、内筒4の給気口10から該内筒内に導入され、油分を揮発又は酸化分解させるために再利用される。   The air supply port 10 of the inner cylinder 4 is connected to a heated air discharge port 12 provided at the end of the outer cylinder 5 on the opposite side to the burner 6, and the heated air is connected to the inner cylinder 4. To be introduced. That is, the air heated by the burner 6 flows into the outer cylinder 5 and is used to heat the inner cylinder 4, and is then introduced into the inner cylinder from the air supply port 10 of the inner cylinder 4, Is reused to volatilize or oxidatively decompose.

一方、バイオレメディエーションシステム3は、高濃度汚染区21の周囲に拡がる低濃度汚染区22から掘削された油分濃度が低い低濃度汚染土を畝状に地表に盛ってなるバイオパイル15と、該バイオパイル内に埋設された通気管16とから概ね構成してあり、必要であれば、散水装置や栄養塩添加装置(図示せず)を適宜備えればよい。   On the other hand, the bioremediation system 3 includes a biopile 15 in which low-concentration soil having a low oil concentration excavated from a low-concentration contamination region 22 spreading around the high-concentration contamination region 21 is accumulated on the ground surface in a bowl shape, It is generally composed of a ventilation pipe 16 embedded in the pile, and if necessary, a watering device or a nutrient salt addition device (not shown) may be appropriately provided.

通気管16は、本管と該本管にヘッダーを介して分岐接続された複数の多孔管とからなり、該各多孔管が上述した各バイオパイル15内にそれぞれ埋設してある。   The vent pipe 16 is composed of a main pipe and a plurality of perforated pipes branched and connected to the main pipe via a header, and each of the perforated pipes is embedded in each biopile 15 described above.

ここで、通気管16の上流側は空気導入管7に連通接続してあり、熱交換器8から廃熱を受け取った温風を通気管16を介してバイオパイル15に送り込むことができるようになっており、通気管16から導入された温風、例えば40゜C〜60゜Cの空気がバイオパイル15内に供給されることによって、外気温が低い場合であっても、バイオパイル15内の土中温度は、微生物が活動しやすい30゜C程度の温度に適切に維持される。   Here, the upstream side of the ventilation pipe 16 is connected to the air introduction pipe 7 so that the warm air that has received waste heat from the heat exchanger 8 can be sent to the biopile 15 through the ventilation pipe 16. Even if the outside air temperature is low by supplying hot air introduced from the vent pipe 16, for example, air of 40 ° C. to 60 ° C., into the biopile 15, The soil temperature is appropriately maintained at a temperature of about 30 ° C. where microorganisms are likely to be active.

そして、かかる温風による温度維持と栄養塩や水分供給作用とが相まって微生物の分解活性が高くなり、かくしてバイオパイル15内の油分を効率よく微生物分解することができる。   And the temperature maintenance by such warm air and nutrient salt and water supply action combine, and the decomposition activity of microorganisms becomes high, and thus the oil in the biopile 15 can be efficiently decomposed by microorganisms.

通気管16からバイオパイル15内に送り込む空気の温度は、該バイオパイル内の土中温度が微生物の分解活性に適した温度、例えば30゜C前後となるように、例えば40゜C〜60゜Cに設定するものとし、空気導入管7からの温風の温度が高すぎる場合には、外気を通気管16に入れて適宜混合し、その上でバイオパイル15内に送り込むようにすればよい。   The temperature of the air fed into the biopile 15 from the vent pipe 16 is, for example, 40 ° C to 60 ° so that the temperature in the soil in the biopile is a temperature suitable for microbial decomposition activity, for example, around 30 ° C. If the temperature of the hot air from the air introduction pipe 7 is too high, the outside air may be mixed into the ventilation pipe 16 as appropriate, and then fed into the biopile 15. .

菌体としては土中菌をそのまま用いるようにしてもよいし、油分濃度に応じて適当な選抜菌を用いるようにしてもよい。   As the cells, soil bacteria may be used as they are, or appropriate selected bacteria may be used according to the oil concentration.

油汚染土壌の浄化システム1は、二次燃焼炉からなる排ガス処理装置19を備えており、間接加熱式ロータリーキルン2の排気口11を介して排出された排ガスに残留する油分を酸化分解し、処理済みのガスを排ガス管33を介して大気に放出するとともに、その廃熱を熱交換器8によって空気導入管7内の空気に伝えるようになっている。   The oil-contaminated soil purification system 1 includes an exhaust gas treatment device 19 composed of a secondary combustion furnace, and oxidatively decomposes and treats oil remaining in the exhaust gas discharged through the exhaust port 11 of the indirectly heated rotary kiln 2. The exhausted gas is discharged to the atmosphere through the exhaust gas pipe 33 and the waste heat is transmitted to the air in the air introduction pipe 7 by the heat exchanger 8.

本実施形態に係る油汚染土壌の浄化システム1を用いて油汚染土壌の浄化を行うには、まず、間接加熱式ロータリーキルン2の投入口9を介して該間接加熱式ロータリーキルンの内筒4に高濃度汚染土を投入する。   In order to purify oil-contaminated soil using the oil-contaminated soil purification system 1 according to the present embodiment, first, the inner cylinder 4 of the indirectly heated rotary kiln 2 is made high via the inlet 9 of the indirectly heated rotary kiln 2. Concentrate contaminated soil.

次に、熱交換器8及び空気導入管7を介して導入された空気をバーナー6で加熱して加熱空気とし、これを外筒5内に導入することによって、釜である内筒4を周囲から加熱するとともに、内筒4を加熱するために利用した加熱空気を、内筒4の給気口10から該内筒内に導入する。   Next, the air introduced through the heat exchanger 8 and the air introduction pipe 7 is heated by the burner 6 to form heated air, and this is introduced into the outer cylinder 5, thereby surrounding the inner cylinder 4 as a pot. The heated air used for heating the inner cylinder 4 is introduced into the inner cylinder from the air supply port 10 of the inner cylinder 4.

