JP2006095412A - Method for decomposing/removing heavy oils - Google Patents

Method for decomposing/removing heavy oils Download PDF

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JP2006095412A
JP2006095412A JP2004284099A JP2004284099A JP2006095412A JP 2006095412 A JP2006095412 A JP 2006095412A JP 2004284099 A JP2004284099 A JP 2004284099A JP 2004284099 A JP2004284099 A JP 2004284099A JP 2006095412 A JP2006095412 A JP 2006095412A
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heavy oils
white rot
decomposing
rot fungus
culture
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Tomoaki Nishida
友昭 西田
Hitoshi Murata
仁 村田
Fukashi Oguchi
深志 小口
Tatsuo Yamamoto
達生 山本
Yuko Takubo
祐子 田窪
Daisuke Morihashi
大輔 森橋
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Maeda Corp
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Maeda Corp
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for decomposing/removing heavy oils, by which the soil which is contaminated with heavy oils and contains a large amount of high-concentration heavy oils or a persistent component, can be cleaned under simple control. <P>SOLUTION: This method for decomposing/removing heavy oils is used for cleaning the soil contaminated with heavy oils by decomposing heavy oils by the decomposability of a microbe. A white rot fungus is adopted as the microbe. The contaminated soil is cleaned by using the white rot fungus and a white rot fungus-inoculated culture or a lignin-decomposable enzyme produced from the white rot fungus. When the white rot fungus and its culture are mixed in the soil contaminated with heavy oils and the mixture is cultured for one week to four weeks at 25-30°C, heavy oils can be decomposed/detoxified. Since the white rot fungus has the capacity for decomposing a persistent polycyclic aromatic compound, lignin can be decomposed. The white rot fungus is known as a microbe capable of decomposing dioxins, or the like. Therefore, the polycyclic aromatic compound to be hardly treated by the conventional bioremediation can be decomposed by the white rot fungus. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、重油類に汚染された汚染土壌を微生物の分解能により分解浄化する重油類の分解浄化工法に関する。   TECHNICAL FIELD The present invention relates to a method for decomposing and purifying heavy oils that decomposes and purifies contaminated soil contaminated with heavy oils by the resolution of microorganisms.

石油製品等を取り扱う事業所等の敷地を他の事業に転用する場合に、これらの敷地の土壌が石油等で汚染されている場合があり、この汚染土壌を浄化する必要がある。   When diverting the site of a business establishment that handles petroleum products to other businesses, the soil on these sites may be contaminated with oil or the like, and it is necessary to purify the contaminated soil.

従来行われている石油製品等による汚染土壌の浄化方法はその原理により、以下のように分類される。
(1)熱、触媒、光等により汚染物質を化学的に分解する方法。
(2)吸着、固化、抽出により汚染物質を化学的に除去する方法。
(3)土壌を遮蔽して汚染物質を物理的に封じ込める方法。
(4)微生物等を利用したバイオレメディエーションにより汚染物質を生物学的に分解する方法。
Conventional methods for purifying contaminated soil with petroleum products and the like are classified according to the principle as follows.
(1) A method of chemically decomposing pollutants with heat, catalyst, light or the like.
(2) A method of chemically removing contaminants by adsorption, solidification, and extraction.
(3) A method of shielding the soil and physically containing the contaminants.
(4) A method of biologically degrading contaminants by bioremediation using microorganisms or the like.

