JP2005319395A - Decomposition method of high bod specimen, urea, ammonia, and nitrate - Google Patents

Decomposition method of high bod specimen, urea, ammonia, and nitrate Download PDF

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JP2005319395A
JP2005319395A JP2004139387A JP2004139387A JP2005319395A JP 2005319395 A JP2005319395 A JP 2005319395A JP 2004139387 A JP2004139387 A JP 2004139387A JP 2004139387 A JP2004139387 A JP 2004139387A JP 2005319395 A JP2005319395 A JP 2005319395A
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ammonia
nitrate
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bacillus midousuji
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Sadayori Hoshina
定頼 保科
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DNA FUTURE KK
MARIUSU KK
TOKYO KADAN KK
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Abstract

<P>PROBLEM TO BE SOLVED: To realize decomposition of nitrogen-containing urea, ammonia, and nitrate in the environment, such as agricultural effluent, domestic effluent, and industrial wastewater, and decomposition of a specimen having high BOD at low energy and cost with a small-scale apparatus. <P>SOLUTION: Bacillus midousuji obtained by fresh culture etc. is added to the high BOD specimen, urea, ammonia, and nitrate, and the specimen is left still at 62 to 65°C for several hours to several days. As a result, the high BOD specimen, urea, ammonia, and nitrate are decomposed by Bacillus midousuji. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、高BOD試料、尿素、アンモニア、硝酸塩の分解方法に関するものである。   The present invention relates to a method for decomposing high BOD samples, urea, ammonia, and nitrates.

窒素は生物にとって欠くことのできない栄養素であって、農業において肥料として窒素化合物の散布が日常的に行われている。また、肥料以外でも牛などの家畜を飼育する際には窒素を含む大量の糞尿が発生している。農業排水のみならず生活排水においても大量の窒素を含む排水がなされており、かかる排水が河川や湖沼に流入することで河川等の富栄養化が進み赤潮の発生原因や水質汚濁の原因となっているという報告がある。国の窒素に関する排出規制は厳しさを増しており農業排水や生活排水、工業排水などからいかに窒素を除去するかが問題化している。また、窒素のみならずたんぱく質などを多く含んでいてBODの数値が高い高BOD試料も河川や湖沼の富栄養化を招く原因として取りざたされている。   Nitrogen is an essential nutrient for living organisms. In agriculture, nitrogen compounds are regularly applied as fertilizers. In addition to fertilizers, large amounts of manure containing nitrogen are generated when raising livestock such as cattle. Wastewater containing a large amount of nitrogen is generated not only in agricultural wastewater but also in domestic wastewater, and when such wastewater flows into rivers and lakes, the eutrophication of rivers and the like progresses, causing red tides and water pollution. There is a report that it is. The emission regulations on nitrogen in the country are becoming stricter, and how to remove nitrogen from agricultural wastewater, domestic wastewater, industrial wastewater, etc. is becoming a problem. In addition, high BOD samples that contain a large amount of protein as well as nitrogen and have a high BOD value are also being investigated as a cause of eutrophication of rivers and lakes.

従来は、非特許文献1、非特許文献2などの技術がある。しかし、生活排水や農業排水から窒素を除去する場合大型水槽4台で対応する場合があるなど設備が大規模であった。また、処理費用も数千万円かかることもありコストパフォーマンスの点からも問題であった。
水質汚濁防止技術概論、化学工業協会編、培風館、157pから169p 技術・嫌気性処理分野(2)Anammox反応を用いた窒素除去技術、安井英斉、徳富孝明、環境技術、vol33、No2、2004、46pから49p 戸田新細菌学、南山堂、吉田真一、柳雄介、改訂32版、ISBN4-525-16012-8、67p、844p
Conventionally, there are technologies such as Non-Patent Document 1 and Non-Patent Document 2. However, when removing nitrogen from domestic wastewater or agricultural wastewater, there are cases where four large water tanks may be used, and the facilities are large. In addition, the processing cost may be tens of millions of yen, which is a problem from the viewpoint of cost performance.
Water Pollution Control Technology Overview, Chemical Industry Association, Bafukan, 157p to 169p Technology and Anaerobic Treatment Field (2) Nitrogen removal technology using Anammox reaction, Hidei Yasui, Takaaki Tokutomi, Environmental Technology, vol33, No2, 2004, 46p to 49p Toda New Bacteriology, Nanzando, Shinichi Yoshida, Yusuke Yanagi, Rev. 32, ISBN4-525-16012-8, 67p, 844p