このようにすることで、内筒4内の高濃度汚染土に含まれる油分を揮発又は酸化分解するとともに、その排ガスを給気口10から排気口11へと抜ける空気の流れに連行させて該排気口から排出させる。   In this way, the oil contained in the high-concentration contaminated soil in the inner cylinder 4 is volatilized or oxidatively decomposed, and the exhaust gas is entrained in the flow of air passing from the air supply port 10 to the exhaust port 11. Exhaust from the exhaust port.

加熱温度は、例えば200〜300゜C程度とし、油分の濃度によって適宜調整するのがよい。   The heating temperature is, for example, about 200 to 300 ° C., and is suitably adjusted depending on the oil concentration.

一方、高濃度汚染区21の周囲に拡がる低濃度汚染区22から掘削された低濃度汚染土を地表に畝状に盛ってバイオパイル15とするとともに該バイオパイル内に通気管16を埋設し、該通気管の上流側を空気導入管7に連通接続する。   On the other hand, the low-concentration soil excavated from the low-concentration contamination area 22 spreading around the high-concentration contamination area 21 is piled up on the ground surface to form a biopile 15 and a ventilation pipe 16 is embedded in the biopile. The upstream side of the ventilation pipe is connected to the air introduction pipe 7 in communication.

そして、かかる状態で熱交換器8から廃熱を受け取った温風を通気管16を介してバイオパイル15内に送り込み、かかる温風による温度維持によって微生物活性を高めて油分の分解速度を促進させる。   And the warm air which received the waste heat from the heat exchanger 8 in this state is sent into the biopile 15 through the vent pipe 16, and the microorganism activity is enhanced by maintaining the temperature by the warm air to promote the decomposition rate of the oil. .

次に、間接加熱式ロータリーキルン2の排気口11を介して排出された排ガスに残留する油分を排ガス処理装置19で二次燃焼して酸化分解し、次いで、処理済みの排ガスを排ガス管33を介して大気に放出する。   Next, the oil remaining in the exhaust gas discharged through the exhaust port 11 of the indirectly heated rotary kiln 2 is subjected to secondary combustion in the exhaust gas treatment device 19 for oxidative decomposition, and then the treated exhaust gas is passed through the exhaust gas pipe 33. To the atmosphere.

以上説明したように、本実施形態に係る油汚染土壌の浄化システム1及び浄化方法によれば、まず、油分を含む汚染土壌区域23を高濃度汚染区21とその周囲に拡がる低濃度汚染区22とに分け、高濃度汚染区21から掘削された高濃度汚染土を間接加熱式ロータリーキルン2で加熱処理するとともに、低濃度汚染区から掘削された低濃度汚染土をバイオレメディエーションシステム3で微生物分解処理するようにしたので、濃度は低いが大量に発生する低濃度汚染土を、微生物分解処理という比較的安価でかつ安全な処理方法で油分を除去することができるとともに、土量は少ないが汚染濃度が高い高濃度汚染土を、確実な揮発又は酸化分解が可能な加熱処理という処理方法で油分を除去することができる。   As described above, according to the purification system 1 and the purification method for oil-contaminated soil according to the present embodiment, first, the contaminated soil area 23 containing oil is spread over the high-concentration contaminated area 21 and its surroundings. The high-concentration contaminated soil excavated from the high-concentration contaminated area 21 is heated by the indirect heating rotary kiln 2, and the low-concentration contaminated soil excavated from the low-concentrated contaminated area is microbially decomposed by the bioremediation system 3. As a result, it is possible to remove oil from low-concentration contaminated soil that is generated in large quantities but with a low concentration by using a relatively inexpensive and safe treatment method called microbial decomposition, and the soil concentration is low but the contamination concentration is low. The oil content can be removed from the high-concentration contaminated soil with a high temperature by a treatment method called heat treatment capable of reliable volatilization or oxidative decomposition.

そのため、小規模な加熱炉であっても、汚染源とその周囲に拡がった大量の油汚染土壌を効率よく浄化することが可能となり、かくして経済性に優れた高効率な浄化システムの構築が可能となる。   Therefore, even in a small heating furnace, it becomes possible to efficiently purify a large amount of oil-contaminated soil that spreads around the pollution source and its surroundings, and thus it is possible to construct a highly efficient purification system with excellent economic efficiency. Become.

加えて、上述した構成により、高濃度汚染土及び低濃度汚染土のいずれについても油汚染土を環境基準を満たすように確実に浄化することが可能となる。   In addition, with the above-described configuration, it is possible to reliably purify the oil-contaminated soil so as to satisfy the environmental standards for both the high-concentration contaminated soil and the low-concentration contaminated soil.

また、本実施形態に係る油汚染土壌の浄化システム1及び浄化方法によれば、バイオレメディエーションシステム3における微生物分解処理を、間接加熱式ロータリーキルン2の加熱処理で生じた加熱空気を用いて行うようにしたので、寒冷な気候であっても、加熱処理の廃熱を微生物分解処理で有効利用することで加温のためのエネルギーを節約することが可能となり、浄化コストをさらに下げることができる。   Moreover, according to the purification system 1 and the purification method for oil-contaminated soil according to the present embodiment, the microbial decomposition treatment in the bioremediation system 3 is performed using the heated air generated by the heat treatment of the indirect heating rotary kiln 2. Therefore, even in a cold climate, it is possible to save energy for heating by effectively utilizing the waste heat of the heat treatment in the microbial decomposition treatment, and the purification cost can be further reduced.

本実施形態では、排ガス処理装置として燃焼式を採用したが、これに代えて活性炭吸着方式を採用してもかまわない。 In the present embodiment , the combustion type is adopted as the exhaust gas treatment device, but an activated carbon adsorption method may be adopted instead.

