JPH0220234B2 - - Google Patents
Info
- Publication number
- JPH0220234B2 JPH0220234B2 JP14079781A JP14079781A JPH0220234B2 JP H0220234 B2 JPH0220234 B2 JP H0220234B2 JP 14079781 A JP14079781 A JP 14079781A JP 14079781 A JP14079781 A JP 14079781A JP H0220234 B2 JPH0220234 B2 JP H0220234B2
- Authority
- JP
- Japan
- Prior art keywords
- edta
- bacteria
- culture
- medium
- pseudomonas
- 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.)
- Expired
Links
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 claims description 46
- 241000894006 Bacteria Species 0.000 claims description 29
- 238000000354 decomposition reaction Methods 0.000 claims description 11
- 241000588986 Alcaligenes Species 0.000 claims description 10
- 241000589516 Pseudomonas Species 0.000 claims description 10
- 150000003839 salts Chemical class 0.000 claims description 5
- 150000001875 compounds Chemical class 0.000 claims description 4
- 150000004696 coordination complex Chemical class 0.000 claims description 2
- 238000003672 processing method Methods 0.000 claims 1
- 239000002609 medium Substances 0.000 description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 7
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 6
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 6
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- 238000011282 treatment Methods 0.000 description 6
- 230000001580 bacterial effect Effects 0.000 description 5
- 238000000034 method Methods 0.000 description 5
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 description 4
- 239000011575 calcium Substances 0.000 description 4
- 244000005700 microbiome Species 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 3
- OVBJJZOQPCKUOR-UHFFFAOYSA-L EDTA disodium salt dihydrate Chemical compound O.O.[Na+].[Na+].[O-]C(=O)C[NH+](CC([O-])=O)CC[NH+](CC([O-])=O)CC([O-])=O OVBJJZOQPCKUOR-UHFFFAOYSA-L 0.000 description 3
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 3
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 3
- 229910052791 calcium Inorganic materials 0.000 description 3
- 229910052799 carbon Inorganic materials 0.000 description 3
- 238000012258 culturing Methods 0.000 description 3
- 239000012153 distilled water Substances 0.000 description 3
- 229910052742 iron Inorganic materials 0.000 description 3
- 239000007788 liquid Substances 0.000 description 3
- 239000011777 magnesium Substances 0.000 description 3
- 229910052749 magnesium Inorganic materials 0.000 description 3
- 239000013028 medium composition Substances 0.000 description 3
- 229910052757 nitrogen Inorganic materials 0.000 description 3
- LWIHDJKSTIGBAC-UHFFFAOYSA-K potassium phosphate Substances [K+].[K+].[K+].[O-]P([O-])([O-])=O LWIHDJKSTIGBAC-UHFFFAOYSA-K 0.000 description 3
- 239000013535 sea water Substances 0.000 description 3
- 229910052725 zinc Inorganic materials 0.000 description 3
- 239000011701 zinc Substances 0.000 description 3
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 2
- 238000003794 Gram staining Methods 0.000 description 2
- 229910021380 Manganese Chloride Inorganic materials 0.000 description 2
- GLFNIEUTAYBVOC-UHFFFAOYSA-L Manganese chloride Chemical compound Cl[Mn]Cl GLFNIEUTAYBVOC-UHFFFAOYSA-L 0.000 description 2
- ZOKXTWBITQBERF-UHFFFAOYSA-N Molybdenum Chemical compound [Mo] ZOKXTWBITQBERF-UHFFFAOYSA-N 0.000 description 2
- 229910019142 PO4 Inorganic materials 0.000 description 2
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical class [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 2
- 241001214115 Pseudoalteromonas mariniglutinosa Species 0.000 description 2
- 239000001110 calcium chloride Substances 0.000 description 2
- 229910001628 calcium chloride Inorganic materials 0.000 description 2
- 229940041514 candida albicans extract Drugs 0.000 description 2
- 238000005119 centrifugation Methods 0.000 description 2
- 238000012136 culture method Methods 0.000 description 2