解決しようとする問題点は、小さな装置で効率よく高BOD試料、尿素、アンモニア、硝酸塩を分解するかである。   The problem to be solved is how to efficiently decompose a high BOD sample, urea, ammonia, and nitrate with a small apparatus.

本発明は、高BOD試料、尿素、アンモニア、硝酸塩にBacillus midousuji菌体(ATCC受託番号第55926号と第202050号として寄託されている微生物またはそれに由来する突然変異体株の生物学的純粋培養物、以下「Bacillus midousuji菌体」という。)を混ぜて分解することを最も主要な特徴とする。   The present invention relates to a biologically pure culture of a Bacillus midousuji cell (a microorganism deposited as ATCC accession numbers 55926 and 202050 or a mutant strain derived therefrom in a high BOD sample, urea, ammonia, and nitrate. , Hereinafter referred to as "Bacillus midousuji cells"), and the most important feature is to decompose by mixing.

本発明によれば、小型の装置で処理費用をかけずに高BOD試料、尿素、アンモニア、硝酸塩を分解できるという利点がある。   According to the present invention, there is an advantage that a high-BOD sample, urea, ammonia, and nitrate can be decomposed without a processing cost with a small apparatus.

小型の装置を使用して温度の管理、吸排気の管理など最小の管理を行うことで分解を実現した。   Disassembly was realized by performing minimum management such as temperature control and intake / exhaust control using a small device.

まず、窒素のみならずたんぱく質などを多く含んでいてBODの数値が高い高BOD試料の分解方法について説明する。人の生化学検査に使用するため採血された血液の血清血漿残渣につき高圧蒸気滅菌処理(日立製ロトクレーブTMを用いて140度で30分間処理)したヒトプール血清血漿希釈液200Lに、Bacillus midousuji菌体の株をTrypticase Soy Agar(BBL)寒天培地で65℃3時間新鮮培養した菌を4g(湿菌量)加えた試料を作成し、高たんぱく分解装置(児玉機械製作所製、処理タンク200リットル、貯蔵タンク300リットル)のものを用いて、処理タンク内に試料を入れ空気を混ぜて、排気をしながら65℃で攪拌した。簡易BOD測定装置(堀場製作所製)により24時間後の処理水、48時間後の処理水のBODを測定した結果を表1に示す。

Figure 2005319395
First, a method for decomposing a high BOD sample containing a large amount of protein as well as nitrogen and having a high BOD value will be described. A blood collection has been (30 minutes at 140 ° using a Hitachi Rotokurebu TM) Serum Plasma residue per high-pressure steam sterilization of blood was pooled human serum plasma dilutions 200L for use in biochemical tests of human, Bacillus midousuji cells A sample prepared by adding 4 g (wet amount of bacteria) of freshly cultured strains from Trypticase Soy Agar (BBL) agar medium at 65 ° C. for 3 hours to a high protein digester (Kodachi Machinery Manufacturing Co., Ltd., processing tank 200 liters, storage) Using a tank of 300 liters), a sample was placed in a processing tank, mixed with air, and stirred at 65 ° C. while evacuating. Table 1 shows the results of measuring the BOD of treated water after 24 hours and treated water after 48 hours with a simple BOD measuring device (manufactured by Horiba Seisakusho).
Figure 2005319395

この実験結果によれば、BOD値が約96%程度減少しており、たんぱく質などがBacillus midousuji菌体によって分解されたことを示す。また、排気をせずに実験を行った場合BOD値が逆に増大したことから排気することが必要である。   According to this experimental result, the BOD value decreased by about 96%, indicating that the protein and the like were decomposed by Bacillus midousuji cells. Further, when the experiment was conducted without exhausting, it was necessary to exhaust because the BOD value increased conversely.

