JP2513495B2 - Denitrification method - Google Patents
Denitrification methodInfo
- Publication number
- JP2513495B2 JP2513495B2 JP63047261A JP4726188A JP2513495B2 JP 2513495 B2 JP2513495 B2 JP 2513495B2 JP 63047261 A JP63047261 A JP 63047261A JP 4726188 A JP4726188 A JP 4726188A JP 2513495 B2 JP2513495 B2 JP 2513495B2
- Authority
- JP
- Japan
- Prior art keywords
- nitrogen
- yeast
- nitrite
- wastewater
- filamentous fungus
- 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 - Lifetime
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Description
【発明の詳細な説明】 産業上の利用分野 本発明は、硝酸態窒素又は亜硝酸態窒素の脱窒方法に
係り、特に、廃水中に含有される硝酸態窒素又は亜硝酸
態窒素を還元して、ガス状の窒素として除去する脱窒方
法に関する。TECHNICAL FIELD The present invention relates to a method for denitrifying nitrate nitrogen or nitrite nitrogen, and more particularly to reducing nitrate nitrogen or nitrite nitrogen contained in wastewater. The present invention relates to a denitrification method for removing nitrogen as gaseous nitrogen.
従来の技術 自然界における窒素循環システムについては研究がか
なり行われ、有機態窒素やアンモニウム塩が、最終的に
は、好気的条件下で、硝化細菌により亜硝酸態窒素及び
硝酸態窒素に酸化され、また、この亜硝酸態窒素及び硝
酸態窒素が、嫌気的条件下に通性嫌気性の脱窒素菌によ
り、ガス状の窒素に還元されることは良く知られてい
る。2. Description of the Related Art A considerable amount of research has been conducted on the nitrogen circulation system in the natural world, and organic nitrogen and ammonium salts were eventually oxidized to nitrite nitrogen and nitrate nitrogen by nitrifying bacteria under aerobic conditions. It is well known that the nitrite nitrogen and the nitrate nitrogen are reduced to gaseous nitrogen by a facultative anaerobic denitrifying bacterium under anaerobic conditions.
近年、水域における富栄養化の進行及びこれによる藻
や赤潮の異常発生にともない、廃水中の窒素の除去プロ
セスとして、上記窒素循環システムの一部を利用する試
みが多々なされている。すなわち、先ず、都市下水や工
場廃水等を、好気的条件下に活性汚泥と接触させ、有機
物の酸化とともに、有機態窒素及びアンモニウム塩を、
亜硝酸態窒素及び硝酸態窒素に酸化し、次いで、嫌気的
条件にし、亜硝酸態窒素及び硝酸態窒素を還元、脱窒す
る方法が行われている。In recent years, with the progress of eutrophication in water bodies and the abnormal occurrence of algae and red tides due to this, many attempts have been made to utilize a part of the nitrogen circulation system as a nitrogen removal process in wastewater. That is, first, municipal sewage and industrial wastewater are brought into contact with activated sludge under aerobic conditions to oxidize organic substances and to remove organic nitrogen and ammonium salts.
A method is used in which nitrite nitrogen and nitrate nitrogen are oxidized, and then anaerobic conditions are applied to reduce and denitrify nitrite nitrogen and nitrate nitrogen.
尚、上記脱窒素作用は、原核生物であるバクテリアで
は知られているが、真核生物では、全く知られていな
い。なお、従来、上記脱窒の際に作用する通性嫌気性の
脱窒素菌は、好気性菌等に比べて大きなフロツクができ
難く、したがつて、脱窒後の菌体の分離が難しいという
問題がある。The denitrification action is known in prokaryotes, but not in eukaryotes. Conventionally, facultative anaerobic denitrifying bacteria that act during the above-mentioned denitrification are less likely to form large flocks than aerobic bacteria, and therefore it is difficult to separate the cells after denitrification. There's a problem.