- ZPWVASYFFYYZEW-UHFFFAOYSA-L dipotassium hydrogen phosphate Chemical compound [K+].[K+].OP([O-])([O-])=O ZPWVASYFFYYZEW-UHFFFAOYSA-L 0.000 description 2
- 235000019797 dipotassium phosphate Nutrition 0.000 description 2
- 229910000396 dipotassium phosphate Inorganic materials 0.000 description 2
- 239000004744 fabric Substances 0.000 description 2
- 239000001963 growth medium Substances 0.000 description 2
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 2
- 235000019341 magnesium sulphate Nutrition 0.000 description 2
- 239000011565 manganese chloride Substances 0.000 description 2
- 235000002867 manganese chloride Nutrition 0.000 description 2
- 229940099607 manganese chloride Drugs 0.000 description 2
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 229910052750 molybdenum Inorganic materials 0.000 description 2
- 239000011733 molybdenum Substances 0.000 description 2
- 239000010452 phosphate Substances 0.000 description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 description 2
- 230000001766 physiological effect Effects 0.000 description 2
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 description 2
- 239000011591 potassium Chemical class 0.000 description 2
- 229910052700 potassium Inorganic materials 0.000 description 2
- 235000011121 sodium hydroxide Nutrition 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000012138 yeast extract Substances 0.000 description 2
- ONDPHDOFVYQSGI-UHFFFAOYSA-N zinc nitrate Chemical compound [Zn+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O ONDPHDOFVYQSGI-UHFFFAOYSA-N 0.000 description 2
- 241000588813 Alcaligenes faecalis Species 0.000 description 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical class [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 108010010803 Gelatin Proteins 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical class C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- 239000001888 Peptone Substances 0.000 description 1
- 108010080698 Peptones Proteins 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 229940005347 alcaligenes faecalis Drugs 0.000 description 1
- 150000003863 ammonium salts Chemical class 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000000721 bacterilogical effect Effects 0.000 description 1
- 239000011203 carbon fibre reinforced carbon Substances 0.000 description 1
- 239000003518 caustics Substances 0.000 description 1
- 239000002738 chelating agent Substances 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 150000001805 chlorine compounds Chemical class 0.000 description 1
- 229910017052 cobalt Inorganic materials 0.000 description 1
- 239000010941 cobalt Substances 0.000 description 1
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 150000004683 dihydrates Chemical class 0.000 description 1
- 238000007865 diluting Methods 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 239000000284 extract Substances 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 238000004817 gas chromatography Methods 0.000 description 1
- 229920000159 gelatin Polymers 0.000 description 1
- 239000008273 gelatin Substances 0.000 description 1
- 235000019322 gelatine Nutrition 0.000 description 1
- 235000011852 gelatine desserts Nutrition 0.000 description 1
- 239000002054 inoculum Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 235000013372 meat Nutrition 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 239000011785 micronutrient Substances 0.000 description 1
- 235000013369 micronutrients Nutrition 0.000 description 1
- 229910000402 monopotassium phosphate Inorganic materials 0.000 description 1
- 235000019796 monopotassium phosphate Nutrition 0.000 description 1
- 150000004767 nitrides Chemical class 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 235000019319 peptone Nutrition 0.000 description 1
- 239000008363 phosphate buffer Substances 0.000 description 1
