JPH09155385A - Treatment of garbage waste water - Google Patents
Treatment of garbage waste waterInfo
- Publication number
- JPH09155385A JPH09155385A JP7347294A JP34729495A JPH09155385A JP H09155385 A JPH09155385 A JP H09155385A JP 7347294 A JP7347294 A JP 7347294A JP 34729495 A JP34729495 A JP 34729495A JP H09155385 A JPH09155385 A JP H09155385A
- Authority
- JP
- Japan
- Prior art keywords
- decomposition
- carriers
- liquefaction
- garbage
- liquefying
- 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.)
- Pending
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Biological Treatment Of Waste Water (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は各種食品材料の調理
ゴミ及び残飯等を粉砕装置であるディスポーザーで少量
の水を加えながら粉砕した後、ディスポーザーより排出
される厨芥排水の処理方法に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating kitchen waste water discharged from a disposer after crushing cooked garbage, leftover rice and the like of various food materials with a disposer which is a crusher while adding a small amount of water. .
【0002】[0002]
【従来の技術】従来の厨芥排水処理方法で液化分解処理
は、嫌気性微生物を固形物と接触させるため、緩やかな
液化分解槽内での撹拌が必要であり、この撹拌により液
化分解槽の上部に浮上したスカムの破砕も併わせて行っ
ている。又、液化分解槽内に嫌気性微生物が希薄に分布
するため、処理効率が悪く、液化分解槽の滞留容量は常
温(20℃前後)で50〜60日、中温加温(35〜3
8℃)で30日程度である。2. Description of the Related Art The liquefaction and decomposition treatment in the conventional kitchen wastewater treatment method requires gentle agitation in the liquefaction and decomposition tank to bring anaerobic microorganisms into contact with solid matter. The scum that surfaced in the area is also crushed. Further, since the anaerobic microorganisms are dilutedly distributed in the liquefaction and decomposition tank, the treatment efficiency is poor, and the retention capacity of the liquefaction and decomposition tank is 50 to 60 days at room temperature (around 20 ° C) and medium temperature heating (35 to 3).
It is about 30 days at 8 ° C).
【0003】又、従来の厨芥排水処理方法で酸化分解処
理は活性汚泥法及び生物膜法(接触曝気)がある。しか
し、活性汚泥法は曝気槽内の汚泥濃度(MLSS)が高
くなりすぎ、浄化微生物である活性汚泥と処理水の分離
が困難である。又、生物膜法も同様に汚泥による接触濾
材の目詰まりが激しく、一週間に数回の割合で、濾材が
充填された濾床の逆洗洗浄が必要となり、維持管理が煩
雑である。In the conventional wastewater treatment method for garbage, oxidative decomposition treatment includes activated sludge method and biofilm method (contact aeration). However, in the activated sludge method, the sludge concentration (MLSS) in the aeration tank becomes too high, and it is difficult to separate the treated water from the activated sludge which is a purification microorganism. Further, similarly in the biofilm method, the contact filter medium is severely clogged with sludge, and the filter bed filled with the filter medium needs to be backwashed several times a week, and the maintenance is complicated.
【0004】[0004]
【発明が解決しようとする課題】一般に厨芥排水は各種
食品材料の調理ゴミ及び残飯等を粉砕装置であるディス
ポーザーで少量の水を加えながら粉砕され厨房より排出
される。特に厨芥排水中の微細固形物は有機物を多量に
含むことによりBOD値(生物化学的酸素要求量)、S
S値(浮遊物質量)が非常に高く、前記従来の様な一般
の浄化設備で処理することが困難である。Generally, the kitchen wastewater is crushed and discharged from the kitchen with a disposer which is a crusher while adding a small amount of water to the cooking waste and leftover food of various food materials. In particular, the fine solids in the kitchen wastewater contain a large amount of organic matter, so that the BOD value (biochemical oxygen demand), S
Since the S value (amount of suspended solids) is extremely high, it is difficult to treat it with conventional general purification equipment as described above.