また、本実施形態では、油分を含む汚染土壌区域を高濃度汚染区とその周囲に拡がる低濃度汚染区とに分け、高濃度汚染区から掘削された高濃度汚染土を加熱処理することによって油分を除去するとともに、低濃度汚染区から掘削された低濃度汚染土を微生物分解処理することによって油分を除去するようにしたが、これ以外にも、油分を含む汚染土壌区域を重質油汚染区と軽質油汚染区とに分け、重質油汚染区から掘削された重質油汚染土を間接加熱式ロータリーキルン2で加熱処理することによって油分を除去するとともに、軽質油汚染区から掘削された軽質油汚染土をバイオレメディエーションシステム3で微生物分解処理することによって油分を除去するようにしてもよい。   In the present embodiment, the contaminated soil area containing oil is divided into a high-concentration contaminated area and a low-concentrated contaminated area extending around the high-concentration contaminated area. In addition to removing oil by removing microorganisms from the low-contaminated soil excavated from the low-concentration contaminated area, the contaminated soil area containing the oil is treated as a heavy oil-contaminated area. The oil is removed by heating the heavy oil contaminated soil excavated from the heavy oil contaminated area with the indirect heating rotary kiln 2 and the light oil excavated from the light oil contaminated area. The oil content may be removed by subjecting the oil-contaminated soil to a microbial decomposition treatment using the bioremediation system 3.

かかる構成によれば、軽質油ゆえ処理はしやすいが比較的大量に発生する軽質油汚染土を、バイオレメディエーションシステム3を用いた微生物分解処理という比較的安価な処理方法で油分を除去することができるとともに、微生物では分解処理しにくい重質油汚染土を、間接加熱式ロータリーキルン2を用いた加熱処理という処理方法で油分を確実に除去することができる。   According to such a configuration, light oil contaminated soil that is easy to treat because of light oil but is generated in a relatively large amount can be removed by a relatively inexpensive treatment method called microbial decomposition treatment using the bioremediation system 3. In addition, heavy oil-contaminated soil that is difficult to decompose with microorganisms can be reliably removed by a treatment method called heat treatment using the indirectly heated rotary kiln 2.

そのため、重質油汚染区と軽質油汚染区とが混在している油汚染土壌を効率よく浄化することが可能となる。   Therefore, it becomes possible to efficiently purify oil-contaminated soil in which heavy oil-contaminated areas and light oil-contaminated areas are mixed.

かかる構成においては、高濃度汚染土が重質油汚染土に、低濃度汚染土が軽質油汚染土に代わるだけで他の構成や処理手順は上述の実施形態と同様であり、詳細な説明は省略するが、重質油汚染土を間接加熱式ロータリーキルン2で加熱処理する場合、加熱温度は600゜C程度に設定するのが望ましい。   In such a configuration, the high-concentration contaminated soil is replaced with heavy oil-contaminated soil, and the low-concentration contaminated soil is replaced with light oil-contaminated soil. Although omitted, when the heavy oil-contaminated soil is heat-treated with the indirectly heated rotary kiln 2, the heating temperature is preferably set to about 600 ° C.

また、本実施形態では、バイオパイル15内に通気管16を埋設するようにしたが、かかる構成に代えて、バイオパイル15の表面近傍に通気管16を気密に配置するようにしてもよい。   In the present embodiment, the ventilation pipe 16 is embedded in the biopile 15. However, instead of such a configuration, the ventilation pipe 16 may be airtightly disposed near the surface of the biopile 15.

通気管16を気密に配置する構成としては、例えばバイオパイル15を気密性シートで覆い、該気密性シートとバイオパイル15の表面との間に通気管16を配置する構成が考えられる。   As a configuration in which the ventilation pipe 16 is disposed in an airtight manner, for example, a configuration in which the biopile 15 is covered with an airtight sheet and the ventilation pipe 16 is disposed between the airtight sheet and the surface of the biopile 15 is conceivable.

また、本実施形態及び上述した変形例では、通気管16を空気導入管7に連通接続することで、該空気導入管からの温風を通気管16を介してバイオパイル15に送るように構成したが、かかる構成に代えて、空気導入管7を温水発生器に連通接続するとともに該温水発生器に連通接続された通水管から温水を取り出すようにし、該通水管をバイオパイル15内に埋設し又はそれらの表面近傍に配置するようにしてもよい。   Further, in the present embodiment and the above-described modification, the vent pipe 16 is connected to the air introduction pipe 7 so that the warm air from the air introduction pipe is sent to the biopile 15 through the vent pipe 16. However, instead of such a configuration, the air introduction pipe 7 is connected to the hot water generator and the hot water is taken out from the water pipe connected to the hot water generator, and the water pipe is embedded in the biopile 15. Alternatively, they may be arranged near the surface thereof.

(第2実施形態) (Second Embodiment)

次に、第2実施形態について説明する。なお、第1実施形態と実質的に同一の部品等については同一の符号を付してその説明を省略する。   Next, a second embodiment will be described. Note that components that are substantially the same as those of the first embodiment are denoted by the same reference numerals, and description thereof is omitted.

図3は、本実施形態に係る油汚染土壌の浄化システムを示した概略図である。同図でわかるように、本実施形態に係る油汚染土壌の浄化システム31は、加熱炉としての直接加熱式ロータリーキルン32と、微生物分解処理手段としてのバイオレメディエーションシステム3とから概ね構成してある。   FIG. 3 is a schematic view showing a purification system for oil-contaminated soil according to the present embodiment. As can be seen from the figure, the oil-contaminated soil purification system 31 according to this embodiment is generally composed of a direct heating rotary kiln 32 as a heating furnace and a bioremediation system 3 as a microbial decomposition treatment means.

直接加熱式ロータリーキルン32は、油分を含む汚染土壌区域23のうち、高濃度汚染区21から掘削された高濃度汚染土を加熱処理するようになっている。   The direct heating rotary kiln 32 heats high-concentration contaminated soil excavated from the high-concentration contaminated region 21 in the contaminated soil region 23 containing oil.