- PJNZPQUBCPKICU-UHFFFAOYSA-N phosphoric acid;potassium Chemical compound [K].OP(O)(O)=O PJNZPQUBCPKICU-UHFFFAOYSA-N 0.000 description 1
- 229910052697 platinum Inorganic materials 0.000 description 1
- 229910001414 potassium ion Inorganic materials 0.000 description 1
- 229910000160 potassium phosphate Inorganic materials 0.000 description 1
- 235000011009 potassium phosphates Nutrition 0.000 description 1
- 230000035755 proliferation Effects 0.000 description 1
- 238000011218 seed culture Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- 159000000000 sodium salts Chemical class 0.000 description 1
- 235000019698 starch Nutrition 0.000 description 1
- 239000008107 starch Substances 0.000 description 1
- 150000003467 sulfuric acid derivatives Chemical class 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- RZLVQBNCHSJZPX-UHFFFAOYSA-L zinc sulfate heptahydrate Chemical compound O.O.O.O.O.O.O.[Zn+2].[O-]S([O-])(=O)=O RZLVQBNCHSJZPX-UHFFFAOYSA-L 0.000 description 1
Landscapes
- Preparation Of Compounds By Using Micro-Organisms (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Description
本発明は細菌によりエチレンジアミン四酢酸を
分解する方法に関する。エチレンジアミン四酢酸
(以下EDTAと略記する)は、種々な金属と強固
な錯化合物を形成するキレート剤として知られ、
工業、濃水産業、医薬などの分野で大量に使用さ
れているが、EDTAが工場などの廃水中に含有
されると海水、湖水などの富栄養化など環境汚染
への影響が問題になる。従つて、EDTAの有効
な分解処理が望まれるのであるが、EDTAは従
来より微生物による分解が困難な物質として知ら
れている。
EDTAは紫外線と活性塩素などの化学的処理
で分解できることが知られているが(例えば特開
昭51−31052号参照)、この方法は工程管理が難し
く、特定の設備を必要とし、またコストが比較的
高くつくなどの欠点を有している。またEDTA
は土壤中の微生物〔テイージエのアプライド・マ
クロバイオロジー第30巻第2号第327頁〜第329頁
(1975年)参照〕、EDTAの流入するバツ気式ラ
グーン中の微生物〔ベリー等のアブライド・マイ
クロバイオロジー第29巻第6号第787頁〜第794頁
(1975年)〕、活性汚泥(米沢等の公害資源研究所
彙第6巻第4号第15頁〜第21頁(昭和52年)〕に
より分解されることが認められているが、数週間
にもおよぶ長期培養や処理にも拘らず、その分解
力は極めて弱いので実用的ではなく、微生物によ
る効果的なEDTAの分解方法が望まれている。
かかる観点から本発明者等は広く自然界り
EDTA資化菌を求めた結果、EDTAを単一炭素
源および単一窒素源とする培地で成長しうるシユ
ードモナス(Pseudomonas)属に属する細菌お
よびアルカリゲネス(Alcaligeness)属に属する
細菌が存在すると、およびかかる細菌により
EDTAが資化分解されることとを見出し本発明
を達成した。
即ち本発明はEDTAを分解する能力を有する
シユードモナス属に属する細菌またはアルカリゲ
ネス属に属する細菌をEDTA、その金属錯体ま
たはこれらの塩類に接触させることを特徴とする
ものである。
ここにEDTAの資化とは菌体が炭素源、窒素
源としてEDTAを摂取して消費し増殖する現象
を意味するのであつて、単にEDTAの炭素−炭
素結合、炭素−窒素結合が切断されることを意味
するものではない。
本発明で用いられる細菌は土壤、河川水、海水
など広く自然界から採取し得るが、具体的には例
えばシユードモナス(Pseudomonas)No.51−Y
(微工研菌寄第6103号)、アルカリゲネス
(Alcaligenes)No.51−z(微工研菌寄第6104号)
が挙げられる。なおシユードモナスNo.51−Y、ア
ルカリゲネスNo.51−zの菌学的性質について述べ
ると第1表の如くである。菌学的性質の試験およ
び分類はバージエース、マニユアル・オブ・バタ
ーミネイテイブ・バクテリオロジー(Bergey′s、
Manual of Determinative Bactariology)第7
版および第8版に基づいて行なつた。
The present invention relates to a method for decomposing ethylenediaminetetraacetic acid by bacteria. Ethylenediaminetetraacetic acid (hereinafter abbreviated as EDTA) is known as a chelating agent that forms strong complex compounds with various metals.
It is used in large quantities in industries, concentrated water industries, medicine, and other fields, but if EDTA is contained in wastewater from factories, it can cause environmental pollution such as eutrophication of seawater and lake water. Therefore, an effective decomposition treatment for EDTA is desired, but EDTA has been known as a substance that is difficult to decompose by microorganisms. It is known that EDTA can be decomposed by chemical treatments such as ultraviolet light and active chlorine (for example, see Japanese Patent Application Laid-open No. 51-31052), but this method is difficult to control, requires specific equipment, and is expensive. It has drawbacks such as being relatively expensive. Also EDTA
microorganisms in the soil [see Teisier's Applied Macrobiology Vol. Microbiology Vol. 29 No. 6 No. 787-794 (1975)], activated sludge (Yonezawa et al. Pollution Resources Research Institute Vol. 6 No. 4 No. 15-21 (1975) )], but despite long-term cultivation and treatment for several weeks, its decomposition power is extremely weak and is not practical, and there is no effective method for decomposing EDTA using microorganisms. From this perspective, the present inventors have widely studied the natural world.
