JP2015045562A - Decontamination method of radioactive contaminated soil, etc. - Google Patents

Decontamination method of radioactive contaminated soil, etc. Download PDF

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JP2015045562A
JP2015045562A JP2013176643A JP2013176643A JP2015045562A JP 2015045562 A JP2015045562 A JP 2015045562A JP 2013176643 A JP2013176643 A JP 2013176643A JP 2013176643 A JP2013176643 A JP 2013176643A JP 2015045562 A JP2015045562 A JP 2015045562A
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radioactive
contaminated soil
fermentation
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雅朋 皆川
Masatomo Minagawa
雅朋 皆川
達也 梶栗
Tatsuya Kajikuri
達也 梶栗
秀明 赤司
Hideaki Akashi
秀明 赤司
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JUNKANGATA SHAKAI KENKYU KYOKAI
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Abstract

PROBLEM TO BE SOLVED: To decontaminate soil, etc., contaminated with a radioactive material (cesium) by biology means.SOLUTION: The decontamination method of a radioactive contaminated soil, etc., comprises: adding an aqueous solution containing a microorganism group for promoting fermentation decomposition to wastes derived from deforestation trees including a bark of 50% or more to perform primary crushing; adding and mixing an organic fertilizer to chips obtained by the primary crushing to perform crushing again; filling the secondary crushing object in a bag formed by a material poor in water permeability and gas permeability; mixing and agitating a base member manufactured by fermenting and aging the secondary crushing object for an appropriate period of time and an object to be decontaminated, such as radioactive contaminated soil at an appropriate ratio; mixing an appropriate amount of a fermentation accelerator therewith; and maturing the resultant mixture in the state that ventilation is limited.

Description

本発明は、放射性セシウムで汚染された土壌、森林等において、微生物を利用して放射性物質を封じ込め、放射線を低減させる放射能汚染土壌等の除染方法に関するものである。   The present invention relates to a decontamination method for radioactively contaminated soil and the like in which radioactive substances are contained by using microorganisms in soil or forest contaminated with radioactive cesium to reduce radiation.

原子力発電所の事故により放射性物質が広く拡散され、拡散された土壌の表面から土中に浸透し、更に土中の水分と共に、樹木に吸収されている。   Radioactive materials are widely diffused due to accidents at nuclear power plants, penetrate into the soil from the surface of the diffused soil, and are absorbed by trees together with moisture in the soil.

これらの放射性物質特に放射性セシウムの除染手段として、微生物(放射性菌)に取り込ませて除染する方法が提案されている。例えば特許文献1(特開2013−68556号公報)には、特定の菌株に電気的に吸着させ、菌体が生存している状態で菌体ごと回収し、回収後に廃棄処分を行うことが開示されている。   As a means for decontaminating these radioactive substances, particularly radioactive cesium, a method of decontaminating them by incorporating them into microorganisms (radioactive bacteria) has been proposed. For example, Patent Document 1 (Japanese Patent Laid-Open No. 2013-68556) discloses that cells are electrically adsorbed to a specific strain, collected together with the cells remaining alive, and discarded after the collection. Has been.

また特許文献2(特開2013−130574号公報)には、光合成菌を含む除染剤を汚染地域に散布し、光合成菌が放射性物質を体内に取り込み、放射線を成長エネルギーとして吸引させて、放射線量の低減を図る手段が開示されている。   In Patent Document 2 (Japanese Patent Laid-Open No. 2013-130574), a decontaminating agent containing a photosynthetic bacterium is dispersed in a contaminated area, the photosynthetic bacterium takes a radioactive substance into the body, and the radiation is sucked as growth energy. Means for reducing the amount are disclosed.

また土壌中に存在する細菌の約1/10がセシウムを濃縮する能力を持っていることが知られている。これらの細菌はカリウムの濃縮機構(細胞内への取り込み)と同じ機構で濃縮している(非特許文献1:国立環境研究所ニュース1996年度15巻1号・富岡典子著「微生物による環境汚染物質の濃縮」)。更に「放線菌ロドコッカス・エリスロポリス」が放射性物質セシウム137を取り込むことが広く知られている。   It is also known that about 1/10 of the bacteria present in the soil have the ability to concentrate cesium. These bacteria are concentrated by the same mechanism as the potassium concentration mechanism (incorporation into cells) (Non-patent Document 1: National Institute for Environmental Studies, Vol. 15, No. 1, 1996, Noriko Tomioka, “Environmental Pollutants by Microorganisms” Concentration "). Furthermore, it is widely known that the actinomycetes Rhodococcus erythropolis takes in the radioactive substance cesium 137.

