JPH0823965A - Proliferation factor of microorganism made hydrophobic - Google Patents

Proliferation factor of microorganism made hydrophobic

Info

Publication number
JPH0823965A
JPH0823965A JP16197594A JP16197594A JPH0823965A JP H0823965 A JPH0823965 A JP H0823965A JP 16197594 A JP16197594 A JP 16197594A JP 16197594 A JP16197594 A JP 16197594A JP H0823965 A JPH0823965 A JP H0823965A
Authority
JP
Japan
Prior art keywords
oil
growth factor
microorganisms
microorganism
proliferation factor
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.)
Pending
Application number
JP16197594A
Other languages
Japanese (ja)
Inventor
Naoshi Okawa
直士 大川
Hiromi Aoki
弘美 青木
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.)
Neos Co Ltd
Original Assignee
Neos Co Ltd
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 Neos Co Ltd filed Critical Neos Co Ltd
Priority to JP16197594A priority Critical patent/JPH0823965A/en
Publication of JPH0823965A publication Critical patent/JPH0823965A/en
Pending legal-status Critical Current

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Abstract

PURPOSE:To effectively decompose spilled pollutant oil with an microorganism without secondary environmental pollution by using a specific proliferation factor of microorganism made hydrophobic by coating it with a solid and hydrophobic organic compound. CONSTITUTION:A proliferation factor of a microorganism capable of decomposing oil such as of Pseudomonas bacterium is coated with a solid and hydrophobic organic compound such as paraffin wax or the like to obtain the objective proliferation factor. A microorganism capable of decomposing oil and this proliferation factor composition are scattered to the spilled oil contaminating sea and river or applied to the soil in the construction site penetrated with the pollutant oil.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、海、河川、湖水、排水
ピット等に流出した油および石油備蓄基地や工事現場等
の土壌に滲入した油等の流出汚染油の処理に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the treatment of oil spilled into the sea, rivers, lake water, drainage pits, etc. and oil spilled into soil such as oil storage bases and construction sites.

【0002】[0002]

【従来の技術】タンカーの事故等によって油が海上に流
出し、しばしば多大な被害を及ぼしている。また、陸上
においても、油が流出して水や土壌を汚染する事故が頻
発している。このような流出油を除去するための方法
は、3種に大別される。
2. Description of the Related Art Oil is leaked to the sea due to a tanker accident or the like, which often causes great damage. Also on land, there are frequent accidents where oil spills and contaminates water and soil. Methods for removing such spilled oil are roughly classified into three types.

【0003】第一の方法は、特殊なマットで油を吸収し
て除去する方法である。この方法による油の除去は迅速
であり、大まかな油の除去に効果的である。しかしなが
ら、この方法によっては、岸壁、砂、岩石等に付着した
油や、土壌に滲入した油を除去することはできない。ま
た、油を吸収したマットは焼却する以外には処理する方
法がなく、これを処理することによってばい煙や有害な
ガスが発生することが問題である。
The first method is to absorb and remove oil with a special mat. The removal of oil by this method is rapid and effective in removing crude oil. However, this method cannot remove oil adhering to the quay, sand, rocks, etc., or oil that has infiltrated into the soil. In addition, there is no method for treating a mat that has absorbed oil except incineration, and there is a problem that soot and harmful gas are generated by treating this.

【0004】第二の方法は化学薬品を用いて油を水に乳
化分散させる方法であり、簡便に油を処理できることが
利点である。しかしながら、水中に分散した油は自然界
に生息する微生物によって分解されると考えられている
が、現実には分散した油の挙動は不明である。また、化
学薬品が水産動植物に及ぼす影響が懸念されている。
The second method is a method in which an oil is emulsified and dispersed in water by using a chemical, and it is advantageous that the oil can be easily treated. However, although it is considered that oil dispersed in water is decomposed by microorganisms living in nature, the behavior of dispersed oil is unknown in reality. In addition, there are concerns about the effects of chemicals on aquatic plants and animals.