【0005】上記点より本発明は、ディスポーザーで粉
砕され厨房より排出される厨芥排水中に含まれる微細生
ゴミをスカムの発生もなく効率よく液化分解すると共
に、液化分解後の厨芥排水中の有機物の好気浄化処理を
容易にし、以って汚濁負荷の大きな厨芥排水を下水道又
は河川へ放流できる清澄水に浄化することを可能とした
厨芥排水処理方法を提供しようとするものである。From the above point, the present invention efficiently liquefies and decomposes fine garbage contained in the kitchen waste water crushed by the disposer and discharged from the kitchen without generating scum, and the organic matter in the kitchen waste water after liquefaction decomposition. It is intended to provide a kitchen wastewater treatment method capable of facilitating the aerobic purification process of (1), thereby purifying kitchen wastewater having a large pollution load into clear water that can be discharged to a sewer or a river.
【0006】[0006]
【課題を解決するための手段】本発明は、液化分解処理
工程、好気処理工程及び沈澱処理工程より成る厨芥排水
処理方法に於いて、厨芥粉砕水に含まれる微細生ゴミを
嫌気性分解菌により低分子に液化させるに際し、液化分
解槽内の略中央より上方部に嫌気性微生物を担持するポ
リウレタンフォームの多数の担体を緩やかに充填し、こ
の担体の浮遊状態の濾床内に微細生ゴミを含む厨芥粉砕
水が通過し、濾過及び液化分解を受けることを特徴とす
るものである。DISCLOSURE OF THE INVENTION The present invention provides a method for treating kitchen wastewater, which comprises a liquefaction decomposition step, an aerobic treatment step, and a precipitation treatment step, in which fine garbage contained in the kitchen waste water is anaerobically decomposed. When liquefying to a low molecule by means of the above, a large number of carriers of polyurethane foam carrying anaerobic microorganisms are gently filled above the center of the liquefaction decomposition tank, and fine raw garbage is placed in the suspended filter bed of this carrier. Garbage crushed water containing is passed, filtered and liquefied and decomposed.
【0007】又、本発明は、液化分解処理工程、好気処
理工程及び沈澱処理工程より成る厨芥排水処理方法に於
いて、液化分解後の厨芥排水中の有機物を酸化分解する
に際し、好気処理槽内に好気性微生物を担持するポリウ
レタンフォームの担体を多数浮遊させ、この担体と担体
の総量に対して等量以上の液化分解後の厨芥排水とを曝
気混合することを特徴とするものである。The present invention also provides a kitchen wastewater treatment method comprising a liquefaction decomposition treatment step, an aerobic treatment step, and a precipitation treatment step, in which the organic matter in the kitchen wastewater after liquefaction decomposition is oxidatively decomposed. A large number of polyurethane foam carriers carrying aerobic microorganisms are suspended in the tank, and the carrier and the kitchen wastewater after liquefaction and decomposition in an amount equal to or more than the total amount of the carriers are aerated and mixed. .
【0008】又、本発明は、請求項1の液化分解工程及
び請求項2の好気処理工程から成ることを特徴とするも
のである。Further, the present invention is characterized by comprising the liquefaction decomposition step of claim 1 and the aerobic treatment step of claim 2.
【0009】依って、本発明は液化分解槽の略中央より
上方部が濾床となり、濾床内で嫌気性微生物を担持した
ポリウレタンフォームの担体は浮遊しており、液化分解
槽の略中央より下方部にて未分解な固形物は、この濾床
で濾過捕捉される。そして、担体表面及び担体内部の多
種多量の嫌気性分解菌の働きで液化分解される。このた
め、従来の液化分解槽の最大の弱点であったスカムの発
生が完全に抑制された。Therefore, according to the present invention, the filter bed is located above the center of the liquefaction decomposition tank, and the polyurethane foam carrier carrying the anaerobic microorganisms floats in the filter bed. Undecomposed solids in the lower part are filtered and trapped in this filter bed. Then, it is liquefied and decomposed by the action of a large amount of anaerobic degrading bacteria on the surface and inside the carrier. For this reason, the generation of scum, which is the greatest weakness of the conventional liquefaction decomposition tank, was completely suppressed.