バイオレメディエーションとは生物的環境修復(浄化)技術であって、バイオレメディエーションには、土着微生物を活性化して自浄作用を増強、強化するバイオスティムレーションと外来微生物を導入(投入)するバイオオーギュメンテーションとがある。そして、これらの浄化方法は、浄化処理を、汚染現場で行う方法(インサイチューバイオレメディエーション又はオンサイトバイオレメディエーション)と、汚染現場以外で行う方法(エクサイチューバイオレメディエーション又はオフサイトバイオレメディエーション)とに分類できる。また、この方法は、土着の微生物類等を栄養塩の添加及び酸素供給によって活性化させ、重油類を分解・無害化させる方法である。
特開2004−8900号公報
Bioremediation is a bioenvironmental remediation (purification) technology, and bioremediation involves biostimulation that activates indigenous microorganisms to enhance and reinforce self-cleaning and introduces (inputs) foreign microorganisms. There is. These purification methods are classified into a method for performing purification treatment at a contaminated site (in situ bioremediation or on-site bioremediation) and a method for performing treatment at a site other than the contaminated site (ex situ bioremediation or offsite bioremediation). Can be classified. In addition, this method is a method in which indigenous microorganisms and the like are activated by adding nutrient salts and supplying oxygen, thereby decomposing and detoxifying heavy oils.
JP 2004-8900 A

ところで、前記(1)〜(4)の浄化方法は、比較的短時間の処理が可能であるが、燃料や電気のようなエネルギーを必要とし、また、1つの生態系である土壌環境を殺してしまう等、比較的環境への負荷(負担)が大きく、処理コストも高いという問題があった。   By the way, although the purification methods (1) to (4) can be processed for a relatively short time, they require energy such as fuel and electricity, and kill the soil environment as one ecosystem. For example, the load on the environment is relatively large and the processing cost is high.

また、(4)のバイオレメディエーションでは、高濃度の汚染土壌を処理するのが難しいといった問題や、重油成分の中でも難分解性の多環芳香族を分解することが難しいといった問題があった。   In addition, the bioremediation (4) has a problem that it is difficult to treat highly-contaminated soil, and a problem that it is difficult to decompose hardly decomposable polycyclic aromatics among heavy oil components.

更に、(4)のバイオレメディエーションでは、栄養塩を添加する工程や酸素を供給する工程が必要であり、などが必要であり、栄養塩の添加や酸素の供給(培養物を堆肥化させる)を管理するコストが高いという問題があった。   Furthermore, in the bioremediation of (4), a process of adding nutrient salts and a process of supplying oxygen are necessary, and it is necessary to add nutrient salts and supply oxygen (composting the culture). There was a problem that the cost to manage was high.

本発明は、前記課題を解決するためになされたものであり、高濃度の汚染土壌の処理、及び難分解性成分を多量に含んでいる重油類汚染土壌を簡単な管理で浄化処理できる重油類の分解浄化工法を提供することを技術的課題とする。   The present invention has been made in order to solve the above-mentioned problems, and can be used to treat high-concentration contaminated soil and heavy oil-contaminated soil containing a large amount of hardly decomposable components with a simple management. It is a technical problem to provide a method for decomposing and purifying water.

本発明は、重油類の分解浄化工法であり、前述の技術的課題を解決すべく以下のような構成とされている。
すなわち、本発明の重油類の分解浄化工法は、重油類に汚染された汚染土壌を微生物の分解能により分解浄化する重油類の分解浄化工法であって、
前記微生物として白色腐朽菌を採用し、
前記白色腐朽菌および前記白色腐朽菌を接種した培養物、または前記白色腐朽菌の産生するリグニン分解酵素を用いて前記汚染土壌を浄化することを特徴とする。
The present invention is a method for decomposing and purifying heavy oils, and has the following configuration in order to solve the above technical problems.
That is, the heavy oil decomposition and purification method of the present invention is a heavy oil decomposition and purification method that decomposes and purifies contaminated soil contaminated with heavy oil by the resolution of microorganisms,
Adopting white rot fungi as the microorganism,
The contaminated soil is purified using the white rot fungus, a culture inoculated with the white rot fungus, or a lignin-degrading enzyme produced by the white rot fungus.