As a result of searching for EDTA-assimilating bacteria, it was found that there are bacteria belonging to the genus Pseudomonas and bacteria belonging to the genus Alcaligeness that can grow in a medium using EDTA as a sole carbon source and a sole nitrogen source, and by bacteria
The present invention was achieved by discovering that EDTA is assimilated and decomposed. That is, the present invention is characterized in that bacteria belonging to the genus Pseudomonas or bacteria belonging to the genus Alcaligenes, which have the ability to decompose EDTA, are brought into contact with EDTA, a metal complex thereof, or a salt thereof. Here, EDTA assimilation refers to the phenomenon in which bacterial cells take in EDTA as a carbon source and nitrogen source, consume it, and proliferate, and the carbon-carbon bond and carbon-nitrogen bond of EDTA are simply broken. It does not mean that. Bacteria used in the present invention can be collected from a wide range of sources in the natural world, such as soil, river water, and seawater, but specifically, for example, Pseudomonas No.51-Y
(Feikoken Bibori No. 6103), Alcaligenes No. 51-z (Feikoku Kenbibi No. 6104)
can be mentioned. The mycological properties of Pseudomonas No. 51-Y and Alcaligenes No. 51-z are as shown in Table 1. Mycological testing and classification is carried out by Bergey's Manual of Bacteriological Bacteriology.
Manual of Determinative Bactariology) No. 7
8th edition.
【表】【table】
【表】【table】
【表】【table】
【表】【table】
【表】【table】
【表】【table】
【表】
以上の菌学的性質に基づき、シユードモナスNo.
51−Y株およびアルカリゲネスNo.51−z株の同定
を行なつた。
シユードモナスNo.51−Y株は、菌の形態、グラ
ム染色などの顕微鏡的処見、生理学的諸性質、お
よび海水から分離されたことなどから、バージエ
ース、マニユアル・オブ・デターミネイテイブ・
バクテリオロジー第7版および第8版に基づき、
シユードモナス・マリノグルチノーサに近縁の菌
と同定された。しかしながらシユードモナスNo.51
−Y株はゼラチンを液化しない、澱粉を分解しな
いなどの点で明らかにシユードモナス・マリノグ
ルチノーサとは区別される。
またアルカリゲネスNo.51−Z株は菌の形態、グ
ラム染色などの顕微鏡的処見、および生理学的諸
性質からアルカリゲネス属細菌と同定され、ゼラ
チンと液化せず、運動性があるなどの性質から、
バージエース、マニユアル・オブ・デターミネイ
テイブ・バクテリオロジー第7版および第8版の
分類に記載されたアルカリゲネス・フエカリスに
類似の菌と同定された。
本発明は上記発見に基づいてなされたもので
EDTAにこれらの菌を接触せしめることを特徴
とするEDTAの微生物分解処理方法を提供する
ものである。
本発明でいうEDTAとはEDTAの遊離酸、マ
グネシウム、カルシウム、鉄、コバルト、亜鉛、
銅などとの錯化合物、およびナトリウム、カリウ
ム、アンモニウム等の塩など全てを含み、これら
の化合物は被処理物中に単独でまたは混合して存
在してもよい。
また本発明によるEDTAの分解の程度は
EDTAの減少の度合または菌体の増殖度の程度
で示される。
本発明は例えばEDTAを炭素源および窒素源
とし、リン酸塩、カリウム、マグネシウム、カル
