JPS59382A - Packing material adherering biomembane for waste water disposal - Google Patents

Packing material adherering biomembane for waste water disposal

Info

Publication number
JPS59382A
JPS59382A JP57108509A JP10850982A JPS59382A JP S59382 A JPS59382 A JP S59382A JP 57108509 A JP57108509 A JP 57108509A JP 10850982 A JP10850982 A JP 10850982A JP S59382 A JPS59382 A JP S59382A
Authority
JP
Japan
Prior art keywords
paint
microbe
waste water
packing material
biofilm
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.)
Granted
Application number
JP57108509A
Other languages
Japanese (ja)
Other versions
JPS6023875B2 (en
Inventor
Tatsuo Sumino
立夫 角野
Ichiro Nakajima
一郎 中島
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.)
Hitachi Plant Construction Co Ltd
Hitachi Plant Technologies Ltd
Original Assignee
Hitachi Plant Construction Co Ltd
Hitachi Plant Technologies 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 Hitachi Plant Construction Co Ltd, Hitachi Plant Technologies Ltd filed Critical Hitachi Plant Construction Co Ltd
Priority to JP57108509A priority Critical patent/JPS6023875B2/en
Publication of JPS59382A publication Critical patent/JPS59382A/en
Publication of JPS6023875B2 publication Critical patent/JPS6023875B2/en
Expired legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Abstract

PURPOSE:To obtain a pcking material for waste water disposal which can produce treated water stably at all times, by applying microbe-contg. paint onto the surface of a carrier such as plastics. CONSTITUTION:Microbe-contg. paint is applied onto the surface of a carrier such as plastics, sand or anthracite. A product obtd. by purely or mixedly cultivating bacteria, mold, yeast, etc. is used as said microbe, while acryl or epoxy resin paint or the like thereon is used as said paint. Thus, a packing material having adhered microbe immobilized is obtained, biomembranes rapidly adhere to the surface of said packing material at the time of staring the operation of waste water disposal, and the biomembranes rapidly regenerates themselves even when their exfoliation is caused during the operation.

Description

【発明の詳細な説明】 本発明は、微生物を充填材に膜状に付着させ。[Detailed description of the invention] In the present invention, microorganisms are attached to a filler in a film form.

廃水を生物膜に接触させて処理する。廃水の生物学的処
理に用いる充填材に関する。
Wastewater is treated by contacting it with biofilm. This invention relates to fillers used in biological treatment of wastewater.

従来、廃水の生物膜処理法には固定層型と流動層型があ
り、固定層型の充填材としては塩化ビニル、ポリエチレ
ン等のプラスチックの板状、波板状、網目状のものが用
いられ、捷だ流動層型の充填材としては砂、アンスラサ
イト等の粒状体が使用されている。これらの充填材は廃
水処理の運転開始から長期間にわたって生物膜を付着し
難く。
Traditionally, there are two types of biofilm treatment methods for wastewater: fixed bed type and fluidized bed type, and the filling material for fixed bed type is plate-shaped, corrugated plate-shaped, or mesh-shaped plastics such as vinyl chloride and polyethylene. Granular materials such as sand and anthracite are used as the filler for the shattered fluidized bed type. These fillers are difficult to adhere to biofilm over a long period of time from the start of wastewater treatment operations.

また生物膜が付着しても剥離すると、もう−膜付着する
までに長期間を要し、生物膜が付着していない期間の処
理水の水質が極めて悪化するという欠点があった。
Furthermore, even if a biofilm is attached, if it is peeled off, it takes a long time for the biofilm to attach again, and the quality of the treated water deteriorates significantly during the period when the biofilm is not attached.

本発明の目的は、前記従来技術の欠点を解消し。The object of the present invention is to overcome the drawbacks of the prior art.

運転開始時の生物膜の付着が早く、生物膜が剥離しても
迅速に再生することができ、常に安定して良好な処理水
を生ずることのできる充填材を提供することにあり、担
体表面に微生物の種菌を固定することによって達成され
る。
Our objective is to provide a filler that allows biofilm to adhere quickly at the start of operation, can be quickly regenerated even if the biofilm is detached, and can always produce stable and good quality treated water. This is achieved by immobilizing a microbial inoculum on a microorganism.

即ち1本発明による充填材は、プラスチック。Namely, one filler according to the present invention is plastic.

砂、アンスラサイト等の担体の表面に微生物を含有する
塗料を塗布したことを特徴とする。
It is characterized by coating the surface of a carrier such as sand or anthracite with a paint containing microorganisms.