直接加熱式ロータリーキルン32は図3でわかるように、高濃度汚染土が内部空間に保持され中間部が筒体軸線廻りに回転自在に構成された筒体を備えるとともに該筒体の一端にバーナー6を取り付けてあり、筒体に連通接続された空気導入管7を介して導入され熱交換器8から廃熱を受け取った空気をバーナー6で加熱して加熱空気とし、これを筒体内に導入することによって、筒体内の高濃度汚染土を加熱処理することができるようになっている。   As shown in FIG. 3, the direct heating rotary kiln 32 includes a cylindrical body in which high-concentration contaminated soil is held in an internal space and an intermediate portion is configured to be rotatable around a cylindrical axis, and a burner 6 is provided at one end of the cylindrical body. The air that has been introduced through the air introduction pipe 7 connected to the cylinder and receives the waste heat from the heat exchanger 8 is heated by the burner 6 to be heated air, and this is introduced into the cylinder. As a result, the highly-contaminated soil in the cylinder can be heat-treated.

直接加熱式ロータリーキルン32は、バーナー6が設けられた同じ筒体端部に処理土排出口13aを設けてあるとともに、筒体の他端には高濃度汚染土を投入する投入口9a及び排気口11aをそれぞれ設けてあり、バーナー6による加熱空気によって筒体内の高濃度汚染土を加熱処理するとともに、該加熱処理によって油分を揮発又は酸化分解するようになっており、排ガスは、排気口11aから排出された後、二次燃焼炉からなる排ガス処理装置19で油分が酸化分解され、しかる後、排ガス管33を介して大気に放出される。ちなみに、油分が除去された処理済みの土は、処理土として処理土排出口13aから排出される。   The direct heating rotary kiln 32 is provided with a treated soil discharge port 13a at the end of the same cylinder where the burner 6 is provided, and an input port 9a and an exhaust port for supplying high-concentration contaminated soil to the other end of the cylinder. 11a is provided, and the high-concentration contaminated soil in the cylindrical body is heat-treated by the heated air from the burner 6, and the oil is volatilized or oxidatively decomposed by the heat treatment. The exhaust gas is discharged from the exhaust port 11a. After being discharged, the oil component is oxidatively decomposed by the exhaust gas treatment device 19 composed of a secondary combustion furnace, and then released to the atmosphere via the exhaust gas pipe 33. Incidentally, the treated soil from which oil has been removed is discharged from the treated soil discharge port 13a as treated soil.

一方、バイオレメディエーションシステム3は、高濃度汚染区21の周囲に拡がる低濃度汚染区22から掘削された油分濃度が低い低濃度汚染土を畝状に地表に盛ってなるバイオパイル15と、該バイオパイル内に埋設された通気管16とから概ね構成してあり、必要であれば、散水装置や栄養塩添加装置(図示せず)を適宜備えればよい。   On the other hand, the bioremediation system 3 includes a biopile 15 in which low-concentration soil having a low oil concentration excavated from a low-concentration contamination region 22 spreading around the high-concentration contamination region 21 is accumulated on the ground surface in a bowl shape, It is generally composed of a ventilation pipe 16 embedded in the pile, and if necessary, a watering device or a nutrient salt addition device (not shown) may be appropriately provided.

通気管16は、本管と該本管にヘッダーを介して分岐接続された複数の多孔管とからなり、該各多孔管が上述した各バイオパイル15内にそれぞれ埋設してある。   The vent pipe 16 is composed of a main pipe and a plurality of perforated pipes branched and connected to the main pipe via a header, and each of the perforated pipes is embedded in each biopile 15 described above.

ここで、通気管16の上流側は空気導入管7に連通接続してあり、熱交換器8から廃熱を受け取った温風を通気管16を介してバイオパイル15に送り込むことができるようになっており、通気管16から導入された温風、例えば40゜C〜60゜Cの空気がバイオパイル15内に供給されることによって、外気温が低い場合であっても、バイオパイル15内の土中温度は、微生物が活動しやすい30゜C程度の温度に適切に維持される。   Here, the upstream side of the ventilation pipe 16 is connected to the air introduction pipe 7 so that the warm air that has received waste heat from the heat exchanger 8 can be sent to the biopile 15 through the ventilation pipe 16. Even if the outside air temperature is low by supplying hot air introduced from the vent pipe 16, for example, air of 40 ° C. to 60 ° C., into the biopile 15, The soil temperature is appropriately maintained at a temperature of about 30 ° C. where microorganisms are likely to be active.

そして、かかる温風による温度維持と栄養塩や水分供給作用とが相まって微生物の分解活性が高くなり、かくしてバイオパイル15内の油分を効率よく微生物分解することができる。   And the temperature maintenance by such warm air and nutrient salt and water supply action combine, and the decomposition activity of microorganisms becomes high, and thus the oil in the biopile 15 can be efficiently decomposed by microorganisms.

通気管16からバイオパイル15内に送り込む空気の温度は、該バイオパイル内の土中温度が微生物の分解活性に適した温度、例えば30゜C前後となるように、例えば40゜C〜60゜Cに設定するものとし、空気導入管7からの温風の温度が高すぎる場合には、外気を通気管16に入れて適宜混合し、その上でバイオパイル15内に送り込むようにすればよい。   The temperature of the air fed into the biopile 15 from the vent pipe 16 is, for example, 40 ° C to 60 ° so that the temperature in the soil in the biopile is a temperature suitable for microbial decomposition activity, for example, around 30 ° C. If the temperature of the hot air from the air introduction pipe 7 is too high, the outside air may be mixed into the ventilation pipe 16 as appropriate, and then fed into the biopile 15. .

菌体としては土中菌をそのまま用いるようにしてもよいし、油分濃度に応じて適当な選抜菌を用いるようにしてもよい。   As the cells, soil bacteria may be used as they are, or appropriate selected bacteria may be used according to the oil concentration.