シウム、鉄、マンガン、亜鉛、モリブデンなどの
無機塩類を含む培地(EDTAを含有被処理液)
中にて前記菌を生育させることにより実施でき
る。この場合必要に応じて酵母エキスなどの有機
微量栄養素を添加すると菌の増殖は促進される。
リン酸イオンおよびカリウムイオンは通常のリ
ン酸1水素カリウムまたはリン酸2水素カリウム
の形で使用される。またカルシウム、マグネシウ
ム、鉄、マンガン、亜鉛、モリブデンなどの無機
金属塩類は、塩化物、硫酸塩、硝化物、酸化物な
どの形で使用される。
ペプトン、肉エキスなどのEDTA以外の栄養
分豊かな培地に菌を植え継ぐと、EDTAの分解
能は低下することがあるので好ましくない。
培養または処理温度は20〜37℃、培地
(EDTA含有処理液)のPHは5.0〜9.0が適当であ
るが、より好適には培養温度30℃、培地のPHは
7.0付近が良い。
培養または処理は静置、振盪または通気撹拌す
ることにより行なわれ、酸素を非常に消費し易い
条件下ではEDTAの資化速度は早い。暗所や密
閉培養槽など光の当らない条件下でも良好に菌を
生育させることができるが、光の当る条件の下で
は、更に菌の増殖速度が早く、通常4〜7日で培
養され、培地中のEDTAの濃度を経時的に減少
させることができる。
更に本発明方法を実施するに当り、予めこれら
の微生物を適当な培地にて培養させた培養物、ま
たは要すれば遠心分離法、過法などにより濃縮
した菌体区分をEDTAと接触させても目的を達
成することができる。この場合には菌を増殖させ
る必要はないが、適宜撹拌しながら溶液中の組成
を均一に保持するとEDTAの分解に好適である。
なお本発明で記載するEDTAの量は、ガスク
ロマトグラフイー(ルーデイング等のウオータ
ー・リサーチ・ベルガモン・プレス第6巻第871
頁〜第876頁、1972)を、用いて測定し、減少し
たEDTAの割合を分解率として表示した。また
菌数測定は顕微鏡法で行なつた。
次に本発明を実施例を挙げて説明する。
実施例 1
EDTA2ナトリウム・2水塩 1.86g
リン酸2カリウム(K2HPO4) 8.7g
硫酸マグネシウム(MgSO4・7H2O) 0.24g
塩化カルシウム(CaCl2・2H2O) 0.5mg
塩化マンガン(MnCl2・4H2O) 3mg
硝酸亜鉛(ZnSO4・7H2O) 10mg
を蒸留水1000mlに溶解し、苛性ソードを用いてPH
を7.0に調整した。これを500ml容の坂口フラスコ
に50ml分注し、120℃、110分間殺菌して培養液と
した。この培地にシユードモナスNo.51−Y株(微
工研菌第6103号)の一白金耳を接種してフラスコ
を完全に光を透さない黒い布で覆い、30℃、150
時間往復式振盪機にかけて培養した。
EDTAの分解率および菌数を測定した結果を
第2表に示す。なお対照例として培地組成、培養
条件を同一とし、菌を接種しない場合、EDTA
の減少は全く認められなかつた。
実施例 2
実施例1に記載した培地組成、培養方法、培養
条件のうち、接種した菌をアルカリゲネスNo.51−
z株(微工研菌寄第6104号)におきかえたこと以
外は実施例1と同様にしてEDTAの減少および
菌数の測定を行なつた結果を第2表に示す。[Table] Based on the above mycological properties, Pseudomonas No.
51-Y strain and Alcaligenes No. 51-z strain were identified. Pseudomonas No. 51-Y strain was identified by Verge Ace, Manual of Determinative Research, based on its morphology, microscopic examination such as Gram staining, various physiological properties, and the fact that it was isolated from seawater.
Based on Bacteriology 7th and 8th editions,
It was identified as a bacterium closely related to Pseudomonas marinoglutinosa. However, Pseudomonas No. 51
-Y strain is clearly distinguished from Pseudomonas marinoglutinosa in that it does not liquefy gelatin or decompose starch. In addition, Alcaligenes No. 51-Z strain was identified as a bacterium belonging to the genus Alcaligenes based on its morphology, microscopic examination such as Gram staining, and various physiological properties.