特開2013−68556号公報。JP2013-68556A. 特開2013−130574号公報。JP2013-130574A.

国立環境研究所ニュース1996年度15巻1号・富岡典子著「微生物による環境汚染物質の濃縮」National Institute for Environmental Studies, 1996 Volume 15 No.1 by Noriko Tomioka “Enrichment of Environmental Pollutants by Microorganisms”

種々の微生物が放射性物質(放射性セシウム)を細胞内に取り込むことは広く知られているが、当該微生物が多くの放射性物質を取り込んでしまうと、当該物質の放射線によって死滅してしまい、結局のところ放射性物質は元に戻ってしまう。このため特許文献1に示されているように菌が生存状態で回収する必要がある。その回収手段として当該菌体を含む水を回収したり、鉄分を塗布した多孔質担体に菌体を固定化し、磁石による回収を行うこと等が記載されている。   It is widely known that various microorganisms take in radioactive substances (radiocesium) into cells, but if the microorganisms take in many radioactive substances, they are killed by the radiation of the substances, and eventually Radioactive material will return. For this reason, as shown in Patent Document 1, it is necessary to recover the bacteria in a living state. As the recovery means, it is described that water containing the cells is recovered, or that the cells are immobilized on a porous carrier coated with iron, and recovered with a magnet.

然し所定の菌体に環境中の放射線物質を取り込ませても、その生存菌の回収作業が煩雑で有り、而も回収した放射線物質は更に所定の封じ込め処理を必要とする。   However, even if radioactive substances in the environment are taken into predetermined cells, the recovery of the viable bacteria is complicated, and the collected radioactive substances still require a predetermined containment process.

そこで本発明は、所定の発酵処理ベース部材を使用すると、微生物に放射線物質が取り込まれると共に、当該微生物の死滅後と想定された後も放射線を遮断(封じ込める)する現象を見出し、除染処理物も再利用できる新規な放射能汚染土壌等の除染方法を提案したものである。   Therefore, the present invention finds a phenomenon in which, when a predetermined fermentation treatment base member is used, a radiation substance is taken into a microorganism and radiation is blocked (contained) even after it is assumed that the microorganism has been killed. Proposed a new decontamination method for radioactively contaminated soil.

本発明に係る放射能汚染土壌等の除染方法は、樹皮50%以上を含む伐採樹木由来の廃棄物に、発酵分解を促進する微生物群を含有する水溶液を添加して一次粉砕を行い、前記一次粉砕で得られたチップに有機肥料を添加混合して再度粉砕し、二次粉砕物を通水性及び通気性が乏しい材質で形成した袋に詰めて、適宜期間発酵熟成させて製造したベース部材と、放射能汚染土壌等の除染対象物とを適宜な比率で混合撹拌すると共に、発酵促進剤を適宜量混合し、通気を制限した状態で腐熟させてなることを特徴とするものである。   In the decontamination method for radioactively contaminated soil and the like according to the present invention, an aqueous solution containing a group of microorganisms that promote fermentation decomposition is added to waste derived from a felled tree containing 50% or more of bark, and primary pulverization is performed. A base member manufactured by adding organic fertilizer to the chip obtained by primary pulverization, pulverizing it again, filling the secondary pulverized product in a bag formed of a material having poor water permeability and air permeability, and fermenting and aging as appropriate. And an object to be decontaminated such as radioactively contaminated soil at a suitable ratio, and a suitable amount of a fermentation accelerator is mixed and ripened in a state in which aeration is restricted. .

自然界(土壌中)の微生物群のうち放射性物質を取り込むことが知られており、厳密な微生物の特定が困難であるが、実証試験ではγ線の外部放射量が半減したことが確認できている。   It is known that radioactive substances are taken in from a group of microorganisms in the natural world (in the soil), and it is difficult to identify the exact microorganisms. However, in the verification test, it has been confirmed that the external radiation amount of γ rays has been halved. .