この構成によれば、重油類汚染土壌に白色腐朽菌およびその培養物を混合し、25℃〜30℃で1週間から4週間培養を行うことにより、重油類を分解・無害化する。   According to this configuration, white rot fungi and cultures thereof are mixed with heavy oil contaminated soil and cultured at 25 ° C. to 30 ° C. for 1 to 4 weeks, thereby decomposing and detoxifying heavy oils.

また、白色腐朽菌は、難分解性の多環芳香族を分解する能力を有し、リグニンを分解できる。更に、白色腐朽菌は、ダイオキシン類等を分解する微生物として知られており、従来のバイオレメディエーションでは処理が困難であった多環芳香族を分解できる。   In addition, white rot fungi have the ability to degrade persistent polycyclic aromatics and can degrade lignin. Furthermore, white rot fungi are known as microorganisms that degrade dioxins and the like, and can degrade polycyclic aromatics that have been difficult to treat with conventional bioremediation.

また、本発明の重油類の分解浄化工法における前記培養物の中の培養基材としては、木質系材料を採用し、前記木質系材料を堆肥化させることなしに前記培養物を作成する。また、前記木質系材料は、葉を含有する剪定材である。   In addition, as a culture substrate in the culture in the method for decomposing and purifying heavy oils of the present invention, a woody material is adopted, and the culture is prepared without composting the woody material. The woody material is a pruning material containing leaves.

更に、本発明の重油類の分解浄化工法において、前記白色腐朽菌の産生するリグニン分解酵素がマンガンペルオキシダーゼ、ラッカーゼおよびリグニンペルオキシダーゼであることを特徴とする。   Furthermore, in the method for decomposing and purifying heavy oils of the present invention, the lignin-degrading enzyme produced by the white rot fungus is manganese peroxidase, laccase and lignin peroxidase.

更にまた、前記培養物を作成する時には、栄養塩を添加しないことを特徴とする。   Still further, when preparing the culture, no nutrient salt is added.

本発明は、高濃度の汚染土壌の処理、及び難分解性成分を多量に含んでいる重油類汚染土壌を栄養塩の添加や酸素の供給(培養物を堆肥化させる)を管理することなしに浄化処理できるものである。そのために、管理に必要な人件費の削減、および高濃度の汚染にまで対応できることから、浄化対象範囲を大幅に広げることができる。   The present invention is capable of treating highly contaminated soil, and managing the addition of nutrients and oxygen supply (composting the culture) to heavy oil contaminated soil containing a large amount of persistent components. It can be purified. For this reason, it is possible to reduce the labor cost required for management and cope with high-concentration contamination, so that the scope of purification can be greatly expanded.

以下、本発明に係る重油類の分解浄化工法の実施の形態について、図面を参照して詳細に説明する。   DESCRIPTION OF EMBODIMENTS Hereinafter, an embodiment of a heavy oil decomposition and purification method according to the present invention will be described in detail with reference to the drawings.

この実施の形態の重油類の分解浄化工法は、重油類(汚染土壌)を浄化する方法であって、重油類汚染土壌を白色腐朽菌およびその培養物、または白色腐朽菌の産生するリグニン分解酵素を用いて浄化するものである。この白色腐朽菌の産生するリグニン分解酵素はマンガンペルオキシダーゼ、ラッカーゼおよびリグニンペルオキシダーゼである。   The method for decomposing and purifying heavy oils according to this embodiment is a method for purifying heavy oils (contaminated soil), and lignin-degrading enzymes produced by white rot fungi and their cultures or white rot fungi. To purify. The lignin-degrading enzymes produced by this white rot fungus are manganese peroxidase, laccase and lignin peroxidase.

なお、この実施の形態では、重油類として、最も不揮発成分が多く分解しにくいC重油を対象とする。また、この実施の形態における培養物の中で培養基材として、木質系材料の木粉(ブナ脱脂木粉)を堆肥化させることなしに使用する。また、この木質系材料は、葉を含有する剪定材である。更に、白色腐朽菌(キノコ菌)は、YK−624やカワラタケを使用する。   In this embodiment, as heavy oils, C heavy oil with the largest amount of non-volatile components is the target. Moreover, the wood flour (beech defatted wood flour) is used as a culture substrate in the culture in this embodiment without composting. Further, this woody material is a pruning material containing leaves. Furthermore, YK-624 and Kawaratake are used as white rot fungi (mushrooms).