【0005】第三の方法は、油分解能を有する微生物を
利用することによって油を分解・除去する方法である。
微生物を利用する油処理技術においては、化学薬品によ
る処理を行った場合のような二次汚染の懸念が全くない
ことが利点である。また、微生物は、土壌に滲入した油
のように吸着マットが使用できない油の除去にも有効で
ある。これらのことから、微生物を用いる油の除去技術
には大きな期待がかけられてきた。
The third method is a method of decomposing and removing oil by utilizing a microorganism having oil degrading ability.
In the oil treatment technology utilizing microorganisms, it is an advantage that there is no concern about secondary contamination as in the case of treatment with chemicals. Microorganisms are also effective in removing oils that the adsorption mat cannot use, such as oils that have infiltrated the soil. For these reasons, great expectations have been placed on oil removal technology using microorganisms.

【0006】微生物によって油を分解・除去するために
は、微生物に必須の増殖因子を油と接触させることが必
要である。しかしながら、これらの増殖因子は水溶性で
あるため水に拡散し、油分解菌が効果的に増殖因子を利
用できないこととなる。このような課題を克服するた
め、増殖因子をw/oエマルション内に封入して流出を防
止する方法が提案されている(特公昭61−11590
号公報参照)。しかしながら、この方法においてはエマ
ルションが外部からの衝撃等によって比較的容易に破壊
されるため、増殖因子が水中に拡散する恐れがある。ま
た、エマルションを形成するためには活性剤等の薬剤を
添加する必要があり、これによって二次的な環境汚染が
引き起こされる懸念もある。
In order to decompose and remove oil by microorganisms, it is necessary to bring a growth factor essential for microorganisms into contact with oil. However, since these growth factors are water-soluble, they diffuse into water, and the oil-degrading bacteria cannot effectively use the growth factors. In order to overcome such problems, a method has been proposed in which a growth factor is enclosed in a w / o emulsion to prevent outflow (Japanese Patent Publication No. 61-11590).
Reference). However, in this method, the emulsion is relatively easily broken by an external impact or the like, so that the growth factor may diffuse into water. Further, in order to form an emulsion, it is necessary to add a chemical such as an activator, which may cause secondary environmental pollution.

【0007】[0007]

【発明が解決しようとする課題】この発明は当該分野に
おける上記諸問題を解決し、流出汚染油を油分解能を有
する微生物によって効率よく処理させると共に、二次的
な環境汚染を発生させない技術を提供するためになされ
たものである。
SUMMARY OF THE INVENTION The present invention solves the above problems in the art, and provides a technique for efficiently treating spilled contaminated oil with microorganisms having an oil decomposing ability and preventing secondary environmental pollution. It was made to do.

【0008】[0008]

【課題を解決するための手段】即ちこの発明は、油分解
能を有する微生物用増殖因子を固体状の疎水性有機化合
物によって被覆して成る微生物用疎水化増殖因子、およ
び該疎水化増殖因子を流出汚染油に、該微生物の存在下
に接触させることを特徴とする流出汚染油の処理方法に
関する。
That is, the present invention provides a hydrophobizing growth factor for microorganisms comprising a growth factor for oil-degrading microorganisms coated with a solid hydrophobic organic compound, and an outflow of the hydrophobizing growth factor. The present invention relates to a method for treating spilled contaminated oil, which comprises contacting contaminated oil in the presence of the microorganism.

【0009】本発明による疎水化増殖因子は、固体状の
疎水性有機化合物を用いて、油分解能を有する微生物用
増殖因子を被覆することによって調製される。本発明に
用いる固体状の疎水性有機化合物としては各種のワック
ス(例えば、パラフィンワックス、モンタンワックス、
カルナウバワックス等)、高級飽和脂肪酸(例えば、ラウ
リン酸、ミリスチン酸、パルミチン酸、ステアリン酸
等)、動物油(例えば、牛脂、豚脂等)等が例示される。
The hydrophobized growth factor according to the present invention is prepared by coating a microbial growth factor having oil degradability with a solid hydrophobic organic compound. As the solid hydrophobic organic compound used in the present invention, various waxes (for example, paraffin wax, montan wax,
Carnauba wax etc.), higher saturated fatty acids (eg lauric acid, myristic acid, palmitic acid, stearic acid etc.), animal oils (eg beef tallow, lard etc.) and the like.