次に、尿素をアンモニアに分解する方法について説明する。Bacillus midousuji菌体をSoybean-Casein Digest Broth中で混ぜた試料を作成し、商品名スタットウレアーゼ「アスカ」(アスカ純薬株式会社販売)に入れて、65℃に温度を設定して2時間静置した。その結果試料は鮮明な赤色を示し尿素がアンモニアに分解されたことを示した。   Next, a method for decomposing urea into ammonia will be described. A sample prepared by mixing Bacillus midousuji cells in Soybean-Casein Digest Broth, put it in the trade name Staturease “Asuka” (sold by Asuka Pure Chemicals), set the temperature at 65 ° C. and let stand for 2 hours did. As a result, the sample showed a bright red color, indicating that urea was decomposed into ammonia.

次にアンモニアを亜硝酸塩に分解する方法について説明する。NaNO3を0.25g、2.94mM、MgSO4を0.2g、1.66mM、Na2HPO4を0.21g、1.48mM、KClを0.5g、6.70mM、NH4Clを0.25g、4.67mM、NaH2PO4を0.09g、7.50mM、CaCl2を0.02g、1.80mM、FeSO4を1.0mg、6.58μM含む1Lの無機塩培地を作成し、7mlのライニングスクリューキャップ付ガラス試験管に該無機塩培地を2mL分注した無機塩培地2mL試料を用意した。 Next, a method for decomposing ammonia into nitrite will be described. NaNO 3 0.25 g, 2.94 mM, MgSO 4 0.2 g, 1.66 mM, Na 2 HPO 4 0.21 g, 1.48 mM, KCl 0.5 g, 6.70 mM, NH 4 Cl 0.25 g, 4.67 mM, NaH 2 PO 4 0.09 g, 7.50 mm, the CaCl 2 0.02g, 1.80mM, FeSO 4 and 1.0 mg, to create a mineral salts medium of 6.58μM containing 1L, the inorganic salt medium in a glass test tube with lined screw cap 7ml A 2 mL sample of inorganic salt medium dispensed in 2 mL was prepared.

菌は、Bacillus midousuji菌体の株をTrypticase Soy Agar(BBL)平板塩地で65℃3時間新鮮培養後滅菌精製水にて109/mL濃度に調整したものを該無機塩培地2mL試料に0.1mL加えた試料を作成した。また、対照系として菌を加えない試料を用意した。両方の試料を62度で11時間反応させた後アンモニア窒素濃度(アンモニア性窒素の定義も含む。)を測定した。測定方法は、アミチェックTM(アークレイ株式会社販売)によった。アミチェックTMによって測定しやすいように両方の試料を希釈した。この実験結果を表2に示す。但し、理論上はBacillus midousuji菌体なしの場合0.09g/LになるがアミチェックTMの測定による誤差などがあると思われる。しかしアンモニア窒素は減少している。

Figure 2005319395
Bacteria are strains of Bacillus midousuji cells that were freshly cultured in Trypticase Soy Agar (BBL) flat salt salt at 65 ° C for 3 hours and adjusted to a concentration of 10 9 / mL with sterile purified water. A sample added with mL was prepared. Moreover, the sample which does not add bacteria as a control system was prepared. After both samples were reacted at 62 degrees for 11 hours, the ammonia nitrogen concentration (including the definition of ammoniacal nitrogen) was measured. The measurement method was based on Amicheck (Arkray, Inc.). Both samples were diluted for easy measurement by Amicheck . The experimental results are shown in Table 2. However, theoretically, it is 0.09 g / L without Bacillus midousuji cells, but it seems that there are errors due to the measurement of Amicheck . However, ammonia nitrogen is decreasing.
Figure 2005319395

Bacillus midousuji菌体を加えた試料はアンモニア窒素濃度が0.046g/Lまで低下したのに対して、Bacillus midousuji菌体を加えなかった試料のアンモニア窒素濃度は0.159g/Lとなっている。アンモニアはBacillus midousuji菌体の酸化反応により硝酸塩に分解されたものと考えられる。   The sample to which Bacillus midousuji cells were added decreased to an ammonia nitrogen concentration of 0.046 g / L, whereas the ammonia nitrogen concentration of the sample to which Bacillus midousuji cells were not added was 0.159 g / L. It is thought that ammonia was decomposed into nitrate by the oxidation reaction of Bacillus midousuji cells.