油汚染土壌の浄化システム31は、二次燃焼炉からなる排ガス処理装置19を備えており、直接加熱式ロータリーキルン32の排気口11aを介して排出された排ガスに残留する油分を酸化分解し、処理済みのガスを排ガス管33を介して大気に放出するとともに、その廃熱を熱交換器8によって空気導入管7内の空気に伝えるようになっている。   The oil-contaminated soil purification system 31 includes an exhaust gas treatment device 19 including a secondary combustion furnace, and oxidatively decomposes and treats oil remaining in the exhaust gas discharged through the exhaust port 11a of the direct heating rotary kiln 32. The exhausted gas is discharged to the atmosphere through the exhaust gas pipe 33 and the waste heat is transmitted to the air in the air introduction pipe 7 by the heat exchanger 8.

本実施形態に係る油汚染土壌の浄化システム31を用いて油汚染土壌の浄化を行うには、まず、直接加熱式ロータリーキルン32の投入口9aを介して該直接加熱式ロータリーキルンの筒体に高濃度汚染土を投入する。   In order to purify oil-contaminated soil using the oil-contaminated soil purification system 31 according to the present embodiment, first, a high concentration is applied to the cylinder of the direct heating rotary kiln through the inlet 9a of the direct heating rotary kiln 32. Put contaminated soil.

次に、熱交換器8及び空気導入管7を介して導入された空気をバーナー6で加熱して加熱空気とし、これを筒体内に導入することで筒体内の高濃度汚染土から油分を揮発又は酸化分解するとともに、その排ガスを排気口11aから排出させる。   Next, the air introduced through the heat exchanger 8 and the air introduction pipe 7 is heated by the burner 6 to form heated air, and this is introduced into the cylinder to volatilize the oil from the highly-contaminated soil in the cylinder. Alternatively, the exhaust gas is exhausted from the exhaust port 11a while being oxidatively decomposed.

加熱温度は、例えば200゜C〜300゜C程度とし、油分の濃度によって適宜調整するのがよい。   The heating temperature is preferably about 200 ° C. to 300 ° C., for example, and may be appropriately adjusted depending on the oil concentration.

一方、高濃度汚染区21の周囲に拡がる低濃度汚染区22から掘削された低濃度汚染土を地表に畝状に盛ってバイオパイル15とするとともに該バイオパイル内に通気管16を埋設し、該通気管の上流側を空気導入管7に連通接続する。   On the other hand, the low-concentration soil excavated from the low-concentration contamination area 22 spreading around the high-concentration contamination area 21 is piled up on the ground surface to form a biopile 15 and a ventilation pipe 16 is embedded in the biopile. The upstream side of the ventilation pipe is connected to the air introduction pipe 7 in communication.

そして、かかる状態で直接加熱式ロータリーキルン32で生じた廃熱をもらった温風を通気管16を介してバイオパイル15内に送り込み、かかる温風による温度維持によって微生物活性を高めて油分の分解速度を促進させる。   In such a state, warm air that has received waste heat generated in the direct heating rotary kiln 32 is sent into the biopile 15 through the vent pipe 16, and the microorganism activity is increased by maintaining the temperature by the warm air, thereby decomposing the oil. To promote.

次に、直接加熱式ロータリーキルン32の排気口11aから排出された排ガスに残留する油分を排ガス処理装置19で二次燃焼して酸化分解し、次いで、処理済みの排ガスを排ガス管33を介して大気に放出する。   Next, the oil remaining in the exhaust gas discharged from the exhaust port 11a of the direct heating rotary kiln 32 is subjected to secondary combustion in the exhaust gas treatment device 19 for oxidative decomposition, and then the treated exhaust gas is passed through the exhaust gas pipe 33 to the atmosphere. To release.

以上説明したように、本実施形態に係る油汚染土壌の浄化システム31及び浄化方法によれば、まず、油分を含む汚染土壌区域23を高濃度汚染区21とその周囲に拡がる低濃度汚染区22とに分け、高濃度汚染区21から掘削された高濃度汚染土を直接加熱式ロータリーキルン32で加熱処理するとともに、低濃度汚染区から掘削された低濃度汚染土をバイオレメディエーションシステム3で微生物分解処理するようにしたので、濃度は低いが大量に発生する低濃度汚染土を、微生物分解処理という比較的安価でかつ安全な処理方法で油分を除去することができるとともに、土量は少ないが汚染濃度が高い高濃度汚染土を、確実な揮発又は酸化分解が可能な加熱処理という処理方法で油分を除去することができる。   As described above, according to the purification system 31 and the purification method for oil-contaminated soil according to the present embodiment, first, the contaminated soil area 23 containing the oil component is spread over the high-concentration contaminated area 21 and its surroundings. The high-concentration contaminated soil excavated from the high-concentration contaminated area 21 is directly heated by the rotary kiln 32, and the low-concentration contaminated soil excavated from the low-concentrated contaminated area is microbially decomposed by the bioremediation system 3. As a result, it is possible to remove oil from low-concentration contaminated soil that is generated in large quantities but with a low concentration by using a relatively inexpensive and safe treatment method called microbial decomposition, and the soil concentration is low but the contamination concentration is low. The oil content can be removed from the high-concentration contaminated soil with a high temperature by a treatment method called heat treatment capable of reliable volatilization or oxidative decomposition.

そのため、小規模な加熱炉であっても、汚染源とその周囲に拡がった大量の油汚染土壌を効率よく浄化することが可能となり、かくして経済性に優れた高効率な浄化システムの構築が可能となる。   Therefore, even in a small heating furnace, it becomes possible to efficiently purify a large amount of oil-contaminated soil that spreads around the pollution source and its surroundings, and thus it is possible to construct a highly efficient purification system with excellent economic efficiency. Become.

加えて、上述した構成により、高濃度汚染土及び低濃度汚染土のいずれについても油汚染土を環境基準を満たすように確実に浄化することが可能となる。   In addition, with the above-described configuration, it is possible to reliably purify the oil-contaminated soil so as to satisfy the environmental standards for both the high-concentration contaminated soil and the low-concentration contaminated soil.