発明が解決しようとする課題 本発明は、上記問題点を解決して、硝酸態窒素又は亜
硝酸態窒素を含有する基質、例えば廃水中のこれら窒素
化合物を微生物を利用して還元し、ガス状の窒素として
除去するための脱窒方法を提供することを課題とする。DISCLOSURE OF THE INVENTION Problems to be Solved by the Invention The present invention solves the above-mentioned problems and reduces nitrate nitrogen or nitrite nitrogen-containing substrates, for example, these nitrogen compounds in waste water by using a microorganism to produce a gaseous form. It is an object of the present invention to provide a denitrification method for removing nitrogen as nitrogen.
課題を解決するための手段 本発明者らは、植物病原菌である数種の糸状菌の代謝
研究を進めていた過程において、培地中に硝酸塩や亜硝
酸塩を添加し、通気を抑えて前記糸状菌を培養すると、
異化型の硝酸、亜硝酸呼吸を行うこと及び酵母について
も同様の作用があることを見い出した。かかる異化型の
硝酸、亜硝酸呼吸は、前述したように真核生物において
は全く知られていなかつた。Means for Solving the Problems In the process of advancing the metabolic research of several filamentous fungi, which are plant pathogenic fungi, the present inventors added nitrates and nitrites to the medium to suppress the aeration and to control the filamentous fungi. When cultured,
It was found that catabolic nitric acid, nitrite respiration and yeast also have similar effects. Such catabolic nitric acid and nitrite respiration have never been known in eukaryotes as described above.
本発明は、このような知見に基づきなされたもので、
本発明は、硝酸態窒素又は亜硝酸態窒素を含有する基質
を嫌気性条件下に糸状菌または酵母と接触させ、脱窒素
することから構成されるものである。尚、この発明にお
いては、リゾプス属、ギベレラ属、フザリウム属、ハン
セヌラ属に属する微生物から選択された菌株を用いるこ
とが好ましい。The present invention has been made based on such findings,
The present invention is constituted by bringing a substrate containing nitrate nitrogen or nitrite nitrogen into contact with a filamentous fungus or yeast under anaerobic conditions to denitrify. In the present invention, it is preferable to use a strain selected from microorganisms belonging to the genera Rhizopus, Gibberella, Fusarium and Hansenula.
本発明にいう糸状菌とは、菌糸からなり、当該菌糸が
分岐して菌糸体を形成し、葉緑素を有しない一群の生物
を指すが、生物分類学上では、菌類の中の真菌類を構成
する接合菌類、子嚢菌類、担子菌類および不完全菌類の
4綱のうちで、主として出芽によつて無性生殖を行うい
わゆる酵母を除外した部分で、しかも体が糸状を呈する
一群の微小な生物を指すものである。この糸状菌の中で
も、リゾプス(Rhizopus)属、ギベレラ(Gibberella)
属、フザリウム(Fusarium)属、ニユーロスポラ(Neur
ospora)属等を好適に用いることができる。The filamentous fungus referred to in the present invention refers to a group of organisms consisting of hyphae, the hyphae branching to form mycelia and having no chlorophyll, but on the taxonomy of organisms, fungi among fungi are constituted. Of the four classes of zygosity, ascomycetes, basidiomycetes and incomplete fungi that exclude so-called yeasts that asexually reproduce by budding, a group of microscopic organisms whose body is filamentous Refers to. Among these filamentous fungi, the genus Rhizopus, Gibberella
Genus Fusarium, Neurospora
genus ospora) and the like can be preferably used.
一方、酵母は、菌類のなかで栄養細胞が出芽によつて
増えるもので、有性生殖を行う有胞子酵母及び有性生殖
を行わない無胞子酵母を含むものである。この酵母の中
で、ハンセヌラ(Hansenula)属等を好適に用いること
ができる。On the other hand, yeast is a fungus in which vegetative cells increase due to budding, and includes spore yeast that sexually reproduces and aspore yeast that does not sexually reproduce. Among these yeasts, the genus Hansenula can be preferably used.