【0010】これらの疎水性有機化合物によって被覆さ
れる増殖因子は、油分解能を有する微生物、例えば、シ
ュードモナス属(Pseudomonas)、アルトロバクター属
(Artrobacter)、アシネトバクター属(Acinetobacte
r)、コネリバクテリウム属(Corynebacterium)、フラボ
バクテリウム属(Flavobacterium)等の細菌のいずれか
の増殖因子であればよく、特に限定的ではないが、燐酸
−カリウム、燐酸二カリウム、燐一ナトリウム、燐酸二
ナトリウムおよび燐酸アンモニウム等の燐酸塩、硝酸ア
ンモニウム、硝酸ナトリウム、硝酸カリウム、尿素、ア
ミノ酸、ペプチドおよびタンパク質等の含窒素化合物、
ビオチン、パントテン酸、葉酸、ナイアシン、アミノ安
息香酸、ピリドキシン、リボフラビンおよびチアミン等
のビタミンが例示される。なお、このような油分解能を
有する微生物は一般に自然界の土壌中に広く存在するも
のであり、当業者であれば、所望により、容易に培養し
て利用し得る微生物である。
Growth factors coated with these hydrophobic organic compounds are microorganisms having oil degrading ability, for example, Pseudomonas spp., Arthrobacter spp.
(Artrobacter), Acinetobacte genus (Acinetobacte
r), a bacterium of the genus Corynebacterium (Corynebacterium), a genus of Flavobacterium (Flavobacterium), or the like, and may be any growth factor, but is not particularly limited. , Phosphates such as disodium phosphate and ammonium phosphate, nitrogen-containing compounds such as ammonium nitrate, sodium nitrate, potassium nitrate, urea, amino acids, peptides and proteins,
Examples include vitamins such as biotin, pantothenic acid, folic acid, niacin, aminobenzoic acid, pyridoxine, riboflavin and thiamine. It should be noted that microorganisms having such oil-degrading properties are generally widely present in natural soil, and those skilled in the art can easily culture and utilize the microorganisms if desired.

【0011】上記の固体状の疎水性有機化合物を用いて
微生物用増殖因子を被覆する一般的な方法は、該増殖因
子とワックス等の固体状疎水性有機化合物を、該疎水性
有機化合物の融点以上の温度下で混合する方法である。
疎水性有機化合物の被覆層の厚さは、該疎水性有機化合
物の種類、被処理汚染油の種類、汚染油の流出した場所
や時期等に応じて適宜選定すればよく、特に限定的では
ないが、一般的には0.001〜1mm、好ましくは0.0
1〜0.1mmである。該被覆層が薄過ぎると、微生物増
殖因子が流出し、逆に厚過ぎると、微生物がこれを利用
できない。増殖因子が液体の場合または増殖因子を溶液
として使用する場合には、自体公知のマイクロカプセル
化法によって、該増殖因子を上記疎水性有機化合物を用
いてマイクロカプセル化すればよい。なお、上記の固体
状の疎水性有機化合物と増殖因子は所望により、2種以
上適宜併用してもよい。また、本発明による微生物用疎
水化増殖因子の粒径も特に限定的ではないが、通常は
0.05〜5mm、好ましくは0.1〜1mmである。該粒径
が小さ過ぎると、微生物増殖因子の相対含量が低下し、
逆に大き過ぎると、微生物による利用効率が低下する。
A general method of coating a growth factor for microorganisms with the above solid hydrophobic organic compound is to add the growth factor and a solid hydrophobic organic compound such as wax to the melting point of the hydrophobic organic compound. This is a method of mixing at the above temperature.
The thickness of the coating layer of the hydrophobic organic compound may be appropriately selected according to the type of the hydrophobic organic compound, the type of the contaminated oil to be treated, the place or time when the contaminated oil flows out, and is not particularly limited. However, it is generally 0.001 to 1 mm, preferably 0.0
It is 1 to 0.1 mm. If the coating layer is too thin, the microbial growth factor will flow out, and if it is too thick, the microorganism will not be able to utilize it. When the growth factor is a liquid or when the growth factor is used as a solution, the growth factor may be microencapsulated using the above hydrophobic organic compound by a microencapsulation method known per se. If desired, the solid hydrophobic organic compound and the growth factor may be used in combination of two or more kinds. The particle size of the hydrophobizing growth factor for microorganisms according to the present invention is not particularly limited, but is usually 0.05 to 5 mm, preferably 0.1 to 1 mm. If the particle size is too small, the relative content of microbial growth factor decreases,
On the other hand, if it is too large, the utilization efficiency by microorganisms decreases.