除染原理については、次の通り推定できる。ベース部材は、木質系バーク堆肥であり、放射性耐性細菌(例えばデイノコッカス・ラジオデュランス及ロドコッカス・エリスロポリス等)他の多種多様の有効微生物群と、有機ガラス成分と、樹木に含有されているアルミニウム成分を含んでおり、ベース部材と処理対象物を混合して腐熟させると、腐熟過程で、放射性耐性細菌がカリウムの取り込みと同様に放射性セシウムを細胞内に取り込む。   The decontamination principle can be estimated as follows. The base material is wood-based bark compost, which is a radio-resistant bacterium (such as Deinococcus radiodurance, Rhodococcus erythropolis, etc.) and other various effective microorganisms, organic glass components, and aluminum components contained in trees When the base member and the object to be treated are mixed and ripened, the radioactive bacterium takes up radioactive cesium into the cells in the same manner as the uptake of potassium.

一方有機ガラス成分は、ポリアクリルアミンをへてポリアクリルアミド化され、樹木に蓄積されていた置換性アルミニウムは、ベース部材製出時に破砕チップ化等にされることで、空気に触れ可溶性アルミニウムに変質する。このAlの媒介によって放射性セシウムが電気的に捕捉され、放射性セシウム(発酵熱で溶融状態である)を前記放射性耐性菌が取り込み、水溶性樹脂であるポリアクリルアミドが前記放射性耐性菌を被覆すると共に、バチルス菌がAl膜に引き寄せられ、体外に備えた胞子袋より硫酸を放出して前記ポリアクリルアミドの被膜形成がなされ、結果的に放射性セシウムを取込んだ放射性耐性菌が死滅しても、放射性セシウムが被膜され、γ線の放射を低減させると想定される。   On the other hand, the organic glass component is polyacrylamide converted into polyacrylamide, and the replaceable aluminum accumulated in the tree is converted into soluble aluminum by touching the air by making it into crushing chips etc. when producing the base member. To do. Radioactive cesium is electrically captured by the mediation of Al, and the radioactive bacterium (which is molten by fermentation heat) is taken up by the radioactive resistant bacterium, and the water-soluble resin polyacrylamide coats the radioactive resistant bacterium, Even if the Bacillus bacteria are attracted to the Al film and sulfuric acid is released from the spore bag provided outside the body to form the polyacrylamide film, the radioactive bacterium that has taken in the radioactive cesium is killed. Is coated to reduce the emission of gamma rays.

本発明は前記のとおりで、放射性物質で汚染された土壌等(汚染土、汚染家畜糞、汚染樹木)を、微生物の作用で除染を可能としたもので、除染処理物(腐熟させた堆肥化物)をそのまま農耕地の土壌改良資材として、リサイクル使用ができ、除染処理後の再固定化を必要としない除染方法を提供できたものである。   The present invention is as described above, and it is possible to decontaminate soil contaminated with radioactive substances (contaminated soil, contaminated livestock excrement, contaminated trees) by the action of microorganisms. As a soil improvement material for agricultural land, it can be recycled and can provide a decontamination method that does not require re-fixation after decontamination.

本発明の実証試験データで、処理対象物の温度経過表:表1。Table 1 shows the temperature course of the processing object in the demonstration test data of the present invention. 同汚染土の測定値:表2。Measurement values of the contaminated soil: Table 2. 同汚染牛糞堆肥の測定値:表3。Table 3 shows measured values of the contaminated cow manure compost. 同汚染木質生チップの測定値:表4。Table 4 shows measured values of the contaminated wooden raw chips. 同処理対象物の放射線量の変化を示すグラフで、各グラフの下方が現物測定値で上方が乾物換算値を示す。It is a graph which shows the change of the radiation dose of the process target object, the lower part of each graph shows an actual measurement value, and the upper part shows a dry matter conversion value. 同微生物の発酵促進用補給物の添加量表。Addition table of supplements for promoting fermentation of the microorganism.

本発明の実証試験を以下のとおり実施した。使用したベース部材は、樹皮50%以上を含む伐採樹木由来の廃棄物に、発酵分解を促進する微生物群を含有する水溶液(種々の有機廃棄物の堆肥化処理によって得られた堆肥液)を添加して一次粉砕を行い、前記一次粉砕で得られたチップに有機肥料を添加混合して再度粉砕し、二次粉砕物を通水性及び通気性が乏しい材質で形成した袋に詰めて、適宜期間発酵熟成させて製造した木質系バーク堆肥である。   The verification test of the present invention was performed as follows. The base member used is an aqueous solution containing a group of microorganisms that promote fermentation decomposition (compost solution obtained by composting various organic wastes) to the waste derived from felled trees containing 50% or more of the bark. Then, organic fertilizer is added to the chip obtained by the primary pulverization, pulverized again, and the secondary pulverized product is packed in a bag formed of a material having poor water permeability and air permeability, and is appropriately timed. It is a woody bark compost produced by fermentation and aging.