以上のような糸状菌又は酵母の菌株の一部は、第1表
に記載する受理番号で工業技術院微生物工業技術研究所
(FERM)に寄託され、また、表に記載する菌株番号によ
り、(財)発酵研究所(IFO)、東京大学応用微生物研
究所(IAM)から、当該技術分野における通常の知識を
有するものが容易に入手できるようになつている。Some of the strains of filamentous fungus or yeast as described above have been deposited at the Institute of Microbial Science and Technology (FERM) with the accession number shown in Table 1, and with the strain numbers shown in the table, ( Those having ordinary knowledge in the technical field can be easily obtained from the Fermentation Research Institute (IFO) and the Institute for Applied Microbiology (IAM) of the University of Tokyo.
また、寄託微生物であるフザリウム・オキシスポラム
の菌学的性質は、T.Satoh et al.、アグリカルチユラル
アンド バイオロジカル ケミストリイ〔Agr.Biol.C
hem.、40、953〜961(1976)〕に詳記されている。 In addition, the mycological properties of the deposited microorganism Fusarium oxysporum are described in T. Satoh et al., Agricultural and Biological Chemistry [Agr.
hem., 40, 953-961 (1976)].
本発明においては、上記糸状菌及び酵母を利用して、
硝酸態窒素又は亜硝酸態窒素を資化させるが、これらの
窒素は、専ら、イオンあるいは塩の形態で用いる。この
硝酸態窒素又は亜硝酸態窒素の濃度は、用いる糸状菌や
酵母の種類、濃度等により一概には決められないが、10
0〜5000ppmとすることが好ましい。また、基質中には、
これらの窒素以外に炭素源及び無機塩を、適宜添加す
る。基質に対する糸状菌や酵母の濃度は、培地の形態、
資化方式等を勘案し、適宜選定される。尚、培地は、固
体でも、液体でも良く、特に、廃水処理に、本発明を適
用する場合は、糸状菌或いは酵母の生育に必要な基質
で、廃水中に含まれていないものを添加すれば良い。In the present invention, utilizing the above filamentous fungus and yeast,
Nitrate nitrogen or nitrite nitrogen is assimilated, but these nitrogens are used exclusively in the form of ions or salts. The concentration of this nitrate nitrogen or nitrite nitrogen cannot be determined unconditionally depending on the type and concentration of the filamentous fungus or yeast to be used.
It is preferably 0 to 5000 ppm. Also, in the substrate,
In addition to these nitrogen, a carbon source and an inorganic salt are appropriately added. The concentration of filamentous fungus or yeast relative to the substrate depends on the morphology of the medium,
It is selected as appropriate in consideration of the assimilation method. Incidentally, the medium may be solid or liquid, and in particular, for the treatment of wastewater, when the present invention is applied, if a substrate necessary for the growth of filamentous fungi or yeast, which is not contained in the wastewater, is added. good.
糸状菌又は酵母による資化は、バクテリアによる脱窒
と比べ、より好気的であるので、雰囲気を高度の嫌気条
件にする必要もなく、空気とすることも可能である。ま
た、この資化は、pH5〜9、0〜50℃の温度で行われ、
通常は、常圧下で行うが、加圧下で行つてもよい。Since assimilation by filamentous fungi or yeast is more aerobic than denitrification by bacteria, it is not necessary to set the atmosphere to a highly anaerobic condition and air can be used. Also, this assimilation is carried out at a temperature of pH 5-9, 0-50 ° C,
Usually, it is carried out under normal pressure, but it may be carried out under pressure.
資化方式は、回分式、連続式、半回分式のいずれでも
良いが、特に廃水処理に適用する場合は、前記糸状菌及
び酵母を固定し、いわゆるバイオリアクター方式で行う
と効率が良く、特に好ましい。The assimilation system may be a batch system, a continuous system, or a semi-batch system, but particularly when it is applied to wastewater treatment, the filamentous fungus and yeast are fixed, and it is efficient to perform the so-called bioreactor system. preferable.
