JP4423061B2 - Decomposition method of oil in soil - Google Patents
Decomposition method of oil in soil Download PDFInfo
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- JP4423061B2 JP4423061B2 JP2004039771A JP2004039771A JP4423061B2 JP 4423061 B2 JP4423061 B2 JP 4423061B2 JP 2004039771 A JP2004039771 A JP 2004039771A JP 2004039771 A JP2004039771 A JP 2004039771A JP 4423061 B2 JP4423061 B2 JP 4423061B2
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Description
本発明は、油成分を含む土壌において菌を増殖させて油成分を分解する土壌中油分の分解方法に関する。 The present invention relates to a method for degrading oil in soil, in which bacteria are grown in soil containing an oil component to decompose the oil component.
従来、油成分である芳香族炭化水素(PAH)を含む土壌において、微生物を増殖させて油成分を分解する場合、例えば、4環式PAH以下(4環以下のPAH)の低分子の油成分は多くの微生物により比較的容易に分解できるが、5環式PAH以上(5環以上のPAH)の油成分は分解が困難で、分解されることなく土壌中に残留するという問題があった(このような問題点に言及した適切な特許文献は見当たらない)。 Conventionally, when a microorganism is grown to decompose an oil component in soil containing an aromatic hydrocarbon (PAH) that is an oil component, for example, a low-molecular oil component of a 4-ring PAH or less (4-ring or less PAH) Can be decomposed relatively easily by many microorganisms, but oil components of 5-cyclic PAH or higher (5-ring or higher PAH) are difficult to decompose and remain in the soil without being decomposed ( There is no appropriate patent document that mentions such problems).
本発明者らは、5環式PAH以上の油成分に関する微生物による分解について研究と実験を繰り返したところ、硫酸塩還元菌が5環式PAH以上の油成分であるレジンあるいはアスファルテンの分解に有効であることを知見するに至った。 The inventors of the present invention have repeatedly studied and experimented on the decomposition of microorganisms with respect to oil components of five-ring PAH or more, and found that sulfate-reducing bacteria are effective in degrading resins or asphaltenes that are oil components of five-ring PAH or more. I came to know that there was.
本発明は、この新知見に基づくもので、その目的は、たとえ5環式PAH以上の油成分であるレジンあるいはアスファルテンを含む土壌であっても、微生物を増殖させて効果的に分解することのできる土壌中油分の分解方法を提供することである。 The present invention is based on this new finding, and its purpose is to grow microorganisms and effectively decompose them even in soil containing resin or asphaltene , which is an oil component higher than pentacyclic PAH. It is to provide a method for decomposing oil in soil.
本発明の第1の特徴構成は、5環以上の芳香族炭化水素の油成分であるレジンあるいはアスファルテンを含む土壌に硫酸または硫酸塩を添加し、嫌気性条件下で硫酸塩還元菌をpH4〜pH9の環境下で、かつ、10℃〜38℃の温度下で増殖させて、前記硫酸塩還元菌により前記5環以上の芳香族炭化水素を3環以下の芳香族炭化水素に低分子化し、その後、好気性条件下で好気性菌により前記3環以下の芳香族炭化水素を分解するところにある。 The first characteristic feature of the present invention, by adding sulfuric acid or sulfate to the soil containing the resin or asphaltenes is an oil component of 5 or more rings aromatic hydrocarbons, pH 4 to the sulfate-reducing bacteria in anaerobic conditions In an environment of pH 9 and grown at a temperature of 10 ° C. to 38 ° C. , the sulfate-reducing bacterium reduces the molecular weight of the aromatic hydrocarbons having 5 or more rings to aromatic hydrocarbons having 3 or less rings, Thereafter, the aromatic hydrocarbons having 3 or less rings are decomposed by aerobic bacteria under aerobic conditions.