【0010】又、ポリウレタンフォームの担体は厨芥粉
砕水が入っても吸水能力があり、水位が一気に上がらな
いため、隣接の槽内にゆっくり流れ込み流量調節の作用
も有する。又、ポリウレタンフォームの担体は緩やかに
充填されるため、目詰まりをさせずに分解できると共
に、スポンジ内で微生物が繁殖し易くなる。Further, the polyurethane foam carrier has a water-absorbing ability even when garbage crushed water enters, and since the water level does not rise at a stretch, it has a function of slowly flowing into the adjacent tank and controlling the flow rate. Moreover, since the carrier of the polyurethane foam is gently filled, it can be decomposed without clogging, and microorganisms can easily propagate in the sponge.
【0011】又、嫌気性微生物の生育地域を液化分解槽
の上下二ヶ所に分割し、それぞれを高密度に生育保持す
ることにより液化分解槽の滞留容量を常温(20℃前
後)で20日程度で十分な効果を発揮する。The anaerobic microbial growth area is divided into two upper and lower parts of the liquefaction decomposition tank, and each of them is grown and maintained at a high density so that the retention capacity of the liquefaction decomposition tank is about 20 days at room temperature (around 20 ° C). Exerts a sufficient effect.
【0012】又、本発明は、好気処理槽内で好気性微生
物を担体内で多種多量(20,000〜30,000P
PM)に生育させるため液化分解後の高濃度液に対して
も十分な浄化能力を有する。そして、担体表面は曝気
と、それに付随する槽内旋回流によって常に洗滌されて
いる。又、好気処理槽内に流入した汚濁成分は担体内部
に吸着されるため、好気処理槽内の浮遊物質濃度は低く
なる。依って、固液分離のための重力沈降型沈殿槽は能
力を発揮しやすい。In the present invention, a large amount of aerobic microorganisms (20,000 to 30,000 P) are stored in the carrier in the aerobic treatment tank.
Since it grows in PM), it has sufficient purification ability even for a high-concentration liquid after liquefaction decomposition. The surface of the carrier is constantly cleaned by aeration and accompanying swirling flow in the tank. Further, since the pollutant components flowing into the aerobic treatment tank are adsorbed inside the carrier, the concentration of suspended substances in the aerobic treatment tank becomes low. Therefore, the gravity settling type sedimentation tank for solid-liquid separation is easy to exert its capacity.
【0013】又、本発明は、厨芥粉砕水を液化分解槽で
嫌気性微生物を担持するポリウレタンフォームの担体に
より液化分解した後、好気処理槽で曝気を受け好気性微
生物を担持するポリウレタンフォームの担体により酸化
分解されるため、分解処理が容易にできるものである。The present invention also relates to a polyurethane foam carrying aerobic microorganisms which is subjected to aeration in the aerobic treatment tank after being liquefied and decomposed by the carrier of polyurethane foam carrying the anaerobic microorganisms in the liquefaction and decomposition tank. Since it is oxidatively decomposed by the carrier, it can be easily decomposed.
【0014】[0014]
【発明の実施の形態】以下、本発明方法の一実施の形態
を図面に基づき説明する。図1は本発明方法の実施に使
用する排水処理装置の断面図である。而して、図中1は
液化分解槽であり、液化分解槽1の略中央に水平に担体
流出防止網2が設置され、液化分解槽1内を上部の嫌気
濾床部1Aと下部の混合貯留部1Bに分離している。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS One embodiment of the method of the present invention will be described below with reference to the drawings. FIG. 1 is a sectional view of a wastewater treatment equipment used for carrying out the method of the present invention. In the figure, 1 is a liquefaction decomposition tank, and a carrier outflow prevention mesh 2 is installed horizontally at approximately the center of the liquefaction decomposition tank 1, and the inside of the liquefaction decomposition tank 1 is mixed with the upper anaerobic filter section 1A and the lower part. It is separated into the storage section 1B.