すなわち、C重油を含浸させた培養基材である木粉(ブナ脱脂木粉:重油濃度15000ppm)に白色腐朽菌(YK−624あるいはカワラタケ)を接種し、30℃にて1週間〜4週間静置培養を行い、その分解効果を確認した。   That is, inoculate wood flour (beech defatted wood flour: heavy oil concentration 15000 ppm) impregnated with C heavy oil with white rot fungi (YK-624 or Kawaratake) and leave at 30 ° C. for 1 to 4 weeks. Incubation was performed and the degradation effect was confirmed.

図1は重油類(C重油)の分解状態をグラフにて表したものである。なお、図1において、縦軸は残油量(%)を示し、横軸は経過時間を示す。   FIG. 1 is a graph showing the state of decomposition of heavy oils (C heavy oil). In FIG. 1, the vertical axis represents the amount of residual oil (%), and the horizontal axis represents the elapsed time.

図1において、白色腐朽菌にYK−624を用いた場合、開始より2週間経過後、残油量(%)が15%まで急激に変化し、更に6週間経過すると、残油量(%)が8%まで変化した。また、白色腐朽菌にカワラタケを用いた場合、開始より6週間経過すると、残油量(%)が8%まで変化した。   In FIG. 1, when YK-624 is used as a white rot fungus, the residual oil amount (%) changes rapidly to 15% after 2 weeks from the start, and after 6 weeks, the residual oil amount (%) Changed to 8%. In addition, when Kawaratake was used as the white rot fungus, the residual oil amount (%) changed to 8% after 6 weeks from the start.

このことから、白色腐朽菌(YK−624あるいはカワラタケなど)を用いてC重油の分解浄化可能であることがわかる。また、同じ白色腐朽菌でも、YK−624とカワラタケを比較すると、カワラタケよりYK−624の方が効率よく分解浄化することができる。   This shows that C heavy oil can be decomposed and purified using white rot fungi (YK-624, Kawaratake, etc.). Moreover, even if the same white rot fungus is compared with YK-624 and Kawaratake, YK-624 can be decomposed and purified more efficiently than Kawaratake.

また、この実施の形態によれば、白色腐朽菌にYK−624を用いた場合、高濃度のC重油を約1週間で半分程度(50%程度)分解することが確認できた。従って、従来の微生物では高濃度のC重油に対応できなかったものを、この実施の形態は可能にし、また、従来行われていた堆肥化させる(静置培養で切り返し等)ことが不必要であることから、効率的に分解・無害化できることが示唆された。   In addition, according to this embodiment, when YK-624 was used as the white rot fungus, it was confirmed that about a half (about 50%) of heavy C heavy oil was decomposed in about one week. Therefore, this embodiment makes it possible to use conventional microorganisms that could not cope with a high concentration of C heavy oil, and it is unnecessary to make compost (such as switching back by static culture) that has been conventionally performed. It was suggested that it can be efficiently decomposed and detoxified.

図2は効率よく分解浄化できる白色腐朽菌(YK−624)を用いてA重油、B重油、C重油の各々の分解状態をグラフにて表したものである。なお、図2において、縦軸は残油量(%)を示し、横軸は経過時間を示す。   FIG. 2 is a graph showing the decomposition state of each of A heavy oil, B heavy oil, and C heavy oil using white rot fungi (YK-624) that can be efficiently decomposed and purified. In FIG. 2, the vertical axis represents the amount of residual oil (%), and the horizontal axis represents the elapsed time.