微生物は、細菌、カビ、酵母、放線菌、藻類等の純粋培
養したものまたは混合培養した微生物であってよい。
The microorganism may be a pure culture or a mixed culture of bacteria, mold, yeast, actinomycetes, algae, and the like.

本発明に使用しうる塗料としては、アクリル系樹脂塗料
、エポキシ系樹脂塗料、アクリルイミド系樹脂塗料、ア
クリルアミド系樹脂塗料、スチレン系樹脂塗料、多糖類
誘導体塗料、ポリウレタン系樹脂塗料、ビニール系樹脂
塗料等が挙げられ。
Paints that can be used in the present invention include acrylic resin paints, epoxy resin paints, acrylimide resin paints, acrylamide resin paints, styrene resin paints, polysaccharide derivative paints, polyurethane resin paints, and vinyl resin paints. etc. are mentioned.

常温放置または微生物が死滅しない程度の加温により固
化し、固化後には微生物を液中に放出しないものであれ
ば、任意の塗料を使用することができる。
Any paint can be used as long as it solidifies when left at room temperature or is heated to an extent that does not kill microorganisms, and does not release microorganisms into the liquid after solidification.

このような塗料中に微生物を混合し、担体表面、(塗布
し、塗膜を固化させると、微生物が固定さ馴←充填材が
得られる。こうして固定された微生物は種菌として作用
し、廃水処理の運転開始時に充填材表面に迅速に生物膜
が付着し、また運転中に剥離が起っても9種菌が存在す
るため生物膜が迅速に再生する。
When microorganisms are mixed in such a paint and applied to the surface of a carrier, and the paint film is solidified, the microorganisms become immobilized and become accommodating.A filler is obtained. A biofilm quickly adheres to the surface of the filler at the start of operation, and even if peeling occurs during operation, the biofilm is quickly regenerated because of the presence of nine types of bacteria.

次に、実施例に基づいて本発明を詳述するが。Next, the present invention will be explained in detail based on examples.

本発明はこれに限定されるものではな−。The present invention is not limited to this.

実施例 l アクリルアミド及びN 、 N/−メチレンビスアクリ
ルアミド等を主成分とするアクリルアミド系樹脂塗料2
tに、N社食品廃水で馴養した汚泥をM L S Sが
500m9/lになるように添加し、この塗料を塩化ビ
ニル波板に塗布した。塗布する塗料の厚さは10μ〜l
I+III+の程度であってよい。こうして得た充填材
を3m3 の曝気槽に充填率60%、充填材の間隔20
I+++++に充填した。この曝気槽を用いて滞留時間
6時間でBOD500mg/lの廃水を30日間連続処
理し、処理水のBODを測定し、結果を第1図に示す。
Example l Acrylamide-based resin paint 2 containing acrylamide and N, N/-methylenebisacrylamide, etc. as main components
t, sludge acclimatized with food wastewater from Company N was added so that the M L S S was 500 m9/l, and this paint was applied to a vinyl chloride corrugated plate. The thickness of the paint to be applied is 10 μ to 1
It may be of the order of I+III+. The filler thus obtained was placed in a 3 m3 aeration tank with a filling rate of 60% and an interval of 20
I++++++ was filled. Using this aeration tank, wastewater with a BOD of 500 mg/l was continuously treated for 30 days with a residence time of 6 hours, and the BOD of the treated water was measured. The results are shown in FIG.

期間中pH・7.溶存ξ素3〜5m9/lで処理を行な
った。3日目まで:!!、!J、水質が悪かったが、4
日目から生物膜が肉眼−ではっきり判る程、繁殖し、良
好な処理水・が得られた。
During the period pH 7. The treatment was carried out with 3 to 5 m9/l of dissolved ξ element. Until the third day:! ! ,! J. The water quality was poor, but 4
From day 1, the biofilm grew to the extent that it was clearly visible to the naked eye, and good quality treated water was obtained.

従来法として、充填材に微生物を含む塗料を塗布しない
で、曝気槽に種汚泥として汚泥を2000mg / z
添加する以外は同じ条件で、同じ廃水を処理し、結果を
第2図に示す。当初、処理水は白濁し、水質が変動し安
定せず、生物膜は8日目に付着し始め、その後水質が良
くなった。
As a conventional method, 2000 mg/z of sludge is added as seed sludge to the aeration tank without applying paint containing microorganisms to the filler.
The same wastewater was treated under the same conditions except for the addition of the compound, and the results are shown in FIG. At first, the treated water was cloudy and the water quality fluctuated and was unstable, and biofilm started to form on the 8th day, after which the water quality improved.