本発明の第1の特徴構成によれば、5環以上の芳香族炭化水素の油成分であるレジンあるいはアスファルテンを含む土壌に硫酸または硫酸塩を添加して嫌気性条件下で硫酸塩還元菌を増殖させるので、後述する実験結果から明らかなように、その硫酸塩還元菌が高分子量の油成分を分解して低分子化する。より具体的には、レジンやアスファルテンのように、従来微生物による分解が不可能とされていた5環式PAH以上(5環以上のPAH)の油成分を3環式PAH以下(3環以下のPAH)に低分子化する。
そして、その後、好気性条件下で好気性菌によって、3環式PAH以下に低分子化された油成分を更に分解して、最終的に、土壌中に含まれる油成分を分解処理することができる。
According to the first characteristic configuration of the present invention, sulfate-reducing bacteria are added under anaerobic conditions by adding sulfuric acid or sulfate to soil containing resin or asphaltene which is an oil component of five or more aromatic hydrocarbons. As it grows, the sulfate-reducing bacteria decompose the high molecular weight oil component to lower the molecular weight, as is apparent from the experimental results described later. More specifically, oil components of 5-cyclic PAH or more (5-ring or more PAH) that have been conventionally impossible to be decomposed by microorganisms, such as resins and asphaltenes, are tricyclic PAH or less (3-ring or less PAH) is reduced in molecular weight.
And after that, the aerobic bacteria under aerobic conditions further decomposes the oil component whose molecular weight has been reduced to less than tricyclic PAH, and finally decomposes the oil component contained in the soil. I can .
その際、本発明の第1の特徴構成によれば、硫酸塩還元菌をpH4〜pH9の環境下で増殖させるので、硫酸塩還元菌の増殖が促進されて、比較的短期間のうちに5環式PAH以上の油成分を3環式PAH以下に低分子化することができ、特に、pH5〜pH7の環境下で増殖させるのがより効果的で好ましい。
At that time, according to the first characteristic configuration of the present invention, since the sulfate-reducing bacteria are grown in an environment of pH 4 to pH 9, the growth of the sulfate-reducing bacteria is promoted, and within a relatively short period of time, 5 An oil component of cyclic PAH or higher can be reduced to a molecular weight of tricyclic PAH or lower, and it is particularly effective and preferable to grow in an environment of
さらに、本発明の第1の特徴構成によれば、硫酸塩還元菌を10℃〜38℃の温度下で増殖させるので、硫酸塩還元菌の増殖が促進されて、比較的短期間のうちに5環式PAH以上の油成分を3環式PAH以下に低分子化することができ、特に、25℃〜38℃の温度下で増殖させるのがより効果的で好ましい。 Further, according to the first characterizing feature of the present invention, since grown at a temperature of 10 ° C. to 38 DEG ° C. The sulfate reducing bacteria, the growth of sulfate-reducing bacteria is promoted, among relatively short period In addition, it is possible to reduce the molecular weight of an oil component of 5 cyclic PAH or higher to 3 cyclic PAH or lower, and it is particularly effective and preferable to grow at a temperature of 25 ° C. to 38 ° C.
本発明の第2の特徴構成は、前記硫酸塩還元菌を5mM〜20mMの硫酸イオン濃度下で増殖させるところにある。 A second characteristic configuration of the present invention is that the sulfate-reducing bacteria are grown under a sulfate ion concentration of 5 mM to 20 mM.
本発明の第2の特徴構成によれば、硫酸塩還元菌を5mM〜20mMの硫酸イオン濃度下で増殖させるので、濃度的にはあまり毒性もなく、それでいて、硫酸塩還元菌の増殖促進効果を期待することができ、特に、10mM程度の硫酸イオン濃度下で増殖させるのがより効果的で好ましい。 According to the second characteristic configuration of the present invention, since the sulfate-reducing bacteria are grown under a sulfate ion concentration of 5 mM to 20 mM, the concentration is not very toxic, and the growth-promoting effect of the sulfate-reducing bacteria can be achieved. In particular, it is more effective and preferable to grow under a sulfate ion concentration of about 10 mM.