【0012】本発明による微生物用疎水化増殖因子を用
いて流出汚染油を処理する方法は2つに大別される。第
一の態様は、海や河川等に流出した汚染油に、油分解能
を有する上記微生物と共に、本発明による疎水化増殖因
子を散布する方法である。第二の態様は、石油備蓄基地
や工事現場等の土壌に滲入した汚染油に本発明による疎
水化増殖因子を散布する方法である(この場合、油分解
能を有する微生物は土壌中に存在するものを利用すれば
よいが、所望により、培養した微生物を散布してもよ
い)。
The method for treating spilled contaminated oil using the hydrophobizing growth factor for microorganisms according to the present invention is roughly classified into two. The first aspect is a method of spraying a contaminated oil that has flowed out to the sea, rivers, etc., with the above-mentioned microorganism having an oil-degrading property and the hydrophobizing growth factor according to the present invention. The second aspect is a method of spraying the contaminated oil that has infiltrated into the soil such as an oil storage base or a construction site with the hydrophobizing growth factor according to the present invention (in this case, a microorganism having an oil degrading property is present in the soil). However, cultured microorganisms may be sprayed if desired).

【0013】本発明による疎水化増殖因子はそのまま流
出汚染油に散布することも可能であるが、通常は、水性
媒体に分散懸濁させた懸濁液として使用する。該増殖因
子の分散濃度は特に限定的ではないが、一般的には10
〜70重量%、特に30〜50重量%である。このよう
な疎水化増殖因子の水性懸濁液の散布量は、被処理汚染
油の種類や量、汚染油の流出した場所や時期、等に応じ
て適宜選定すればよく、特に限定的ではないが、例え
ば、40〜50重量%の懸濁液の場合には、流出汚染油
1lあたり、200〜1000mlである。本発明による
疎水化増殖因子は外部からの衝撃(例えば、波浪等)によ
って容易に破壊されることはなく、増殖因子は流出汚染
油中において経時的に徐放されて油分解能を有する微生
物に供給され、該微生物の増殖が効果的におこなわれる
ために、流出汚染油の分解処理は効率よくおこなわれ
る。また、増殖因子の被覆剤としての疎水性有機化合物
は該流出汚染油に溶解し、微生物によって分解されるた
め、二次的な環境汚染をもたらすことはない。
Although the hydrophobized growth factor according to the present invention can be directly applied to the spilled contaminated oil, it is usually used as a suspension in which it is dispersed and suspended in an aqueous medium. The dispersed concentration of the growth factor is not particularly limited, but is generally 10
-70% by weight, especially 30-50% by weight. The amount of such an aqueous suspension of hydrophobized growth factor to be sprayed may be appropriately selected according to the type and amount of the contaminated oil to be treated, the place and the time when the contaminated oil flows out, and is not particularly limited. Is 40 to 50% by weight, for example, 200 to 1000 ml per liter of contaminated oil spilled. The hydrophobized growth factor according to the present invention is not easily destroyed by an external impact (e.g., wave), and the growth factor is gradually released in spilled contaminated oil over time and supplied to a microorganism having oil degradability. Therefore, the spilled oil is efficiently decomposed because the microorganisms are effectively propagated. Further, since the hydrophobic organic compound as a growth factor coating agent is dissolved in the spilled contaminated oil and decomposed by microorganisms, secondary environmental pollution is not brought about.