別の実験について言及する。人の生化学検査に使用するため採血された血液の血清血漿残渣につき高圧蒸気滅菌処理(日立製ロトクレーブTMを用いて140度で30分間処理)したヒトプール血清血漿希釈液200Lに、Bacillus midousuji菌体の株をTrypticase Soy Agar(BBL)寒天培地で65℃3時間新鮮培養した菌4g(湿菌量)を加えた試料を作成し、高たんぱく分解装置(児玉機械製作所製、処理タンク200リットル、貯蔵タンク300リットル)のものを用いて処理タンク内に試料を入れ、試料を62度で3時間ないし21時間反応させてアンモニア窒素濃度を測定した。測定の方法は同様にアミチェックTMによった。この実験結果を表3に示す。

Figure 2005319395
Mention another experiment. A blood collection has been (30 minutes at 140 ° using a Hitachi Rotokurebu TM) Serum Plasma residue per high-pressure steam sterilization of blood was pooled human serum plasma dilutions 200L for use in biochemical tests of human, Bacillus midousuji cells A sample prepared by adding 4 g (wet bacteria amount) of freshly cultured strains from Trypticase Soy Agar (BBL) agar medium at 65 ° C. for 3 hours to a high protein digester (Kodama Machinery Co., Ltd., processing tank 200 liters, storage) A sample was placed in the treatment tank using a tank of 300 liters), and the sample was reacted at 62 ° C. for 3 to 21 hours to measure the ammonia nitrogen concentration. The method of measurement was by Ami check TM in the same way. The experimental results are shown in Table 3.
Figure 2005319395

Bacillus midousuji菌体を加えるとアンモニア窒素濃度は3時間で約30%、21時間で約40%減少した。アンモニアはBacillus midousuji菌体の酸化反応により硝酸塩に分解されたものと考えられる。また、Bacillus midousuji菌体は65度でもより代謝反応がある。   When Bacillus midousuji cells were added, the ammonia nitrogen concentration decreased about 30% in 3 hours and about 40% in 21 hours. It is thought that ammonia was decomposed into nitrate by the oxidation reaction of Bacillus midousuji cells. Further, Bacillus midousuji cells have a more metabolic reaction even at 65 degrees.

さらに別の実験についても言及する。人の生化学検査に使用するため採血された血液の血清血漿残渣につき高圧蒸気滅菌処理(日立製ロトクレーブTMを用いて140度で30分間処理)したヒトプール血清血漿希釈液200Lに、Bacillus midousuji菌体の株をTrypticase Soy Agar(BBL)寒天培地で65℃3時間新鮮培養した菌4g(湿菌量)を加えた試料を作成し、高たんぱく分解装置(児玉機械製作所製、処理タンク200リットル、貯蔵タンク300リットル)のものを用いて、処理タンク内に試料入れ空気を混ぜて、65℃で攪拌した。ガラス電極式水素イオン濃度測定器(堀場製作所製)により原水、24時間後の処理水、48時間後の処理水の水素イオン濃度を測定した結果及び別実験での同様の方法により24時間後の処理水、48時間後の処理水、72時間後の処理水の水素イオン濃度を測定した結果を表4に示す。