放射性物質に汚染された処理対象物は、「A:汚染地域の表土(剥ぎ取り汚染土)」「B:汚染地域の牛糞蓄積箇所から採取した牛糞」「C:汚染地域に繁殖している樹木を伐採し粉砕した木質チップ」とした。   The treatment objects contaminated with radioactive materials are “A: top soil in the contaminated area (peeled contaminated soil)”, “B: cattle dung collected from the cow dung accumulation site in the contaminated area”, “C: trees breeding in the contaminated area Wood chips felled and crushed.

実証試験は、処理対象物とベース部材を容積割合で4:6(400リットルと600リットル)として、更に発酵反応を促進させるために、120gの尿素と1リットルのゼオライトを加え、混合し、1立方のフレキシブルコンテナバック(以下「フレコンバック」という)に充填し、発酵熟成させた。   In the demonstration test, the processing object and the base member are set to a volume ratio of 4: 6 (400 liters and 600 liters), and 120 g of urea and 1 liter of zeolite are added and mixed to further promote the fermentation reaction. A cubic flexible container bag (hereinafter referred to as “flexible bag”) was filled and fermented.

実証試験結果の確認は以下のとおりである。
1.発酵の進行は、処理対象物を袋詰した状態で上層から50cmの位置から温度センサを処理対象物の中心に挿し入れ計測した温度で確認した(表1)。測定時の外気温は10〜14℃で、処理対象物をフレコンバックに5月12日に充填した翌日から外気温より高く発酵の進行が認められた。尚放射性セシウムの融点は28℃であるので、放射性セシウムは処理対象物の水分中にイオン化して存在していると推測され、カリウムイオンと同様に菌内に取り込まれる。
Confirmation of the verification test results is as follows.
1. The progress of fermentation was confirmed by the temperature measured by inserting a temperature sensor into the center of the processing object from a position 50 cm from the upper layer in a state where the processing object was packed (Table 1). The outside air temperature at the time of measurement was 10 to 14 ° C., and the progress of fermentation was recognized higher than the outside air temperature from the next day when the object to be treated was filled into the flexible container bag on May 12. Since the melting point of radioactive cesium is 28 ° C., it is assumed that radioactive cesium is ionized and present in the moisture of the object to be treated, and is taken into the fungus like potassium ions.

2.放射性物質濃度は、フレコン充填物から採取した試料1kgを、測定者が一般社団法人新潟県環境衛生中央研究所で、1000秒の測定時間を以て、水分測定とγ線スペクトルメータ(ゲルマニウム半導体検知器)測定した。測定結果は、表2〜4のとおりで、5日ある。また5月31日に表4の微生物発酵促進エネルギー補給のために添加物を添加した。   2. Concentration of radioactive material is 1 kg of sample collected from the flexible container filling, and the measurer is a general incorporated association, Niigata Prefectural Institute of Environmental Health, with a measurement time of 1000 seconds and a gamma ray spectrometer (germanium semiconductor detector). It was measured. A measurement result is as Tables 2-4, and has five days. In addition, additives were added on May 31 to supplement microbial fermentation accelerating energy in Table 4.

以上の実証実験から、放射性セシウムは放射線耐性菌に取り込まれ、5日で1/3もしくはそれ以上に減少した。また発酵が進行し、また発酵の進行促進させる添加物(微生物のエネルギー源)を加えて、発酵を継続して放射性物質の減少が認められない。即ち放射性物質を取り込む放射性耐性菌の増殖が認められず死滅しているが、前記菌が死滅したことによって放射性セシウムが再度処理対象物に溶け込むことなく、封じ込められていることが裏付けられる。   From the above demonstration experiment, radioactive cesium was taken up by radiation resistant bacteria and decreased to 1/3 or more in 5 days. Moreover, fermentation progresses and the additive (microorganism energy source) which accelerates | stimulates fermentation progress is added, fermentation is continued and the reduction | decrease of a radioactive substance is not recognized. That is, although the growth of the radioactive resistant bacteria which take in a radioactive substance is not recognized, it is dying, but it is supported that the radioactive cesium is contained without dissolving again in a processing target object because the said bacterium died.