【0014】[0014]

【実施例】以下、本発明を実施例によって説明する。実施例1 硝酸アンモニウム5g、燐酸一カリウム0.4g、燐酸二
ナトリウム1.7g、硫酸マグネシウム七水和物0.5g
およびパラフィン4gを加熱下(60〜80℃)で混合す
ることによって、本発明による疎水化増殖因子を調製し
た。蒸留水50mlにD−スピンドル油0.5mlを添加し
た後、上記の疎水化増殖因子1gを加えた(水面に浮遊す
る油は疎水化増殖因子によって吸収された)。この混合
物を約5分間激しく振盪した後の水層中には、アンモニ
ウムイオン、燐酸イオン、カリウムイオン、ナトリウム
イオンおよびマグネシウムイオンは検出されなかった。
EXAMPLES The present invention will be described below with reference to examples. Example 1 Ammonium nitrate 5 g, monopotassium phosphate 0.4 g, disodium phosphate 1.7 g, magnesium sulfate heptahydrate 0.5 g
The hydrophobized growth factor according to the invention was prepared by mixing and 4 g of paraffin under heat (60-80 ° C.). After adding 0.5 ml of D-spindle oil to 50 ml of distilled water, 1 g of the above-mentioned hydrophobizing growth factor was added (the oil floating on the water surface was absorbed by the hydrophobizing growth factor). No ammonium ion, phosphate ion, potassium ion, sodium ion or magnesium ion was detected in the aqueous layer after the mixture was vigorously shaken for about 5 minutes.

【0015】比較例1 硝酸アンモニウム5g、燐酸一カリウム0.4g、燐酸二
ナトリウム1.7gおよび硫酸マグネシウム七水和物
0.5gを蒸留水に溶解させ、全体で100gの水溶液を
調製した。該水溶液40g、オレイン酸20g、ラウリル
アルコール・エチレンオキシド4モル付加物およびブト
キシエタノール10gを混合することによって、W/O
型エマルションを調製した。蒸留水100mlに該エマル
ション1gを添加して約5分間激しく振盪した後、遠心
分離処理(3000g)に10分間付し、水層中のアンモ
ニウムイオンと燐酸イオンを分析したところ、約91%
のアンモニウムイオンと約96%燐酸イオンが水層中に
移行したことが認められた。
Comparative Example 1 5 g of ammonium nitrate, 0.4 g of monopotassium phosphate, 1.7 g of disodium phosphate and 0.5 g of magnesium sulfate heptahydrate were dissolved in distilled water to prepare an aqueous solution of 100 g in total. By mixing 40 g of the aqueous solution, 20 g of oleic acid, 4 mol of lauryl alcohol / ethylene oxide adduct and 10 g of butoxyethanol, W / O
A type emulsion was prepared. After adding 1 g of the emulsion to 100 ml of distilled water and shaking vigorously for about 5 minutes, centrifugation treatment (3000 g) was applied for 10 minutes, and ammonium ion and phosphate ion in the aqueous layer were analyzed and found to be about 91%.
It was confirmed that ammonium ion and about 96% of phosphate ion were transferred into the aqueous layer.

【0016】実施例2 カゼイン8gおよびパラフィン2gを加熱下(60〜80
℃)で混合することによって疎水化増殖因子を調製し
た。滅菌した海水または水道水100mlにD−スピンド
ル油、灯油、ナフテン系マシン油、C重油または原油1
00〜500mg加えた混合物に油分解能を有する菌株シ
ュードモナス・フルオレセンス(Pseudomonas fluores
ens)(ATCC31483)を接種するか、または該混合
物に上記の疎水化増殖因子100mgをさらに添加した混
合物に該菌株を接種した後、30℃において振盪培養を
1週間おこなった。培養後、n−ヘキサンとトルエンと
の6:4混合溶媒を用いて油分を抽出し、該溶媒を除去
した後、抽出油分の重量を測定し、結果を表1に示す。
Example 2 8 g of casein and 2 g of paraffin were heated (60 to 80).
Hydrophobicized growth factor was prepared by mixing at (° C). 100 ml of sterilized seawater or tap water, D-spindle oil, kerosene, naphthenic machine oil, C heavy oil or crude oil 1
The strain Pseudomonas fluorescens (Pseudomonas fluorescens), which has oil-degrading ability, was added to a mixture containing 0 to 500 mg.
ens) (ATCC31483) or a mixture obtained by further adding 100 mg of the above-mentioned hydrophobizing growth factor to the mixture, the strain was inoculated, and shaking culture was carried out at 30 ° C. for 1 week. After culturing, the oil was extracted using a 6: 4 mixed solvent of n-hexane and toluene, the solvent was removed, and the weight of the extracted oil was measured. The results are shown in Table 1.