Figure 2005319395
I will mention another experiment. A blood collection has been (30 minutes at 140 ° using a Hitachi Rotokurebu TM) Serum Plasma residue per high-pressure steam sterilization of blood was pooled human serum plasma dilutions 200L for use in biochemical tests of human, Bacillus midousuji cells A sample prepared by adding 4 g (wet bacteria amount) of freshly cultured strains from Trypticase Soy Agar (BBL) agar medium at 65 ° C. for 3 hours to a high protein digester (Kodama Machinery Co., Ltd., processing tank 200 liters, storage) The sample tank was mixed with air in a treatment tank using a tank of 300 liters) and stirred at 65 ° C. Results of measuring the hydrogen ion concentration of raw water, treated water after 24 hours, treated water after 48 hours with a glass electrode type hydrogen ion concentration meter (manufactured by Horiba) and the same method in another experiment Table 4 shows the results of measuring the hydrogen ion concentration of the treated water, the treated water after 48 hours, and the treated water after 72 hours.
Figure 2005319395

この実験結果によれば、水素イオン濃度が急激に減少しており、アルカリ性を有するアンモニア性物質がBacillus midousuji菌体によって分解されたことを示す。アンモニアはBacillus midousuji菌体の酸化反応により硝酸塩に分解されたものと考えられる。   According to this experimental result, the hydrogen ion concentration decreased rapidly, indicating that the alkaline ammoniacal substance was decomposed by Bacillus midousuji cells. It is thought that ammonia was decomposed into nitrate by the oxidation reaction of Bacillus midousuji cells.

次に硝酸塩の分解方法について説明する。硝酸塩培地に、Bacillus midousuji菌体の株をTrypticase Soy Agar(BBL)寒天培地で65℃3時間新鮮培養した菌を108/mL加えて密閉して11時間培養し、硝酸塩還元試験を行った。培養後亜硝酸試薬を加えると試料が赤くならなかった。このため試料には亜硝酸塩を生じていないことが判明した。さらに亜鉛粉末を少量試料に加えてしばらく放置した。しかし、変化がなかったため試料に硝酸塩がないことが判明した。試料の硝酸塩はBacillus midousuji菌体の還元反応により窒素ガスなどに分解されたと考えられる。 Next, a method for decomposing nitrate will be described. Bacteria obtained by cultivating a strain of Bacillus midousuji cells on Trypticase Soy Agar (BBL) agar medium at 65 ° C. for 3 hours in a nitrate medium was added at 10 8 / mL, and the mixture was sealed and cultured for 11 hours, and a nitrate reduction test was performed. When the nitrite reagent was added after incubation, the sample did not turn red. For this reason, it was found that no nitrite was produced in the sample. Further, a small amount of zinc powder was added to the sample and left for a while. However, it was found that the sample was free of nitrate because there was no change. The nitrate of the sample is considered to have been decomposed into nitrogen gas etc. by the reduction reaction of Bacillus midousuji cells.

図1はBacillus midousuji菌体を用いた分解処理サイクルを示した説明図である。Bacillus midousuji菌体を使用すれば、尿素を酸化してアンモニアに分解し、アンモニアを酸化して亜硝酸塩に分解する。亜硝酸塩を硝酸塩にさらに酸化しBacillus midousuji菌体を使用すれば、硝酸塩を還元して窒素ガスなどに分解できる。   FIG. 1 is an explanatory view showing a decomposition treatment cycle using Bacillus midousuji cells. If Bacillus midousuji cells are used, urea is oxidized and decomposed into ammonia, and ammonia is oxidized and decomposed into nitrite. If nitrite is further oxidized to nitrate and Bacillus midousuji cells are used, nitrate can be reduced and decomposed into nitrogen gas and the like.

Bacillus midousuji菌体は、好気条件では高BOD資料の分解など化合物を酸化する働きを持つ。一方で嫌気条件では硝酸塩を窒素ガスなどに分解するなど化合物を還元する働きをもつ。Bacillus midousuji菌体は一つの菌体で酸化反応や還元反応を生じさせる機能を有する点で稀有な菌体である。   Bacillus midousuji cells oxidize compounds such as decomposition of high BOD materials under aerobic conditions. On the other hand, under anaerobic conditions, it has the function of reducing compounds such as decomposing nitrate into nitrogen gas. Bacillus midousuji cells are rare in that they have a function of causing an oxidation reaction or a reduction reaction in one cell.

