JPS6023875B2 - Biofilm-attached filler for wastewater treatment - Google Patents

Biofilm-attached filler for wastewater treatment

Info

Publication number
JPS6023875B2
JPS6023875B2 JP57108509A JP10850982A JPS6023875B2 JP S6023875 B2 JPS6023875 B2 JP S6023875B2 JP 57108509 A JP57108509 A JP 57108509A JP 10850982 A JP10850982 A JP 10850982A JP S6023875 B2 JPS6023875 B2 JP S6023875B2
Authority
JP
Japan
Prior art keywords
biofilm
filler
wastewater
paint
wastewater treatment
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
Application number
JP57108509A
Other languages
Japanese (ja)
Other versions
JPS59382A (en
Inventor
立夫 角野
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 Technologies Ltd
Original Assignee
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 Technologies Ltd filed Critical Hitachi Plant Technologies 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

Landscapes

  • Biological Treatment Of Waste Water (AREA)

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、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。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a filler used for biological treatment of wastewater, in which microorganisms are attached to the filler in the form of a film, and wastewater is treated by contacting the biofilm.

従釆、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、また流動層型の充填材としては砂、アンスラサ
ィト等の粒状体が使用されている。
There are two types of biofilm treatment methods for wastewater: a fixed bed type and a fluidized bed type. The filling material for the fixed bed type is plate-shaped, corrugated plate-shaped, or mesh-shaped plastics such as vinyl chloride and polyethylene. In addition, granular materials such as sand and anthracite are used as fluidized bed fillers.

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、また生物膜が付着しても剥離
すると、もう一度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。本発明の目的は、前記従来技術の
欠点を解消し、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、坦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。
These fillers do not allow biofilm to adhere for a long period of time from the start of wastewater treatment operations, and even if biofilm does adhere, once it peels off, it takes a long time for it to attach again, and no biofilm is attached. The disadvantage was that the quality of the treated water deteriorated significantly during this period. The purpose of the present invention is to eliminate the drawbacks of the prior art as described above, to enable biofilm to adhere quickly at the start of operation, to quickly regenerate even if the biofilm detaches, and to always provide stable and good quality treated water. The objective is to provide a filler material that can be formed by immobilizing a microbial inoculum on the surface of a carrier.

即ち、本発明による充填材は、プラスチック、砂、アン
スラサィト等の坦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。
That is, the filler according to the present invention is characterized in that a paint containing microorganisms is applied to the surface of a carrier such as plastic, sand, or anthracite.

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
、ェポキシ系樹脂塗料、アクリルィミド系樹脂塗料、ア
クリルアミド系樹脂塗料、スチレン系樹脂塗料、多糠類
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、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。
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, bran derivative paints, polyurethane resin paints, and vinyl resin paints. Any paint can be used as long as it solidifies when left at room temperature or 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、坦体表面に塗布し
、塗膜を固化させると、微生物が固定された充填材が得
られる。
When microorganisms are mixed in such a paint, applied to the surface of a carrier, and the paint film is solidified, a filler in which microorganisms are immobilized can be obtained.

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、種菌が存在するため生物
膜が迅速に再生する。次に、実施例に基づいて本発明を
詳述するが、本発明はこれに限定されるものでではない
The microorganisms fixed in this way act as seed bacteria, and a biofilm quickly attaches to the surface of the filler at the start of wastewater treatment.
Furthermore, even if peeling occurs during operation, the biofilm is quickly regenerated because of the presence of seed bacteria. Next, the present invention will be described in detail based on Examples, but the present invention is not limited thereto.

実施例 1アクリルアミド及びN,N′ーメチレンビス
アクリルアミド等を主成分とするアクリルァミド系樹脂
塗料2そに、N社食品廃水で馴萎した汚泥をM比SSが
500雌/夕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。
Example 1: Acrylamide-based resin paint containing acrylamide and N,N'-methylenebisacrylamide as main components 2: Add sludge that has been acclimatized with N company food wastewater so that the M ratio SS is 500 females/day This paint was then applied to a vinyl chloride corrugated board.

塗布する塗料の厚さは10ム〜1脇の程度であってよい
。こうして得た充填材を3めの暖気槽に充填率60%、
充填材の間隔2物収‘こ充填した。この蟻気糟を用いて
滞留時間6時間で80D300雌/その廃水を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。期間中pH7,溶存酸素3〜5のo/そで処理を
行なった。3日目までは、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。
The thickness of the paint applied may be on the order of 10 mm to 1 mm. Filling material obtained in this way was placed in the third warming tank at a filling rate of 60%.
Two pieces of filling material were filled in each interval. Using this ant cage, wastewater from 80D300 females 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. During the period, O/Sleeve treatment was performed at pH 7 and dissolved oxygen 3 to 5. Until the third day, the water quality was poor, but from the fourth day, the biofilm had grown to the point that it was clearly visible to the naked eye, and good 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、爆気槽に種汚泥として汚泥を2000mc/〆添加
する以外は同じ条件で、同じ廃水を処理し、結果が第2
図に示す。
As a conventional method, the same wastewater was treated under the same conditions except that a paint containing microorganisms was not applied to the filler and sludge was added to the blast tank as seed sludge at a rate of 2000 mc/〆.
As shown in the figure.

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‘こ付着し始め、その後水質が良くなった。実
施例 2 純粋培養した枯草菌(Bacill雌s肋tilis)
を遠心分離し、濃縮し、細胞1び個/泌になるようにア
クリルアミド系樹脂塗料に混合した。
At first, the treated water became cloudy and the water quality fluctuated and was not stable.Biofilm began to form on the 8th day, but the water quality improved thereafter. Example 2 Pure culture of Bacillus subtilis
The cells were centrifuged, concentrated, and mixed with acrylamide resin paint at a concentration of 1 cell/secretion.