【0017】[0017]

【表1】 [Table 1]

【0018】実施例3 硝酸アンモニウム5g、燐酸一カリウム0.4g、燐酸二
ナトリウム1.7g、硫酸マグネシウム七水和物0.5
g、酵母エキス1gおよびパラフィン2gを加熱下(60〜
80℃)で混合することによって疎水化増殖因子を調製
した。水道水50mlにマシン油またはナフテン系マシン
油500mgおよび上記の疎水化増殖因子500mgを添加
した混合物に油分解能を有する菌株シュードモナス・フ
ルオレセンス(ATCC31483)を接種した後、25
℃において静置培養をおこなった。1カ月後、2カ月後
および3カ月後、n−ヘキサンとトルエンとの6:4混合
溶媒を用いて油分を抽出し、該溶媒を除去した後、抽出
油分の重量を測定し、結果を表2に示す。
Example 3 Ammonium nitrate 5 g, monopotassium phosphate 0.4 g, disodium phosphate 1.7 g, magnesium sulfate heptahydrate 0.5
g, yeast extract 1 g and paraffin 2 g under heating (60-
The hydrophobized growth factor was prepared by mixing at 80 ° C. After inoculating a mixture obtained by adding 500 mg of machine oil or naphthenic machine oil and 500 mg of the above-mentioned hydrophobizing growth factor to 50 ml of tap water, a strain Pseudomonas fluorescens (ATCC31483) having an oil degrading ability was inoculated,
Static culture was performed at ℃. After 1 month, 2 months and 3 months, an oil component was extracted using a 6: 4 mixed solvent of n-hexane and toluene, the solvent was removed, and then the weight of the extracted oil component was measured. 2 shows.

【0019】[0019]

【表2】 [Table 2]

【0020】比較例2 パラフィンを使用しない以外は実施例3と同様の手順に
準拠した測定をおこなった。結果を表2に示す。
Comparative Example 2 Measurement was carried out according to the same procedure as in Example 3 except that paraffin was not used. Table 2 shows the results.

【0021】比較例3 増殖因子およびパラフィンを使用しない以外は実施例3
と同様の手順に準拠した測定をおこなった。結果を表2
に示す。
Comparative Example 3 Example 3 except that growth factors and paraffin were not used.
The measurement was carried out according to the same procedure as in. Table 2 shows the results
Shown in

【0022】実施例4 硝酸アンモニウム5g、燐酸一カリウム0.4g、燐酸二
ナトリウム1.7g、硫酸マグネシウム七水和物0.5
g、酵母エキス1gおよびステアリン酸2gを加熱下(70
〜80℃)で混合することによって疎水化増殖因子を調
製した。試料管に採取した土壌約30mlにD−スピンド
ル油またはナフテン系マシン油500mgを含浸させ、こ
れに、上記疎水化増殖因子5gを水道水10mlに懸濁さ
せた懸濁液0.5mlを添加した試料を25℃で2カ月間
静置した後、n−ヘキサンとトルエンとの6:4混合溶媒
を用いて油分を抽出し、該溶媒を除去して抽出油分の重
量を測定した。結果を表3に示す。
Example 4 Ammonium nitrate 5 g, monopotassium phosphate 0.4 g, disodium phosphate 1.7 g, magnesium sulfate heptahydrate 0.5
g, yeast extract 1 g and stearic acid 2 g under heating (70
Hydrophobized growth factors were prepared by mixing at ~ 80 ° C). About 30 ml of the soil collected in the sample tube was impregnated with 500 mg of D-spindle oil or naphthenic machine oil, and 0.5 ml of a suspension obtained by suspending 5 g of the hydrophobizing growth factor in 10 ml of tap water was added thereto. After allowing the sample to stand at 25 ° C. for 2 months, an oil component was extracted using a 6: 4 mixed solvent of n-hexane and toluene, the solvent was removed, and the weight of the extracted oil component was measured. The results are shown in Table 3.