尚、都市下水や工場廃水等の処理に本発明を適用する
場合は、先ず、これらの廃水を好気的条件下に活性汚泥
と接触させ、有機物の酸化とともに、有機態窒素及びア
ンモニウム塩を、亜硝酸態窒素及び硝酸態窒素に酸化
し、次いで、この処理水を、糸状菌又は酵母により、亜
硝酸態窒素及び硝酸態窒素を還元、脱窒する方法を採る
と良い。Incidentally, when applying the present invention to the treatment of municipal sewage or industrial wastewater, first, contact these wastewater with activated sludge under aerobic conditions, along with the oxidation of organic matter, organic nitrogen and ammonium salts, A method of oxidizing the nitrite nitrogen and nitrate nitrogen, and then reducing and denitrifying the treated water with a filamentous fungus or yeast may be adopted.
以下実施例により、本発明及びその効果を具体的に説
明する。The present invention and its effects will be specifically described below with reference to examples.
実施例1 三つ口の300ml容三角フラスコに、第2表に示した組
成に亜硝酸ナトリウムまたは硝酸ナトリウムを0.5%の
濃度で加えた液体培地180mlを入れ、これに前記第1表
に記載した糸状菌又は酵母をそれぞれ、おおよそ1g−湿
潤菌体/lの濃度になるように接種し、内部を二酸化炭素
で置換した後、ゴム栓をした。26.5℃の温度で、ロータ
リーシエーカーを用いて振とう培養し、所定時間経過に
上部気体を0.5mlづつサンプリングし、ガスクロマトグ
ラフイーにより窒素ガスの濃度を測定した。Example 1 A three-necked 300 ml Erlenmeyer flask was charged with 180 ml of a liquid medium in which the composition shown in Table 2 was added with sodium nitrite or sodium nitrate at a concentration of 0.5%, and this was described in Table 1 above. Each of the filamentous fungi or yeast was inoculated to a concentration of about 1 g-wet cells / l, the inside was replaced with carbon dioxide, and then a rubber stopper was placed. At a temperature of 26.5 ° C., shaking culture was performed using a rotary shaker, 0.5 ml of the upper gas was sampled for each predetermined time, and the concentration of nitrogen gas was measured by gas chromatography.
この結果を第3表に示す。The results are shown in Table 3.
尚、培養開始時の酸素量は1.5容量%であつた。 The oxygen content at the start of culture was 1.5% by volume.
実施例2 実施例1の第2表と同様な組成に原子量15の安定同位
体窒素を含む亜硝酸ナトリウムまたは硝酸ナトリウムを
0.5%濃度で加えた液体培地に、実施例1で用いたフザ
リウム・オキシスポラム、リゾプス・オリザエ、リゾプ
ス・ジヤバニカスの菌株を接種し、同様に培養した。培
養7日後に、上部のガス中の窒素を、液体窒素で冷却し
たモレキユラーシーブにトラツプした後、放電管に導
き、窒素中の原子量15の同位体の量を発光分光法により
測定した。原子量15の同位体の量は、全窒素に対し、フ
ザリウム・オキシスポラムの場合は、65%、他は、10%
であつた。このことから、糸状菌及び酵母が、異化型の
硝酸、亜硝酸呼吸をしていることが分かる。 Example 2 Sodium nitrite or sodium nitrate containing a stable isotope nitrogen having an atomic weight of 15 in the same composition as in Table 2 of Example 1 was used.
The liquid medium added at a concentration of 0.5% was inoculated with the strains of Fusarium oxysporum, Rhizopus oryzae, and Rhizopus jayvanicas used in Example 1 and the same culture was performed. After 7 days of culturing, nitrogen in the upper gas was trapped in a molecular sieve cooled with liquid nitrogen, introduced into a discharge tube, and the amount of isotope having an atomic weight of 15 in nitrogen was measured by emission spectroscopy. The amount of isotopes with an atomic weight of 15 is 65% for Fusarium oxysporum and 10% for other nitrogen, based on total nitrogen.