本発明によれば生活排水、農業排水、工業排水その他医療廃棄物など窒素を含む排水や高たんぱく質を含む排水の処理に適用できる。   INDUSTRIAL APPLICABILITY The present invention can be applied to the treatment of wastewater containing nitrogen and wastewater containing high protein such as domestic wastewater, agricultural wastewater, industrial wastewater and other medical waste.

Bacillus midousuji菌体を用いた分解処理サイクルを示した説明図である。(実施例5)It is explanatory drawing which showed the decomposition process cycle using Bacillus midousuji microbial cell. (Example 5)

Claims (6)

Bacillus midousuji菌体(ATCC受託番号第55926号と第202050号として寄託されている微生物またはそれに由来する突然変異体株の生物学的純粋培養物)と高BOD試料を混ぜて、好気条件で高BOD試料を分解する方法。   Bacillus midousuji cells (biologically pure cultures of microorganisms deposited as ATCC deposit numbers 55926 and 202050 or mutant strains derived from them) and high BOD samples are mixed and mixed under high aerobic conditions. A method for decomposing BOD samples. Bacillus midousuji菌体(ATCC受託番号第55926号と第202050号として寄託されている微生物またはそれに由来する突然変異体株の生物学的純粋培養物)と尿素を混ぜて尿素を分解する方法。   A method of decomposing urea by mixing Bacillus midousuji cells (biologically pure culture of microorganisms deposited as ATCC deposit numbers 55926 and 202050 or mutant strains derived therefrom) with urea. Bacillus midousuji菌体(ATCC受託番号第55926号と第202050号として寄託されている微生物またはそれに由来する突然変異体株の生物学的純粋培養物)とアンモニアを混ぜてアンモニアを分解する方法。   A method of decomposing ammonia by mixing Bacillus midousuji cells (biologically pure culture of microorganisms deposited as ATCC deposit numbers 55926 and 20950 or mutant strains derived therefrom) and ammonia. Bacillus midousuji菌体(ATCC受託番号第55926号と第202050号として寄託されている微生物またはそれに由来する突然変異体株の生物学的純粋培養物)と硝酸塩を混ぜて、硝酸塩を窒素ガスに分解する方法。   Bacillus midousuji cells (biologically pure culture of microorganisms deposited as ATCC deposit numbers 55926 and 202050 or mutant strains derived from them) and nitrate are mixed to decompose nitrate into nitrogen gas Method. Bacillus midousuji菌体(ATCC受託番号第55926号と第202050号として寄託されている微生物またはそれに由来する突然変異体株の生物学的純粋培養物)を利用して、尿素をアンモニアに分解し、アンモニアを亜硝酸塩に分解し、硝酸塩を窒素ガス、亜酸化窒素に分解する方法。   Utilizing Bacillus midousuji cells (biologically pure culture of microorganisms deposited as ATCC deposit numbers 55926 and 202050 or mutant strains derived from them), urea is decomposed into ammonia and ammonia Is a method that decomposes nitrate into nitrite, which is then decomposed into nitrogen gas and nitrous oxide. Bacillus midousuji菌体(ATCC受託番号第55926号と第202050号として寄託されている微生物またはそれに由来する突然変異体株の生物学的純粋培養物)なる一種の菌体を利用して化合物を酸化し、化合物を還元する方法。   Oxidizing compounds using a kind of fungus, Bacillus midousuji (a biologically pure culture of microorganisms deposited as ATCC Deposit Nos. 55926 and 20950 or mutant strains derived from it) A method for reducing a compound.
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009183198A (en) * 2008-02-06 2009-08-20 Sadayori Hoshina Fermented oil and method for producing the same
JP2010119937A (en) * 2008-11-18 2010-06-03 Shizunai Eiseisha:Kk Efficient nitrifying bacterium and purification process of urea and ammonia using the bacterium

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009183198A (en) * 2008-02-06 2009-08-20 Sadayori Hoshina Fermented oil and method for producing the same
JP2010119937A (en) * 2008-11-18 2010-06-03 Shizunai Eiseisha:Kk Efficient nitrifying bacterium and purification process of urea and ammonia using the bacterium

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