また、本実施形態に係る油汚染土壌の浄化システム31及び浄化方法によれば、バイオレメディエーションシステム3における微生物分解処理を、直接加熱式ロータリーキルン32の加熱処理で生じた排ガスの熱を用いて行うようにしたので、寒冷な気候であっても、加熱処理の廃熱を微生物分解処理で有効利用することで加温のためのエネルギーを節約することが可能となり、浄化コストをさらに下げることができる。   Further, according to the purification system 31 and the purification method for oil-contaminated soil according to the present embodiment, the microbial decomposition treatment in the bioremediation system 3 is performed using the heat of the exhaust gas generated by the heat treatment of the direct heating rotary kiln 32. Therefore, even in a cold climate, it is possible to save energy for heating by effectively utilizing the waste heat of the heat treatment in the microbial decomposition treatment, and the purification cost can be further reduced.

本実施形態では、排ガス処理装置として燃焼式を採用したが、これに代えて活性炭吸着方式を採用してもかまわない。 In the present embodiment , the combustion type is adopted as the exhaust gas treatment device, but an activated carbon adsorption method may be adopted instead.

また、本実施形態では、油分を含む汚染土壌区域を高濃度汚染区とその周囲に拡がる低濃度汚染区とに分け、高濃度汚染区から掘削された高濃度汚染土を加熱処理することによって油分を除去するとともに、低濃度汚染区から掘削された低濃度汚染土を微生物分解処理することによって油分を除去するようにしたが、これ以外にも、油分を含む汚染土壌区域を重質油汚染区と軽質油汚染区とに分け、重質油汚染区から掘削された重質油汚染土を直接加熱式ロータリーキルン32で加熱処理することによって油分を除去するとともに、軽質油汚染区から掘削された軽質油汚染土をバイオレメディエーションシステム3で微生物分解処理することによって油分を除去するようにしてもよい。   In the present embodiment, the contaminated soil area containing oil is divided into a high-concentration contaminated area and a low-concentrated contaminated area extending around the high-concentration contaminated area. In addition to removing oil by removing microorganisms from the low-contaminated soil excavated from the low-concentration contaminated area, the contaminated soil area containing the oil is treated as a heavy oil-contaminated area. The oil is removed by heating the heavy oil-contaminated soil excavated from the heavy oil-contaminated area directly with the rotary kiln 32 and the light oil excavated from the light oil-contaminated area. The oil content may be removed by subjecting the oil-contaminated soil to a microbial decomposition treatment using the bioremediation system 3.

かかる構成によれば、軽質油ゆえ処理はしやすいが比較的大量に発生する軽質油汚染土を、バイオレメディエーションシステム3を用いた微生物分解処理という比較的安価な処理方法で油分を除去することができるとともに、微生物では分解処理しにくい重質油汚染土を、直接加熱式ロータリーキルン32を用いた加熱処理という処理方法で油分を確実に除去することができる。   According to such a configuration, light oil contaminated soil that is easy to treat because of light oil but is generated in a relatively large amount can be removed by a relatively inexpensive treatment method called microbial decomposition treatment using the bioremediation system 3. In addition, heavy oil-contaminated soil that is difficult to decompose with microorganisms can be reliably removed by a treatment method called heat treatment using the direct heating rotary kiln 32.

そのため、重質油汚染区と軽質油汚染区とが混在している油汚染土壌を効率よく浄化することが可能となる。   Therefore, it becomes possible to efficiently purify oil-contaminated soil in which heavy oil-contaminated areas and light oil-contaminated areas are mixed.

かかる構成においては、高濃度汚染土が重質油汚染土に、低濃度汚染土が軽質油汚染土に代わるだけで他の構成や処理手順は上述の実施形態と同様であり、詳細な説明は省略するが、重質油汚染土を直接加熱式ロータリーキルン32で加熱処理する場合、加熱温度は600゜C程度に設定するのが望ましい。   In such a configuration, the high-concentration contaminated soil is replaced with heavy oil-contaminated soil, and the low-concentration contaminated soil is replaced with light oil-contaminated soil. Although omitted, when the heavy oil-contaminated soil is heat-treated directly by the rotary kiln 32, the heating temperature is preferably set to about 600 ° C.

また、本実施形態では、バイオパイル15内に通気管16を埋設するようにしたが、かかる構成に代えて、バイオパイル15の表面近傍に通気管16を気密に配置するようにしてもよい。   In the present embodiment, the ventilation pipe 16 is embedded in the biopile 15. However, instead of such a configuration, the ventilation pipe 16 may be airtightly disposed near the surface of the biopile 15.

通気管16を気密に配置する構成としては、例えばバイオパイル15を気密性シートで覆い、該気密性シートとバイオパイル15の表面との間に通気管16を配置する構成が考えられる。   As a configuration in which the ventilation pipe 16 is disposed in an airtight manner, for example, a configuration in which the biopile 15 is covered with an airtight sheet and the ventilation pipe 16 is disposed between the airtight sheet and the surface of the biopile 15 is conceivable.

また、本実施形態及び上述した変形例では、通気管16を空気導入管7に連通接続することで、該空気導入管からの温風を通気管16を介してバイオパイル15に送るように構成したが、かかる構成に代えて、空気導入管7を温水発生器に連通接続するとともに該温水発生器に連通接続された通水管から温水を取り出すようにし、該通水管をバイオパイル15内に埋設し又はそれらの表面近傍に配置するようにしてもよい。   Further, in the present embodiment and the above-described modification, the vent pipe 16 is connected to the air introduction pipe 7 so that the warm air from the air introduction pipe is sent to the biopile 15 through the vent pipe 16. However, instead of such a configuration, the air introduction pipe 7 is connected to the hot water generator and the hot water is taken out from the water pipe connected to the hot water generator, and the water pipe is embedded in the biopile 15. Alternatively, they may be arranged near the surface thereof.