【0023】[0023]

【表3】 [Table 3]

【0024】比較例4 ステアリン酸を使用しない以外は実施例4と同様の手順
に準拠した測定をおこなった。結果を表3に示す。
Comparative Example 4 Measurement was carried out according to the same procedure as in Example 4 except that stearic acid was not used. The results are shown in Table 3.

【0025】比較例5 増殖因子およびステアリン酸を使用しない以外は実施例
4と同様の手順に準拠した測定をおこなった。結果を表
3に示す。
Comparative Example 5 Measurement was carried out according to the same procedure as in Example 4 except that growth factors and stearic acid were not used. The results are shown in Table 3.

【0026】[0026]

【発明の効果】本発明による疎水化増殖因子を使用する
ことによって、二次的な環境汚染を発生させることな
く、流出汚染油を微生物によって効率よく分解処理させ
ることが可能となる。
EFFECTS OF THE INVENTION By using the hydrophobizing growth factor according to the present invention, it becomes possible to efficiently decompose spilled contaminated oil by microorganisms without causing secondary environmental pollution.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C12R 1:39) ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display C12R 1:39)

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 油分解能を有する微生物用増殖因子を固
体状の疎水性有機化合物によって被覆して成る微生物用
疎水化増殖因子。
1. A hydrophobizing growth factor for microorganisms, which is obtained by coating a growth factor for oil-degrading microorganisms with a solid hydrophobic organic compound.
【請求項2】 固体状の疎水性有機化合物がワックスま
たは高級飽和脂肪酸である請求項1記載の疎水化増殖因
子。
2. The hydrophobized growth factor according to claim 1, wherein the solid hydrophobic organic compound is wax or higher saturated fatty acid.
【請求項3】 請求項1または2記載の疎水化増殖因子
を流出汚染油に、油分解能を有する微生物の存在下で接
触させることを特徴とする流出汚染油の処理方法。
3. A method for treating spilled contaminated oil, which comprises contacting the hydrophobized growth factor according to claim 1 or 2 with the spilled contaminated oil in the presence of a microorganism capable of degrading oil.
JP16197594A 1994-07-14 1994-07-14 Proliferation factor of microorganism made hydrophobic Pending JPH0823965A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16197594A JPH0823965A (en) 1994-07-14 1994-07-14 Proliferation factor of microorganism made hydrophobic

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16197594A JPH0823965A (en) 1994-07-14 1994-07-14 Proliferation factor of microorganism made hydrophobic

Publications (1)

Publication Number Publication Date
JPH0823965A true JPH0823965A (en) 1996-01-30

Family

ID=15745644

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16197594A Pending JPH0823965A (en) 1994-07-14 1994-07-14 Proliferation factor of microorganism made hydrophobic

Country Status (1)

Country Link
JP (1) JPH0823965A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6468675B1 (en) 1998-05-29 2002-10-22 Nec Corporation Organic electroluminescent device having high luminance efficiency
JP2010269244A (en) * 2009-05-21 2010-12-02 Ecocycle Corp Additive and method for cleaning medium contaminated with mineral oil
JP2012040527A (en) * 2010-08-20 2012-03-01 Yoshiro Yamaguchi Textile disposable toiletry, and method for microbiologically treating organic wastewater using the same

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6468675B1 (en) 1998-05-29 2002-10-22 Nec Corporation Organic electroluminescent device having high luminance efficiency
JP2010269244A (en) * 2009-05-21 2010-12-02 Ecocycle Corp Additive and method for cleaning medium contaminated with mineral oil
TWI450745B (en) * 2009-05-21 2014-09-01 Ecocycle Corp Additives for cleaning mineral oil-contaminated medium and cleaning method
JP2012040527A (en) * 2010-08-20 2012-03-01 Yoshiro Yamaguchi Textile disposable toiletry, and method for microbiologically treating organic wastewater using the same

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