本発明による土壌中油分の分解方法につき、その実施の形態を説明する。
本発明は、特に、油成分としての芳香族炭化水素(PAH)を含む土壌に硫酸または硫酸塩を添加して嫌気性条件下で硫酸塩還元菌を増殖させ、その後、好気性条件下で好気性菌により分解する土壌中油分の分解方法であり、各種の実験を通してその効果を確認したので、主たる実験とその結果について言及する。
An embodiment of the method for decomposing oil in soil according to the present invention will be described.
In particular, the present invention adds sulfuric acid or sulfate to soil containing aromatic hydrocarbons (PAH) as an oil component to grow sulfate-reducing bacteria under anaerobic conditions, and then favors them under aerobic conditions. This is a method of degrading oil in soil, which is degraded by aerobic bacteria, and its effects have been confirmed through various experiments, so the main experiments and the results will be mentioned.
まず、実験に使用した装置について説明すると、図1に示すように、試料としての油成分を含む土壌Sを収容するガラス製のフィルターファンネルを試料容器1とし、培地としての溶液Lを収容する筒型平底のセパラブルフラスコ(容量1L)を溶液タンク2として、ポンプ3により溶液タンク2内の溶液Lを試料容器1へ循環供給するように構成した。
試料容器1は、ウォータージャケット4を装備した二重構造とし、試料土壌Sの空隙率を確保して目詰まりを回避するため、試料土壌Sと直径2mmのガラスビーズを1対1の重量比で混合したものを試料容器1内へ300g入れてシリコン栓で蓋をした。
溶液タンク2内には、溶液Lを攪拌するための攪拌装置5を配置し、光による影響を考慮して、試料容器1の外側をアルミホイルで覆って遮光した。
First, the apparatus used in the experiment will be described. As shown in FIG. 1, a glass filter funnel containing a soil S containing an oil component as a sample is used as a
The
In the
[実験例]
この図1に示す装置を使用して油成分の分解実験を行った。
なお、試料として5環式PAH以上(5環以上のPAH)の油成分であるレジンおよびアスファルテンを含む土壌Sを使用し、溶液Lとして硫酸イオン濃度が5mM〜20mM、より好ましくは、10mM程度の溶液を使用し、かつ、溶液LをpH4〜pH9、より好ましくは、pH5〜pH7に調整し、ウォータージャケット4に温水を供給して試料容器1内を10℃〜38℃、好ましくは、25℃〜38℃、より好ましくは、ほぼ35℃に維持して無酸素の条件下で静置した。そして、分解処理開始から57日、143日、248日後にそれぞれ油成分濃度を測定し、その結果を示したのが図2である。
[Experimental example]
An oil component decomposition experiment was conducted using the apparatus shown in FIG.
In addition, the soil S containing resin and asphaltenes, which are oil components of 5-cyclic PAH or higher (5-ring or higher PAH), is used as a sample, and the sulfate ion concentration is 5 mM to 20 mM, more preferably about 10 mM as the solution L. The solution L is used, and the solution L is adjusted to pH 4 to pH 9, more preferably
この図2において、横軸は経過日数、縦軸は土壌1g当たりの炭素濃度(mg)を示し、この実験結果から、248日後には、レジンおよびアスファルテン成分が約50%減少し、その一方で、より低分子のPAHである芳香族成分が増加し、炭素濃度は全体としてほとんど変化しなかったことが解った。
つぎに、その248日後の試料土壌Sをトレー上に広げて、試料土壌Sが乾燥せずかつ水に浸らない程度に水を供給し、1週間に1回の割合で攪拌して試料土壌Sに空気を供給し、56日後に油成分を測定した結果が図2の右端に示されている。これによると、前記芳香族成分が約76%減少し、炭素濃度も全体として約62%減少した。
In FIG. 2, the horizontal axis indicates the number of days elapsed, and the vertical axis indicates the carbon concentration (mg) per gram of soil. From this experimental result, the resin and asphaltene components are reduced by about 50% after 248 days. It was found that the aromatic component, which is a lower molecular weight PAH, increased and the carbon concentration hardly changed as a whole.