第1実施形態に係る油汚染土壌の浄化システムの概略図。The schematic diagram of the purification system of oil pollution soil concerning a 1st embodiment. 高濃度汚染区とその周囲に拡がる低濃度汚染区とを示した図。The figure which showed the high concentration pollution area and the low concentration pollution area which spreads to the circumference | surroundings. 第3実施形態に係る油汚染土壌の浄化システムの概略図。Schematic of the purification system of the oil pollution soil which concerns on 3rd Embodiment.

符号の説明Explanation of symbols

1,31 油汚染土壌の浄化システム
2 間接加熱式ロータリーキルン(加熱炉)
3 バイオレメディエーションシステム
(微生物分解処理手段)
12 加熱空気排出口
15 バイオパイル
16 通気管
19 排ガス処理装置
21 高濃度汚染区
22 低濃度汚染区
23 汚染土壌区域
32 直接加熱式ロータリーキルン(加熱炉)
1,31 Purification system for oil-contaminated soil 2 Indirect heating rotary kiln (heating furnace)
3 Bioremediation system
(Microbe decomposition treatment means)
12 Heated air outlet 15 Biopile 16 Vent pipe 19 Exhaust gas treatment device 21 High-concentration contaminated area 22 Low-concentrated contaminated area 23 Contaminated soil area 32 Direct heating rotary kiln (heating furnace)

Claims (4)

油分を含む汚染土壌区域のうち、高濃度汚染区から掘削された高濃度汚染土を加熱処理することによって前記油分を除去する加熱炉と、前記高濃度汚染区の周囲に拡がる低濃度汚染区から掘削された低濃度汚染土を微生物分解処理することによって前記油分を除去する微生物分解処理手段とからなり、バイオパイルとして畝状に盛られた前記低濃度汚染土内に埋設され又はそれらの表面近傍に気密に配置される通気管を前記微生物分解処理手段に備えるとともに前記加熱炉を間接加熱式ロータリーキルンとし、該間接加熱式ロータリーキルンの排気口に連通接続された排ガス管と熱交換可能に配置され前記間接加熱式ロータリーキルンの外筒に連通接続された空気導入管を前記通気管に連通接続したことを特徴とする油汚染土壌の浄化システム。 Among the contaminated soil areas containing oil, from the heating furnace that removes the oil by heat-treating the high-concentration contaminated soil excavated from the high-concentration contaminated area, and from the low-concentration contaminated area spreading around the high-concentration contaminated area the excavated lower concentration contaminated soil Ri Do from the biodegradation process means for removing the oil by biodegradation process, embedded in the piled in ridged as bio pile low concentration contaminated soil or in their surface The microbial decomposition treatment means is provided with a ventilation pipe arranged in an airtight neighborhood in the vicinity, and the heating furnace is an indirect heating type rotary kiln, and is arranged so as to be able to exchange heat with an exhaust gas pipe connected to the exhaust port of the indirect heating type rotary kiln. purification system of oil contaminated soil, characterized in that the air inlet pipe is communicatively connected to the outer cylinder of the indirect heating type rotary kiln is connected in communication with the vent tube . 油分を含む汚染土壌区域のうち、重質油汚染区から掘削された重質油汚染土を加熱処理することによって前記油分を除去する加熱炉と、軽質油汚染区から掘削された軽質油汚染土を微生物分解処理することによって前記油分を除去する微生物分解処理手段とからなり、バイオパイルとして畝状に盛られた前記軽質油汚染土内に埋設され又はそれらの表面近傍に気密に配置される通気管を前記微生物分解処理手段に備えるとともに前記加熱炉を間接加熱式ロータリーキルンとし、該間接加熱式ロータリーキルンの排気口に連通接続された排ガス管と熱交換可能に配置され前記間接加熱式ロータリーキルンの外筒に連通接続された空気導入管を前記通気管に連通接続したことを特徴とする油汚染土壌の浄化システム。 Of the contaminated soil area containing oil, a heating furnace that removes the oil by heat-treating heavy oil-contaminated soil excavated from the heavy oil-contaminated area, and light oil-contaminated soil excavated from the light oil-contaminated area the Ri Do from the biodegradation process means for removing the oil by microbial decomposition treatment is arranged sealingly embedded in or near the surface thereof to said light oil polluted soil in which served in the ridged as bio pile A ventilation pipe is provided in the microbial decomposition treatment means, and the heating furnace is an indirect heating rotary kiln, and is arranged so as to be able to exchange heat with an exhaust gas pipe connected to an exhaust port of the indirect heating rotary kiln. A system for purifying oil-contaminated soil, characterized in that an air introduction pipe connected to a cylinder is connected to the vent pipe . 油分を含む汚染土壌区域のうち、高濃度汚染区から掘削された高濃度汚染土を加熱処理することによって前記油分を除去する加熱炉と、前記高濃度汚染区の周囲に拡がる低濃度汚染区から掘削された低濃度汚染土を微生物分解処理することによって前記油分を除去する微生物分解処理手段とからなり、バイオパイルとして畝状に盛られた前記低濃度汚染土内に埋設され又はそれらの表面近傍に気密に配置される通気管を前記微生物分解処理手段に備えるとともに前記加熱炉を直接加熱式ロータリーキルンとし、該直接加熱式ロータリーキルンの加熱空気排出口に連通接続された排ガス管と熱交換可能に配置され前記直接加熱式ロータリーキルンの筒体内部空間に連通接続された空気導入管を前記通気管に連通接続したことを特徴とする油汚染土壌の浄化システム。 Among the contaminated soil areas containing oil, from the heating furnace that removes the oil by heat-treating the high-concentration contaminated soil excavated from the high-concentration contaminated area, and from the low-concentration contaminated area spreading around the high-concentration contaminated area the excavated lower concentration contaminated soil Ri Do from the biodegradation process means for removing the oil by biodegradation process, embedded in the piled in ridged as bio pile low concentration contaminated soil or in their surface The microbe decomposition means is provided with a ventilation tube arranged in an airtight manner in the vicinity, and the heating furnace is a direct heating rotary kiln so that heat exchange is possible with an exhaust gas pipe connected to the heating air discharge port of the direct heating rotary kiln. oil pollution, wherein the placed air inlet tube which is communicatively connected to the cylindrical body inner space of the direct heating type rotary kiln that is connected in communication with the vent tube Soil purification system. 油分を含む汚染土壌区域のうち、重質油汚染区から掘削された重質油汚染土を加熱処理することによって前記油分を除去する加熱炉と、軽質油汚染区から掘削された軽質油汚染土を微生物分解処理することによって前記油分を除去する微生物分解処理手段とからなり、バイオパイルとして畝状に盛られた前記軽質油汚染土内に埋設され又はそれらの表面近傍に気密に配置される通気管を前記微生物分解処理手段に備えるとともに前記加熱炉を直接加熱式ロータリーキルンとし、該直接加熱式ロータリーキルンの加熱空気排出口に連通接続された排ガス管と熱交換可能に配置され前記直接加熱式ロータリーキルンの筒体内部空間に連通接続された空気導入管を前記通気管に連通接続したことを特徴とする油汚染土壌の浄化システム。 Among the contaminated soil areas containing oil, a heating furnace that removes the oil by heat-treating heavy oil-contaminated soil excavated from the heavy oil-contaminated area, and light oil-contaminated soil excavated from the light oil-contaminated area the Ri Do from the biodegradation process means for removing the oil by microbial decomposition treatment is arranged sealingly embedded in or near the surface thereof to said light oil polluted soil in which served in the ridged as bio pile The direct heating rotary kiln is provided with a ventilation pipe in the microbial decomposition treatment means and the heating furnace is a direct heating rotary kiln, and is arranged to be able to exchange heat with an exhaust gas pipe connected to a heating air discharge port of the direct heating rotary kiln. A system for purifying oil-contaminated soil, characterized in that an air introduction pipe communicated with the inner space of the cylinder is communicated with the vent pipe .
JP2005078622A 2005-03-18 2005-03-18 Purification system for oil-contaminated soil Active JP4586592B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2005078622A JP4586592B2 (en) 2005-03-18 2005-03-18 Purification system for oil-contaminated soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2005078622A JP4586592B2 (en) 2005-03-18 2005-03-18 Purification system for oil-contaminated soil