このように本発明方法は、放射能汚染物質(除染対象物)を、放射性菌や有用菌(放射性菌の封じ込め作用を為す菌)、及び前記有用菌の働きを促進させる有機ガラス成分並びにアルミニウムを含有する樹木由来の堆肥物と混合して発酵熟成させると、放射性セシウムが微生物の働きで封じ込められ、除染を実現するものである。   As described above, the method of the present invention can be applied to radioactive pollutants (contamination targets), radioactive bacteria and useful bacteria (bacteria that contain radioactive bacteria), organic glass components that promote the action of the useful bacteria, and aluminum. When fermented and matured by mixing with compost derived from trees containing, radioactive cesium is contained by the action of microorganisms to achieve decontamination.

Claims (2)

樹皮50%以上を含む伐採樹木由来の廃棄物に、発酵分解を促進する微生物群を含有する水溶液を添加して一次粉砕を行い、前記一次粉砕で得られたチップに有機肥料を添加混合して再度粉砕し、二次粉砕物を通水性及び通気性が乏しい材質で形成した袋に詰めて、適宜期間発酵熟成して製造したベース部材と、放射能汚染土壌等の除染対象物とを適宜な比率で混合撹拌すると共に、発酵促進剤を適宜量添加混合し、通気を制限した状態で腐熟させてなることを特徴とする放射能汚染土壌等の除染方法。   An aqueous solution containing a group of microorganisms that promote fermentation decomposition is added to the waste derived from the felled tree containing 50% or more of the bark to perform primary pulverization, and organic fertilizer is added to and mixed with the chips obtained by the primary pulverization. Regrind again, pack the secondary pulverized product into a bag made of a material with poor water permeability and air permeability, and appropriately prepare a base member manufactured by fermentation and aging for an appropriate period and a decontamination target such as radioactively contaminated soil. A method for decontamination of radioactively contaminated soil or the like, characterized by mixing and stirring at a proper ratio, adding an appropriate amount of a fermentation accelerator and mixing the mixture, and ripening in a state where aeration is restricted. 有機肥料が、畜糞尿或いは発酵分解を促進する微生物群を含有する水溶液に漬け込んだ鶏糞である請求項1記載の放射能汚染土壌の除染方法、   The method for decontamination of radioactively contaminated soil according to claim 1, wherein the organic fertilizer is animal manure or chicken manure soaked in an aqueous solution containing a microorganism group that promotes fermentation decomposition,
JP2013176643A 2013-08-28 2013-08-28 Decontamination method of radioactive contaminated soil, etc. Pending JP2015045562A (en)

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RU2615486C1 (en) * 2016-08-30 2017-04-04 Федеральное государственное бюджетное научное учреждение "Всероссийский научно-исследовательский институт гидротехники и мелиорации имени А.Н. Костякова" (ФГБНУ "ВНИИГиМ им. А.Н. Костякова") Method for soil purification from radioactive cesium isotope
JP2019128187A (en) * 2018-01-23 2019-08-01 タオ・エンジニアリング株式会社 Wastewater treatment equipment by microorganism, wastewater treatment method, and microorganism used for wastewater treatment
JP2021532726A (en) * 2019-07-09 2021-12-02 コエンバイオ カンパニー リミテッド A composition for elementally converting a radioactive substance into a non-radioactive substance and a method for producing the composition.

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Publication number Priority date Publication date Assignee Title
RU2615486C1 (en) * 2016-08-30 2017-04-04 Федеральное государственное бюджетное научное учреждение "Всероссийский научно-исследовательский институт гидротехники и мелиорации имени А.Н. Костякова" (ФГБНУ "ВНИИГиМ им. А.Н. Костякова") Method for soil purification from radioactive cesium isotope
JP2019128187A (en) * 2018-01-23 2019-08-01 タオ・エンジニアリング株式会社 Wastewater treatment equipment by microorganism, wastewater treatment method, and microorganism used for wastewater treatment
JP7104959B2 (en) 2018-01-23 2022-07-22 タオ・エンジニアリング株式会社 Wastewater treatment equipment using microorganisms, wastewater treatment method, and microorganisms used for wastewater treatment
JP2021532726A (en) * 2019-07-09 2021-12-02 コエンバイオ カンパニー リミテッド A composition for elementally converting a radioactive substance into a non-radioactive substance and a method for producing the composition.

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