図2において、A重油を白色腐朽菌にYK−624を用いて分解浄化すると、開始より2週間経過後、残油量(%)が10%まで急激に変化し、更に6週間経過すると、残油量(%)が5%まで変化した。また、B重油を白色腐朽菌にYK−624を用いて分解浄化すると、開始より2週間経過後、残油量(%)が10%まで急激に変化し、更に6週間経過すると、残油量(%)が5%まで変化した。C重油の場合は、開始より2週間経過後、残油量(%)が15%まで急激に変化し、更に6週間経過すると、残油量(%)が8%まで変化した。   In FIG. 2, when A heavy oil was decomposed and purified using YK-624 as a white rot fungus, the residual oil amount (%) changed rapidly to 10% after 2 weeks from the start, and after another 6 weeks, The oil amount (%) changed to 5%. When heavy oil B is decomposed and purified using white rot fungus with YK-624, the residual oil amount (%) changes rapidly to 10% after 2 weeks from the start, and after 6 weeks, the residual oil amount (%) Changed to 5%. In the case of C heavy oil, the residual oil amount (%) changed rapidly to 15% after 2 weeks from the start, and after 6 weeks, the residual oil amount (%) changed to 8%.

このことから、白色腐朽菌にYK−624を用いて分解浄化すると、A重油及びB重油は、C重油の場合より更に分解浄化が効率よくできることが確認できる。   From this, it can be confirmed that when the white rot fungus is decomposed and purified using YK-624, the A heavy oil and the B heavy oil can be further decomposed and purified more efficiently than the C heavy oil.

次に、本発明に係る重油類の分解浄化工法の実施例を説明する。
この実施例では、重油類汚染土壌として、砂質土壌にC重油を5000〜50000mg/kgで添加した模擬土壌を用いた。また、この実施例では、前述のように木質系材料の木粉(ブナ脱脂木粉)を堆肥化させることなしに使用する。
Next, examples of the heavy oil decomposition and purification method according to the present invention will be described.
In this example, simulated soil obtained by adding C heavy oil to sandy soil at 5000 to 50000 mg / kg was used as heavy oil contaminated soil. Moreover, in this Example, as mentioned above, it is used without composting wood-based material wood flour (beech defatted wood flour).

更に、白色腐朽菌(キノコ菌)は、YK−624を使用する。この実施例では、C重油を含浸させた3種類(5000ppm,20000ppm,50000ppm)の模擬土壌に白色腐朽菌を接種し、25℃にて3週間間静置培養を行い、C重油を添加した模擬土壌の分解浄化処理を行った。   Furthermore, YK-624 is used as a white rot fungus (mushroom fungus). In this example, three types (5000ppm, 20000ppm, 50000ppm) of simulated soil impregnated with C heavy oil were inoculated with white rot fungi, left to stand at 25 ° C for 3 weeks, and simulated with C heavy oil added. The soil was decomposed and purified.

図3はC重油を含浸させた3種類(5000ppm,20000ppm,50000ppm)の模擬土壌の各々の分解状態をグラフにて表したものである。なお、図3において、縦軸は残油量(%)を示し、横軸は経過時間を示す。   FIG. 3 is a graph showing the decomposition state of each of three types (5000 ppm, 20000 ppm, 50000 ppm) of simulated soil impregnated with C heavy oil. In FIG. 3, the vertical axis indicates the amount of residual oil (%), and the horizontal axis indicates the elapsed time.