It was. From this, it is understood that the filamentous fungi and yeast respire catabolic nitric acid and nitrite.
以上の結果から明らかなように、真核生物である糸状
菌又は酵母が異化型の硝酸、亜硝酸呼吸を行い、これを
用いることにより、硝酸態窒素又は亜硝酸態窒素を含む
基質、例えば、都市下水や工場廃水中の脱窒素を行うこ
とができることは明らかである。As is clear from the above results, filamentous fungi or yeasts that are eukaryotes perform catabolic nitric acid respiration, and by using this, a substrate containing nitrate nitrogen or nitrite nitrogen, for example, It is clear that denitrification in municipal sewage and industrial wastewater can be performed.
発明の効果 本発明は、硝酸態窒素又は亜硝酸態窒素を含有する基
質を糸状菌又は酵母で資化させ、脱窒素するため、菌体
の分離が容易であり、都市下水や工場廃水中の脱窒素を
効率良く行うことができるという効果を有する。EFFECTS OF THE INVENTION The present invention utilizes a substrate containing nitrate nitrogen or nitrite nitrogen with a filamentous fungus or yeast to denitrify, so that the cells can be easily separated, and the wastewater in municipal wastewater or factory wastewater can be easily separated. It has an effect that denitrification can be performed efficiently.
Claims (2)
質を、通気を抑えた条件下或いは嫌気性条件下で、これ
ら窒素の資化能を有する、糸状菌又は酵母で資化させ、
脱窒素することを特徴とする脱窒方法。1. A substrate containing nitrate nitrogen or nitrite nitrogen is assimilated by a filamentous fungus or yeast capable of assimilating these nitrogens under aeration-suppressed conditions or anaerobic conditions,
A denitrification method characterized by denitrifying.
ラ属、フザリウム属、ニューロスボラ属及びハンヌラ属
のいずれかに属する微生物を用いる請求項(1)に記載
の脱窒方法。2. The denitrification method according to claim 1, wherein a microorganism belonging to any one of Rhizopus, Gibberella, Fusarium, Neurosbora, and Hannula is used as the filamentous fungus or yeast.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63047261A JP2513495B2 (en) | 1988-02-29 | 1988-02-29 | Denitrification method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP63047261A JP2513495B2 (en) | 1988-02-29 | 1988-02-29 | Denitrification method |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH01218698A JPH01218698A (en) | 1989-08-31 |
JP2513495B2 true JP2513495B2 (en) | 1996-07-03 |
Family
ID=12770345
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP63047261A Expired - Lifetime JP2513495B2 (en) | 1988-02-29 | 1988-02-29 | Denitrification method |
Country Status (1)
Country | Link |
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JP (1) | JP2513495B2 (en) |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2006239583A (en) * | 2005-03-03 | 2006-09-14 | Mie Univ | Sintered body for water purification, and production method |
JP6769615B2 (en) * | 2017-04-20 | 2020-10-14 | 有限会社オフイスヨコオ | Nitrate nitrogen removal method and nitrate nitrogen remover |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5351657A (en) * | 1976-10-20 | 1978-05-11 | Kuraray Co Ltd | Method for disposing organic waste water |
JPS5458951A (en) * | 1977-10-19 | 1979-05-12 | Asahi Carbon Co Ltd | Method of disposing starch and*or saccharoid containing waste water |
ZA791949B (en) * | 1978-05-19 | 1980-05-28 | Ici Ltd | Treatment of effluents arising from the processing of milk |
-
1988
- 1988-02-29 JP JP63047261A patent/JP2513495B2/en not_active Expired - Lifetime
Also Published As
Publication number | Publication date |
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JPH01218698A (en) | 1989-08-31 |
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