Publications (2)

Publication Number Publication Date
JP2006255633A JP2006255633A (en) 2006-09-28
JP4586592B2 true JP4586592B2 (en) 2010-11-24

Family

ID=37095419

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2005078622A Active JP4586592B2 (en) 2005-03-18 2005-03-18 Purification system for oil-contaminated soil

Country Status (1)

Country Link
JP (1) JP4586592B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101147430B1 (en) 2012-01-05 2012-05-22 주식회사 에코프라임 A biopile remediation system for contaminated soil, and the method thereof
JP6055233B2 (en) * 2012-08-10 2016-12-27 株式会社熊谷組 Contaminated soil purification equipment
CN114570763B (en) * 2022-03-15 2023-01-13 生态环境部南京环境科学研究所 Excavation soil remediation method for building construction contaminated soil

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004089793A (en) * 2002-08-30 2004-03-25 Shimizu Corp Method for washing soil contaminated with oil and equipment for washing contamination oil
JP2004202349A (en) * 2002-12-25 2004-07-22 Kajima Corp Polluted soil cleaning treatment apparatus

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004089793A (en) * 2002-08-30 2004-03-25 Shimizu Corp Method for washing soil contaminated with oil and equipment for washing contamination oil
JP2004202349A (en) * 2002-12-25 2004-07-22 Kajima Corp Polluted soil cleaning treatment apparatus

Also Published As

Publication number Publication date
JP2006255633A (en) 2006-09-28

Similar Documents

Publication Publication Date Title
CN103008337B (en) System and method for repairing organic material polluted soil
JP2007181784A (en) Waste treatment apparatus
JP4586592B2 (en) Purification system for oil-contaminated soil
CN202519200U (en) Organic waste cracking and carbonizing system with smoke recirculation
JP2006341249A (en) Dedusting and deodorizing system and method, and barn
KR100406496B1 (en) Stench and VOCs remove system using Biofilter and AC/ACF
KR101919594B1 (en) Non-pollution treatment methods for carcasses of slaughtered or dead animals infected with diseases
JP4534821B2 (en) Purification system and method for volatile organic compounds
KR100844915B1 (en) Food grabage ferment decompose extinction method and device that all processing of simultaneously processing is possible
JP2004034008A (en) Harmful organic material removal method using quick lime, hydrogen peroxide, and heat treatment
KR101217258B1 (en) Apparatus for purifying gas and method for purifying
KR100288578B1 (en) Sorting and method to purify soil, in the maintenance and restoration of the place reclaimed from rubbish
KR100289939B1 (en) Apparatus for removing odor of garbage disposer
JP3876360B2 (en) Detoxification method for contaminated soil
CN112974495A (en) Remediation method for organic contaminated soil
JP5103327B2 (en) Waste ozone treatment method and waste ozone treatment system
JP2007135402A (en) Device for treating contaminant discharged from experimental animal-rearing facility
CN211304219U (en) Organic pollution place prosthetic devices
JP3499782B2 (en) Method and apparatus for removing trace organic compounds in water
JP2010194436A (en) Wastewater treatment method
JP5110494B2 (en) Contaminated soil purification device and purification method
CN202356020U (en) Waste gas treating device
JP2011212669A (en) Decontaminating method for soil pollution
JP4465786B2 (en) Method and apparatus for treating human waste and / or septic tank sludge
CN114309050B (en) Device and method for in-situ remediation of organic contaminated soil by using flue gas

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20080210

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20100517

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20100524

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20100720

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20100810

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20100823

R150 Certificate of patent or registration of utility model

Ref document number: 4586592

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130917

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20130917

Year of fee payment: 3

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20140917

Year of fee payment: 4