It was identified as a bacterium similar to Alcaligenes faecalis described in the classification of Verge Ace, Manual of Determinative Bacteriology, 7th and 8th editions. The present invention was made based on the above discovery.
The present invention provides a method for microbial decomposition of EDTA, which is characterized by bringing these bacteria into contact with EDTA. EDTA in the present invention refers to the free acid of EDTA, magnesium, calcium, iron, cobalt, zinc,
It includes complex compounds with copper, etc., and salts of sodium, potassium, ammonium, etc., and these compounds may be present alone or in a mixture in the object to be treated. Furthermore, the degree of decomposition of EDTA according to the present invention is
It is indicated by the degree of decrease in EDTA or the degree of proliferation of bacterial cells. The present invention uses, for example, EDTA as a carbon source and nitrogen source, and a medium containing inorganic salts such as phosphate, potassium, magnesium, calcium, iron, manganese, zinc, and molybdenum (EDTA-containing liquid to be treated).
This can be carried out by growing the bacteria in the medium. In this case, if necessary, organic micronutrients such as yeast extract may be added to promote bacterial growth. Phosphate and potassium ions are used in the conventional form of potassium monohydrogen phosphate or potassium dihydrogen phosphate. Inorganic metal salts such as calcium, magnesium, iron, manganese, zinc, and molybdenum are used in the form of chlorides, sulfates, nitrides, oxides, and the like. It is not preferable to inoculate the bacteria into a medium rich in nutrients other than EDTA, such as peptone or meat extract, as the ability to decompose EDTA may decrease. The appropriate culture or treatment temperature is 20 to 37°C, and the pH of the medium (EDTA-containing treatment liquid) is 5.0 to 9.0, but more preferably the culture temperature is 30°C, and the pH of the medium is 5.0 to 9.0.
Around 7.0 is good. Cultivation or treatment is carried out by standing still, shaking or aerating, and the rate of assimilation of EDTA is rapid under conditions where oxygen is highly consumed. Bacteria can be grown well even in the dark or in closed culture tanks, where there is no light, but under light conditions, the growth rate of the bacteria is even faster, and it is usually cultured within 4 to 7 days. The concentration of EDTA in the medium can be decreased over time. Furthermore, in carrying out the method of the present invention, a culture obtained by culturing these microorganisms in an appropriate medium in advance, or a cell fraction concentrated by centrifugation, filtration, etc., if necessary, may be brought into contact with EDTA. Able to achieve purpose. In this case, it is not necessary to grow the bacteria, but it is preferable to keep the composition of the solution uniform with appropriate stirring to decompose EDTA. The amount of EDTA described in the present invention is determined by gas chromatography (Ruding et al., Water Research Bergamon Press, Vol. 6, No. 871).
876, 1972), and the percentage of EDTA reduced was expressed as the decomposition rate. Bacterial counts were also measured using a microscope. Next, the present invention will be explained by giving examples. Example 1 Disodium EDTA dihydrate 1.86g Dipotassium phosphate (K 2 HPO 4 ) 8.7g Magnesium sulfate (MgSO 4 7H 2 O) 0.24g Calcium chloride (CaCl 2 2H 2 O) 0.5mg Manganese chloride ( Dissolve 3 mg of zinc nitrate (ZnSO 4.7H 2 O ) in 1000 ml of distilled water and PH using a caustic sword.
Adjusted to 7.0. 50 ml of this was dispensed into a 500 ml Sakaguchi flask and sterilized at 120°C for 110 minutes to obtain a culture solution. A loopful of Pseudomonas strain No. 51-Y (Feikokenbacterium No. 6103) was inoculated into this medium, and the flask was completely covered with a black cloth that did not allow light to pass through.
The cells were cultured on a reciprocating shaker for hours. Table 2 shows the results of measuring the decomposition rate of EDTA and the number of bacteria. As a control example, when the medium composition and culture conditions are the same and no bacteria are inoculated, EDTA
No decrease was observed at all. Example 2 Among the culture medium composition, culture method, and culture conditions described in Example 1, the inoculated bacteria were used as Alcaligenes No. 51-
Table 2 shows the results of measuring the reduction of EDTA and the number of bacteria in the same manner as in Example 1 except that the strain was replaced with Z strain (Feikoken Bacteria No. 6104).