この塗料を直径0.5柵の砂に塗布し、35qoで30
分間で固化した。塗布する塗料の厚さは10山〜1肋程
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1のの曝気槽に充填率30%で充渡し
、曝気により流動させ、膨張率50%で、BOD200
岬/そのK社生産工程廃水を滞留時間5時間で連続処理
した。30日間運転した結果を第3図に示す。
Apply this paint to sand with a diameter of 0.5 and apply it to 30 qo at 35 qo.
It solidified in minutes. The thickness of the paint to be applied may be about 10 to 1 thick, and the temperature at which it solidifies is not limited thereto. This sand was filled into the aeration tank of No. 1 with a filling rate of 30%, and was fluidized by aeration, with an expansion rate of 50% and a BOD of 200.
Misaki/The wastewater from the production process of Company K was continuously treated with a residence time of 5 hours. Figure 3 shows the results after 30 days of operation.

2日目で処理水は安定し、生物膜の繁殖も良好であった
The treated water became stable on the second day, and the growth of biofilm 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、
顔気槽に汚泥を2000のo/〆添加する以外は、同じ
条件で同じ廃水を処理した結果を第4図に示す。
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 tank at a rate of 2000 o/l.

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。実施例1及び2かが判るとおり、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、一貫して良好な処理水が得られた
Biofilm started to adhere on the 5th day, after which the water quality improved. As can be seen from Examples 1 and 2, in the present invention, biofilm adheres to the filler material quickly, and even if the biofilm peels off during long-term operation, the inoculum is fixed by the paint, so the biofilm can be regenerated. was carried out quickly and consistently good 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繋断力に
よる剥離が起りやすく、処理水質が不安定であった。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。
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 the tethering force, resulting in unstable treated water quality. In the above example, an acrylamide resin paint was used, but
Equally good results can be obtained using other paints.

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

第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爆気処理の場合の処理水
のBODの蓬日変化図、第3図は本発明の充填材を使用
して廃水を流動床型暖気処理した場合の処理水の800
の経日変化図、第4図は従来法による流動床型暖気処理
の場合の処理水のBOOの経日変化図である。 第l図 第2図 第3図 第4図
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 diurnal variation of BOD of treated water in the case of fixed bed type catalytic explosion treatment using the conventional method, and Figure 3 shows the treated water in the case of fluidized bed type warm air treatment of wastewater using the filler of the present invention. 800 of
FIG. 4 is a diagram showing the daily change in BOO of treated water in the case of fluidized bed warm air treatment according to the conventional method. Figure l Figure 2 Figure 3 Figure 4

Claims (1)

【特許請求の範囲】 1 プラスチツク、砂、アンスラサイト等の坦体の表面
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充填材。 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。
[Scope of Claims] 1. A biofilm-adhering filler for wastewater treatment, characterized in that a paint containing microorganisms is applied to the surface of a carrier such as plastic, sand, anthracite, etc. 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 JPS59382A (en) 1984-01-05
JPS6023875B2 true 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)

Families Citing this family (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0632824B2 (en) * 1985-02-27 1994-05-02 三菱樹脂株式会社 Microorganism support
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
JPH0632826B2 (en) * 1985-05-28 1994-05-02 三菱樹脂株式会社 Method for manufacturing microorganism holding plate
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
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

Also Published As

Publication number Publication date
JPS59382A (en) 1984-01-05

Similar Documents

Publication Publication Date Title
Yang et al. Inhibition of free ammonia to the formation of aerobic granules
EP3411339B1 (en) Process for aerobic nitritation of ammonia
US6444459B1 (en) Apparatus having pitted or cratered inner surface for culturing biological material and methods thereof
JPS6023875B2 (en) Biofilm-attached filler for wastewater treatment
CN106542655A (en) A kind of efficient denitrification microbial bacterial agent rapid biofilm method
FI973306A0 (en) Process for the preparation of open cell plant media and plant media
CN101913710A (en) Suspended packing microbial quick film forming method
CN109912014A (en) A kind of preparation method of high activity biofilm biologic packing material
CN110407336A (en) A kind of wet preservation and method for activation recovering based on MBBR autotrophic denitrification suspending carrier
JPH10327850A (en) Microelement/inorganic nutrient salt diffusion-type carrier for microbial cell culture
CA2348520A1 (en) Nitrification process
CN103949116B (en) A kind of can as the gel combined filtration of microbe carrier continuous and preparation method
CN108148828A (en) It is a kind of using gypsum as the method for carrier immobilized Nitrite bacteria
JPS6154292A (en) Two-phase mathane fermenting method by immobilized microbe
DE59504103D1 (en) Process and reactor for microbiological water treatment with high oxygen demand
JPS63202382A (en) Immobilized microorganism group
JPS6231637B2 (en)
CN110304715A (en) A kind of MBBR biofilm method suitable for sanitary sewage
DE3865696D1 (en)
JPS62186995A (en) Microorganism immobilized carrier for waste water treatment and its production
JPH05123694A (en) Treatment of organic waste water with nitrogen fixation bacterial
JPS6154294A (en) Treatment of high concentrated organic waste water
JPS6353879B2 (en)
JPS606200B2 (en) Method for producing dextrorotatory lactic acid using spore-forming bacteria
EP1050578B1 (en) Apparatus and methods for culturing biological material