図3において、5000ppmの模擬土壌を白色腐朽菌を用いて分解浄化すると、開始より1週間経過後、残油量(%)が18%まで急激に変化し、更に3週間経過すると、残油量(%)が8%まで変化した。また、20000ppmの模擬土壌を白色腐朽菌を用いて分解浄化する
と、開始より1週間経過後、残油量(%)が20%まで急激に変化し、更に3週間経過すると、残油量(%)が15%まで変化した。また、50000ppmの模擬土壌を白色腐朽菌を用いて分解浄化すると、開始より1週間経過後、残油量(%)が20%まで急激に変化し、更に3週間経過すると、残油量(%)が15%まで変化した。すなわち、本発明の重油類の分解浄化工法を用いると、高濃度(例えば50000ppm)の重油類であっても3週間で10%〜15%まで分解浄化できることが確認された。
In Fig. 3, when the simulated soil of 5000ppm is decomposed and purified using white rot fungi, the residual oil amount (%) changes rapidly to 18% after one week from the start, and after another three weeks, the residual oil amount (%) Changed to 8%. In addition, when 20,000 ppm simulated soil was decomposed and purified using white rot fungi, the remaining oil amount (%) changed rapidly to 20% after one week from the start, and after another three weeks, the remaining oil amount (% ) Changed to 15%. In addition, when 50,000 ppm simulated soil was decomposed and purified using white-rot fungi, the remaining oil amount (%) changed rapidly to 20% after 1 week from the start, and after another 3 weeks, the remaining oil amount (% ) Changed to 15%. That is, it was confirmed that the heavy oil decomposition and purification method of the present invention can be decomposed and purified to 10% to 15% in 3 weeks even for heavy oils of high concentration (for example, 50000 ppm).

5000ppmの模擬土壌を従来のバイオレメディエーションを用いて分解浄化すると、図3に示すように、開始より1週間経過後、残油量(%)が85%まで変化し、更に3週間経過すると、残油量(%)が65%まで変化した。   When the simulated soil of 5000ppm was decomposed and purified using conventional bioremediation, as shown in Fig. 3, the remaining oil amount (%) changed to 85% after 1 week from the start, and when 3 weeks passed, The oil amount (%) changed to 65%.

この実施例の結果によれば、本発明の重油類の分解浄化工法を用いると、従来のバイオレメディエーションでは、3週間かけて65%程度しか分解浄化できなかった高濃度(例えば50000ppm)の重油類を10%〜15%まで分解浄化できる。   According to the results of this example, when the decomposition and purification method for heavy oils of the present invention was used, the conventional bioremediation was able to decompose and purify only about 65% over 3 weeks. Can be decomposed and purified to 10% to 15%.

また、本発明の重油類の分解浄化工法において、培養物作成時には、栄養塩を添加しないので、管理が簡略化できる。更に、従来行われていた堆肥化させる(静置培養で切り返し等)ことが不必要であることから、管理が簡略化でき、効率的に分解・無害化できる。   Further, in the method for decomposing and purifying heavy oils according to the present invention, since no nutrient salt is added at the time of preparing a culture, management can be simplified. Furthermore, since it is not necessary to compost (reversed by static culture, etc.) which has been conventionally performed, management can be simplified, and decomposition and detoxification can be efficiently performed.

重油類(C重油)の分解状態をグラフにて表したものである。The decomposition state of heavy oil (C heavy oil) is represented with a graph. 効率よく分解浄化できる白色腐朽菌(YK−624)を用いてA重油、B重油、C重油の各々の分解状態をグラフにて表したものである。The decomposition state of each of A heavy oil, B heavy oil, and C heavy oil is graphically represented using white rot fungi (YK-624) that can be efficiently decomposed and purified. C重油を含浸させた3種類(5000ppm,20000ppm,50000ppm)の模擬土壌の各々の分解状態をグラフにて表したものである。凝集反応管の斜視図である。The decomposition state of each of three types (5000 ppm, 20000 ppm, 50000 ppm) of simulated soil impregnated with C heavy oil is represented by a graph. It is a perspective view of an aggregation reaction tube.