【表】
実施例 3
実施例1に記載した培地組成、培養方法、培養
条件のうち、培地に用いたEDTA2ナトリウム塩
を、EDTA2アンモニウム塩とした。また、光を
当てて培養する場合には、坂口フラスコを黒い布
で覆うことなく螢光灯の光を600〜800ルツクス照
射して培養した以外は実施例1と同様にして実施
し、EDTAの減少および菌数の測定を行なつた
結果、光を当てて培養した場合、EDTAの分解
率および培養液中の菌数は、光を当てない条件に
比べて著しい効果が認められた。
EDTAの分解率および培養液中の菌数の経時
変化を第3表に示す。[Table] Example 3 Of the medium composition, culture method, and culture conditions described in Example 1, the EDTA2 sodium salt used in the medium was EDTA2 ammonium salt. In addition, when culturing with light, the culture was carried out in the same manner as in Example 1 except that the Sakaguchi flask was not covered with a black cloth and the culture was irradiated with fluorescent light at 600 to 800 lux. As a result of measuring the reduction and number of bacteria, it was found that culturing with light exposure had a significant effect on the decomposition rate of EDTA and the number of bacteria in the culture solution compared to conditions without light exposure. Table 3 shows the decomposition rate of EDTA and the change over time in the number of bacteria in the culture solution.
【表】
実施例 4
EDTA2ナトリウム・2水塩 18.6g
K2HPO4 87.0g
MgSO4・7H2O 2.4g
Ca(NO3)2・4H2O 5mg
MnCl2・4H2O 30mg
ZnSO4・7H2O 100mg
を蒸留水に溶解して、苛性ソーダを用いてPHを
7.0に調整し、30容ジヤーフアーメンターに投
入後、120Kg、10分間殺菌し、液量を10とした。
別にあらかじめ用意した同上培地組成に、酵母
エキス0.01%添加した培地にアルカリゲネスNo.51
−z株(微工研菌寄第6104号)を接種して30℃、
48時間振盪培養した種母培養液20mlを上記本培養
液に移し、30℃、150時間通気撹拌培養した。培
養終了後遠心分離機を用いて菌体を集め菌体区分
を得た。
別に、EDTA2ナトリウム・2水塩186mgを
N/10リン酸緩衝液(PH7.0)に溶解し、更にPH
を7.0に調整した液を100mlとした。この溶液100
mlに上記菌体区分を全量投入分散し、30℃、120
時間ときどき撹拌しながら保持したところ、
EDTAの分解率は80%に達した。
実施例 5
カラー写真漂白定着液廃液に蒸留水を加えて稀
釈してEDTAとして約1000ppm含有する溶液を
調製した。この溶液1000mlにリン酸1カリウム
6.8g、硫酸マグネシウム・7水塩0.24g、塩化
カルシウム・2水塩0.5mg、塩化マンガン3mg、
硫酸亜鉛・7水塩10mgを添加した後、PHを水酸化
ナトリウムで7.0に調整した溶液500mlを3000ml容
坂口フラスコに入れ本培養液とした。別に実施例
1に記載した培地組成を有する培養液50mlに、シ
ユードモナスNo.51−Y株(微工研菌寄第6103号)
の斜面培養の一白金耳を接種して、30℃、150時
間往復式振盪機にかけて培養した液を無菌的に遠
心分離法で集菌し、種菌とした。この全量を上記
本培養液に加え、30℃、150時間往復式振盪機に
かけて培養した後、上澄液のEDTAの残存量か
らEDTAの分解率を測定したところ65%であつ
た。[Table] Example 4 EDTA disodium dihydrate 18.6g K 2 HPO 4 87.0g MgSO 4・7H 2 O 2.4g Ca(NO 3 ) 2・4H 2 O 5mg MnCl 2・4H 2 O 30mg ZnSO 4・7H Dissolve 100mg of 2O in distilled water and adjust the pH using caustic soda.