Next, the sample soil S after 248 days is spread on a tray, and water is supplied to such an extent that the sample soil S is not dried and soaked in water, and stirred once a week for the sample soil S. The result of measuring the oil component after 56 days after supplying air is shown in the right end of FIG. According to this, the aromatic component was reduced by about 76%, and the carbon concentration was also reduced by about 62% as a whole.
[比較例1]
上記の実験例と比較するため、同じ装置を使用して比較実験を行った。
なお、溶液Lとして水を使用した以外は、全て実験例と同じ条件で比較実験を行った。すなわち、試料としてレジンおよびアスファルテンを含む土壌Sを使用し、ウォータージャケット4に温水を供給して試料容器1内をほぼ35℃に維持し、無酸素の条件下で静置した。比較実験開始から57日、143日、248日後にそれぞれ油成分濃度を測定し、その結果を示したのが図3である。
この図3に示す実験結果から、248日後においても、油成分の濃度はほとんど変化しなかったことが解った。
[Comparative Example 1]
In order to compare with the above experimental example, a comparative experiment was performed using the same apparatus.
In addition, except that water was used as the solution L, all comparative experiments were performed under the same conditions as the experimental examples. That is, the soil S containing resin and asphaltenes was used as a sample, hot water was supplied to the water jacket 4 to maintain the inside of the
From the experimental results shown in FIG. 3, it was found that the concentration of the oil component hardly changed even after 248 days.
[比較例2]
念のために、好気性条件下での比較実験も行った。
すなわち、試料としてレジンおよびアスファルテンを含む土壌Sを使用し、その試料土壌Sをトレー上に広げて、試料土壌Sが乾燥せずかつ水に浸らない程度に水を供給し、1週間に1回の割合で攪拌して試料土壌Sに空気を供給し、56日後に油成分を測定した。その結果を示したのが図4である。
この図4に示す実験結果から、炭素成分が全体として約42%分解したが、分解したのはほとんどが前記芳香族成分であり、レジンおよびアスファルテン成分はほとんど分解しなかったことが解った。
[Comparative Example 2]
As a precaution, a comparative experiment was also performed under aerobic conditions.
That is, a soil S containing resin and asphaltenes is used as a sample, the sample soil S is spread on a tray, and water is supplied to the extent that the sample soil S is not dried and immersed in water, once a week. The air was supplied to the sample soil S with stirring at a ratio of ≦, and the oil component was measured after 56 days. The result is shown in FIG.
From the experimental results shown in FIG. 4, it was found that the carbon component decomposed by about 42% as a whole, but most of the carbon components were decomposed by the aromatic component, and the resin and asphaltenes component were hardly decomposed.
以上の実験例および比較例1と2から、油成分であるレジンおよびアスファルテンを含む土壌に硫酸イオン(硫酸または硫酸塩)を添加して嫌気性条件下で硫酸塩還元菌を増殖させ、その後、好気性条件下で好気性菌により分解処理することによって、硫酸イオンを添加しない嫌気性条件下のみでの処理、あるいは、好気性条件下のみでの処理では分解しなかったレジンおよびアスファルテン成分が確実に分解されて、土壌中の油成分が効果的に除去されることが明確となった。 From the above experimental examples and comparative examples 1 and 2, sulfate ions (sulfuric acid or sulfate) are added to the soil containing the resin and asphaltenes as oil components to grow sulfate-reducing bacteria under anaerobic conditions, Decomposition with aerobic bacteria under aerobic conditions ensures that the resin and asphaltene components were not decomposed only under anaerobic conditions without addition of sulfate ions or only under aerobic conditions. It was clarified that the oil component in soil was effectively removed .
1 試料容器
2 溶液タンク
3 ポンプ
4 ウォータージャケット
5 攪拌装置
L 溶液(培地)
S 試料土壌
DESCRIPTION OF
S Sample soil
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