Claims (5)

重油類に汚染された汚染土壌を微生物の分解能により分解浄化する重油類の分解浄化工法であって、
前記微生物として白色腐朽菌を採用し、
前記白色腐朽菌および前記白色腐朽菌を接種した培養物、または前記白色腐朽菌の産生するリグニン分解酵素を用いて前記汚染土壌を浄化することを特徴とする重油類の分解浄化工法。
A method for decomposing and purifying heavy oils by decomposing and purifying contaminated soil contaminated with heavy oils by the resolution of microorganisms,
Adopting white rot fungi as the microorganism,
A method for decomposing and purifying heavy oils, wherein the contaminated soil is purified using the white rot fungus, a culture inoculated with the white rot fungus, or a lignin-degrading enzyme produced by the white rot fungus.
前記培養物の中の培養基材としては、木質系材料を採用し、
前記木質系材料を堆肥化させることなしに前記培養物を作成することを特徴とする請求項1に記載の重油類の分解浄化工法。
As a culture substrate in the culture, a woody material is adopted,
The method for decomposing and purifying heavy oils according to claim 1, wherein the culture is prepared without composting the woody material.
前記木質系材料は、葉を含有する剪定材であることを特徴とする請求項2に記載の重油類の分解浄化工法。   The method for decomposing and purifying heavy oils according to claim 2, wherein the woody material is a pruning material containing leaves. 前記白色腐朽菌の産生するリグニン分解酵素は、マンガンペルオキシダーゼ、ラッカーゼおよびリグニンペルオキシダーゼであることを特徴とする請求項1〜3のいずれかに記載の重油類の分解浄化工法。   The method for decomposing and purifying heavy oils according to any one of claims 1 to 3, wherein the lignin-degrading enzyme produced by the white rot fungus is manganese peroxidase, laccase and lignin peroxidase. 前記培養物を作成する時には、栄養塩を添加しないことを特徴とする請求項1〜4のいずれかに記載の重油類の分解浄化工法。   The method for decomposing and purifying heavy oils according to any one of claims 1 to 4, wherein no nutrient salt is added when the culture is prepared.
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006314858A (en) * 2005-05-10 2006-11-24 Petroleum Energy Center Method of purifying soil or water contaminated with heavy oil
CN105013815A (en) * 2015-07-28 2015-11-04 湖南大学 Biological remediation method for polycyclic aromatic hydrocarbon and heavy metal compound contaminated soil
CN110496856A (en) * 2019-07-24 2019-11-26 浙江工业大学 A kind of soil remediation method by pollution by pesticides based on laccase degradation

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Publication number Priority date Publication date Assignee Title
JPH11128903A (en) * 1997-10-31 1999-05-18 Ohbayashi Corp Decomposition removal of oil-polluted soil by microorganism
JP2002248460A (en) * 2001-02-22 2002-09-03 Marine Biotechnol Inst Co Ltd Method for accelerating decomposition of environmental pollutants by white decaying fungus
JP2004216342A (en) * 2003-01-17 2004-08-05 Kobe Steel Ltd Purifying method for soil contaminated with hardly-decomposable substance

Patent Citations (3)

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Publication number Priority date Publication date Assignee Title
JPH11128903A (en) * 1997-10-31 1999-05-18 Ohbayashi Corp Decomposition removal of oil-polluted soil by microorganism
JP2002248460A (en) * 2001-02-22 2002-09-03 Marine Biotechnol Inst Co Ltd Method for accelerating decomposition of environmental pollutants by white decaying fungus
JP2004216342A (en) * 2003-01-17 2004-08-05 Kobe Steel Ltd Purifying method for soil contaminated with hardly-decomposable substance

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006314858A (en) * 2005-05-10 2006-11-24 Petroleum Energy Center Method of purifying soil or water contaminated with heavy oil
CN105013815A (en) * 2015-07-28 2015-11-04 湖南大学 Biological remediation method for polycyclic aromatic hydrocarbon and heavy metal compound contaminated soil
CN110496856A (en) * 2019-07-24 2019-11-26 浙江工业大学 A kind of soil remediation method by pollution by pesticides based on laccase degradation

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