After adjusting to 7.0 and putting it into a 30 volume jar fermenter, it was sterilized at 120Kg for 10 minutes to make the liquid volume 10. Alcaligenes No. 51 was added to the same medium composition as above prepared separately, and 0.01% yeast extract was added to the medium.
- Inoculated with Z strain (Feikoken Bacteria No. 6104) and incubated at 30°C.
20 ml of the seed culture solution cultured with shaking for 48 hours was transferred to the above main culture solution, and cultured with aeration at 30°C for 150 hours. After the culture was completed, the cells were collected using a centrifuge and the cells were classified. Separately, dissolve 186 mg of EDTA disodium dihydrate in N/10 phosphate buffer (PH7.0), and then
The volume of the solution adjusted to 7.0 was 100 ml. This solution 100
Pour the entire amount of the above bacterial cell types into ml and disperse at 30℃ and 120℃.
After holding for a while with occasional stirring,
The decomposition rate of EDTA reached 80%. Example 5 A solution containing about 1000 ppm of EDTA was prepared by diluting the waste color photographic bleach-fix solution with distilled water. Add 1 potassium phosphate to 1000ml of this solution.
6.8g, magnesium sulfate/7hydrate 0.24g, calcium chloride/dihydrate 0.5mg, manganese chloride 3mg,
After adding 10 mg of zinc sulfate heptahydrate, 500 ml of the solution whose pH was adjusted to 7.0 with sodium hydroxide was placed in a 3000 ml Sakaguchi flask to serve as the main culture solution. Separately, add Pseudomonas No. 51-Y strain (Feikoken Bacteria No. 6103) to 50 ml of a culture solution having the culture medium composition described in Example 1.
A platinum loop of the slant culture was inoculated and cultured in a reciprocating shaker at 30°C for 150 hours.The solution was aseptically collected by centrifugation and used as an inoculum. This entire amount was added to the above-mentioned main culture solution and cultured at 30°C for 150 hours using a reciprocating shaker.The decomposition rate of EDTA was measured from the remaining amount of EDTA in the supernatant and was found to be 65%.
Claims (1)
するシユードモナス属に属する細菌またはアルカ
リゲネス属に属する細菌を、エチレンジアミン四
酢酸、エチレンジアミン四酢酸の金属錯体または
これらの化合物の塩類に接触させることを特徴と
するエチレンジアミン四酢酸の分解処理方法。1. Ethylenediaminetetraacetic acid, which is characterized in that bacteria belonging to the genus Pseudomonas or bacteria belonging to the genus Alcaligenes, which have the ability to decompose ethylenediaminetetraacetic acid, are brought into contact with ethylenediaminetetraacetic acid, a metal complex of ethylenediaminetetraacetic acid, or salts of these compounds. Decomposition processing method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP14079781A JPS5843782A (en) | 1981-09-07 | 1981-09-07 | Treatment of ethylenediaminetetraacetic acid with microorganism |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP14079781A JPS5843782A (en) | 1981-09-07 | 1981-09-07 | Treatment of ethylenediaminetetraacetic acid with microorganism |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5843782A JPS5843782A (en) | 1983-03-14 |
| JPH0220234B2 true JPH0220234B2 (en) | 1990-05-08 |
Family
ID=15276959
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP14079781A Granted JPS5843782A (en) | 1981-09-07 | 1981-09-07 | Treatment of ethylenediaminetetraacetic acid with microorganism |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5843782A (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US5252483A (en) * | 1990-04-11 | 1993-10-12 | Genencor International, Inc. | Degradation of ferric chelates by a pure culture of agrobacterium sp. |
| DE69520519T2 (en) | 1994-05-18 | 2001-08-09 | Fuji Photo Film Co., Ltd. | Process for rendering contaminated solutions from photoprocesses harmless |
| NL1000736C2 (en) * | 1995-07-06 | 1997-01-08 | Akzo Nobel Nv | Microbiological degradation of EDTA. |
| JP2003154352A (en) * | 2001-09-10 | 2003-05-27 | Fuji Photo Film Co Ltd | Method for remediating contaminated soil by microorganisms |
-
1981
- 1981-09-07 JP JP14079781A patent/JPS5843782A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5843782A (en) | 1983-03-14 |
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