実施例 2 純粋培養した枯草菌(BacillLLs sLLbt
itig )を遠心分離し、濃縮し、細胞]o8  個
/mlになるようにアクリルアミド系樹脂塗料に混合し
た。この塗料を直径0.5111111の砂に塗布し、
35℃で30分間で固化した。塗布する塗料の厚さは1
0μ〜l議程度であってよく、固化する温度はこれに限
定されるものでない。この砂をl m3  の曝気槽に
充填率30%で充填し、曝気により流動させ、膨張率5
0%で、BOD200m9/1(DK社生産工程凰水を
滞留時間5時間で連続処理した。30日間珈■した結果
を第3図に示す。2日目で処理水は(定し、生物膜の繁
殖も良好であった。
Example 2 Purely cultured Bacillus subtilis (BacillLLs sLLbt)
itig) was centrifuged, concentrated, and mixed into an acrylamide resin paint at a concentration of 08 cells/ml. Apply this paint to sand with a diameter of 0.5111111,
It was solidified at 35°C for 30 minutes. The thickness of the paint to be applied is 1
The solidification temperature may be about 0 μ to 1 μm, and the solidification temperature is not limited thereto. This sand was filled in an aeration tank of 1 m3 at a filling rate of 30%, and was made to flow by aeration, and the expansion rate was 5.
0%, BOD 200 m9/1 (DK company production process 凰水) was continuously treated with a residence time of 5 hours. The results after 30 days of boiling are shown in Figure 3. On the second day, the treated water became The breeding was also good.

従来法として、砂に微生物を含む塗料を塗布しないで、
曝気槽に汚泥を2000■/を添加する以外は、同じ条
件で同じ廃水を処理した結果を第4図に示す。生物膜は
5日目に付着し始め、その後に水質が良くなった。
Conventional methods do not apply paint containing microorganisms to the sand.
Figure 4 shows the results of treating the same wastewater under the same conditions except that sludge was added to the aeration tank at a rate of 2,000 μ/cm. Biofilm started to adhere on the 5th day, after which the water quality improved.

実施例1及び2から判るとおり1本発明では充填材に生
物膜が早く付着し、長期間運転中に生物膜が剥離しても
、塗料により種菌が固定されているため、生物膜の再生
が早く行な゛われ、−貫して良好な処理水が得られた。
As can be seen from Examples 1 and 2, in the present invention, biofilm quickly adheres to the filler, and even if the biofilm peels off during long-term operation, the inoculum is fixed by the paint, so the biofilm cannot be regenerated. The process was carried out quickly and a consistently good quality of treated water was obtained.

これに反して、従来法では生物膜の付着が遅いばかりで
なく、長期間運転すると生物膜が肥厚しすぎて剪断力に
よる剥離が起りやすく、処理水質が不安定であった。
On the other hand, in the conventional method, not only was the biofilm attached slowly, but also the biofilm became too thick during long-term operation and was likely to peel off due to shearing force, resulting in unstable treated water quality.

前記実施例ではアクリルアミド系樹脂塗料を使用したが
、他の塗料を使用しても同様に良好な結果が得られる。
Although an acrylamide-based resin paint was used in the above examples, similar good results can be obtained by using other paints.

【図面の簡単な説明】[Brief explanation of the drawing]

盪1図は本発明の充填材を使用して廃水を固定床型接触
曝気処理した場合の処理水のBODの経日変化図、第2
図は従来法による固定床型接触曝気処理の場合の処理水
のBODの経口変化図、第3図は本発明の充填材を使用
して廃水を流動床型曝気処理した場合の処理水のBOD
の経日変化図。 第4図は従来法による流動床型曝気処理の場合の処理水
のBODの経日変化図である。
(2) Figure 1 is a diagram of the daily change in BOD of treated water when wastewater is subjected to fixed-bed contact aeration treatment using the filler of the present invention.
The figure shows the oral change in BOD of treated water in the case of fixed bed type contact aeration treatment using the conventional method. Figure 3 shows the BOD of treated water in the case of fluidized bed type aeration treatment of wastewater using the filler of the present invention.
Diagram of changes over time. FIG. 4 is a diagram showing the daily change in BOD of treated water in the case of fluidized bed aeration treatment according to the conventional method.

Claims (2)

【特許請求の範囲】[Claims] (1)  プラスチック、砂、アンスラサイト等の担体
の表面に微生物を含有する塗料を塗布したことを特徴と
する廃水処理用の生物膜付着光*桐。
(1) Biofilm-attached light * Paulownia for wastewater treatment, which is characterized by coating the surface of a carrier such as plastic, sand, or anthracite with a paint containing microorganisms.
(2)純粋培養した微生物または混合培養した微生物を
混合した塗料を使用した特許請求の範囲第1項記載の充
填材。
(2) The filler according to claim 1, which uses a paint containing pure cultured microorganisms or mixed cultured microorganisms.
JP57108509A 1982-06-25 1982-06-25 Biofilm-attached filler for wastewater treatment Expired JPS6023875B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57108509A JPS6023875B2 (en) 1982-06-25 1982-06-25 Biofilm-attached filler for wastewater treatment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57108509A JPS6023875B2 (en) 1982-06-25 1982-06-25 Biofilm-attached filler for wastewater treatment

Publications (2)

Publication Number Publication Date
JPS59382A true JPS59382A (en) 1984-01-05
JPS6023875B2 JPS6023875B2 (en) 1985-06-10

Family

ID=14486579

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57108509A Expired JPS6023875B2 (en) 1982-06-25 1982-06-25 Biofilm-attached filler for wastewater treatment

Country Status (1)

Country Link
JP (1) JPS6023875B2 (en)

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61197095A (en) * 1985-02-27 1986-09-01 Mitsubishi Plastics Ind Ltd Microbe carrier
JPS61209091A (en) * 1985-03-09 1986-09-17 Shimizu Constr Co Ltd Concentrated bacteria carrier for treating organic waste water
JPS61271092A (en) * 1985-05-28 1986-12-01 Mitsubishi Plastics Ind Ltd Preparation of holding plate for microorganism
JPS62136292A (en) * 1985-12-10 1987-06-19 Takuma Co Ltd Method for inclusive immobilization of biological reaction promoter and two-layer utilization of said promoter in sewage denitrifying operation
JPS62155990A (en) * 1985-12-27 1987-07-10 Takenaka Komuten Co Ltd Plate-shaped bioreactor
US4804576A (en) * 1985-02-28 1989-02-14 Canon Kabushiki Kaisha Elastic rotatable member
FR2681591A1 (en) * 1991-09-20 1993-03-26 Pronatec WATER PURIFICATION MATERIAL, COMPRISING NATURAL CELLS, AND PROCESS FOR OBTAINING THE SAME.
KR20010003825A (en) * 1999-06-25 2001-01-15 윤창진 Media coated with microscopic organism and method for coating them
CN105948400A (en) * 2016-06-22 2016-09-21 内蒙古阜丰生物科技有限公司 Environment-friendly technique for restoring L-threonine fermentation wastewater
CN106006997A (en) * 2016-06-03 2016-10-12 北京荣蒂盛环境科技有限公司 Sewage ecological water-purification system

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61197095A (en) * 1985-02-27 1986-09-01 Mitsubishi Plastics Ind Ltd Microbe carrier
US4804576A (en) * 1985-02-28 1989-02-14 Canon Kabushiki Kaisha Elastic rotatable member
JPS61209091A (en) * 1985-03-09 1986-09-17 Shimizu Constr Co Ltd Concentrated bacteria carrier for treating organic waste water
JPS61271092A (en) * 1985-05-28 1986-12-01 Mitsubishi Plastics Ind Ltd Preparation of holding plate for microorganism
JPS62136292A (en) * 1985-12-10 1987-06-19 Takuma Co Ltd Method for inclusive immobilization of biological reaction promoter and two-layer utilization of said promoter in sewage denitrifying operation
JPH0714517B2 (en) * 1985-12-10 1995-02-22 株式会社タクマ Sewage denitrification method
JPS62155990A (en) * 1985-12-27 1987-07-10 Takenaka Komuten Co Ltd Plate-shaped bioreactor
FR2681591A1 (en) * 1991-09-20 1993-03-26 Pronatec WATER PURIFICATION MATERIAL, COMPRISING NATURAL CELLS, AND PROCESS FOR OBTAINING THE SAME.
KR20010003825A (en) * 1999-06-25 2001-01-15 윤창진 Media coated with microscopic organism and method for coating them
CN106006997A (en) * 2016-06-03 2016-10-12 北京荣蒂盛环境科技有限公司 Sewage ecological water-purification system
CN105948400A (en) * 2016-06-22 2016-09-21 内蒙古阜丰生物科技有限公司 Environment-friendly technique for restoring L-threonine fermentation wastewater
CN105948400B (en) * 2016-06-22 2018-11-16 内蒙古阜丰生物科技有限公司 A kind of environment-protective process for repairing L-threonine fermentation waste water

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