【0015】嫌気濾床部1A内には嫌気性微生物を担持
するポリウレタンフォームの担体3が緩やかに多数充填
されている。担体3は水と同様の状態になり浮遊する。
担体2はセル数20〜50ヶ/インチ、大きさ10〜2
0mm角、見掛け比重0.95〜1.1のポリウレタン
フォームより成っている。A large number of polyurethane foam carriers 3 carrying anaerobic microorganisms are slowly filled in the anaerobic filter bed 1A. The carrier 3 becomes in a state similar to water and floats.
Carrier 2 has 20 to 50 cells / inch and size 10 to 2
It is made of polyurethane foam having a 0 mm square and an apparent specific gravity of 0.95 to 1.1.
【0016】そして、液化分解槽1内に厨房よりの生ゴ
ミをディスポーザーで粉砕された後の微細生ゴミを含む
厨芥排水が流入管4より流入し、滞留容量を常温(20
℃前後)で混合貯留部1Bに10日、嫌気濾床部1Aに
10日と20日程度で液化処理される。[0016] Then, kitchen waste water containing fine garbage after the garbage from the kitchen is crushed by the disposer into the liquefaction decomposition tank 1 flows in through the inflow pipe 4, and the retention capacity is kept at room temperature (20
Liquefaction treatment is performed in the mixed storage portion 1B in about 10 days and in the anaerobic filter portion 1A in about 10 days and 20 days.
【0017】5は液化分解槽1に隣接する好気処理槽で
あり、好気処理槽5内に好気性微生物を担持するポリウ
レタンフォームの担体6が多数浮遊している。そして、
担体6と担体6の総量に対して等量以上の液化分解後の
厨芥排水とが曝気混合される。担体6は前記担体3と同
様の構成である。Reference numeral 5 denotes an aerobic treatment tank adjacent to the liquefaction and decomposition tank 1, in which a large number of polyurethane foam carriers 6 carrying aerobic microorganisms are suspended. And
The carrier 6 and the kitchen wastewater after liquefaction decomposition in an amount equal to or more than the total amount of the carrier 6 are aerated and mixed. The carrier 6 has the same structure as the carrier 3.
【0018】7は好気処理槽5の底部に設けた散気装置
であり、散気装置7による曝気と、それによる槽内旋回
流によって担体6の表面は常に洗滌されている。8は好
気処理槽5と好気処理槽5間に設置した担体流出防止用
のスクリーンである。尚、図中9は好気処理槽5に隣接
する沈澱槽、10は沈澱槽9内に設置したエアーリフト
ホンプである。Reference numeral 7 is an air diffuser provided at the bottom of the aerobic treatment tank 5, and the surface of the carrier 6 is constantly washed by aeration by the air diffuser 7 and the swirling flow in the tank. Reference numeral 8 is a screen for preventing carrier outflow installed between the aerobic treatment tanks 5 and 5. In the figure, 9 is a precipitation tank adjacent to the aerobic treatment tank 5, and 10 is an air lift horn installed in the precipitation tank 9.
【0019】[0019]
【発明の効果】本発明に依れば、ディスポーザーで粉砕
され厨房より排出される厨芥排水中に含まれる微細生ゴ
ミを液化分解槽で嫌気性微生物を担持したポリウレタン
フォームの担体により液化分解するため、スカムの発生
が完全に抑制されると共に、滞留容量を常温(20℃前
後)で20日程度と処理効率が向上した。又、好気性微
生物を担持したポリウレタンフォームの担体で高濃度液
の浄化を行うため、余剰汚泥の発生を極力抑えた処理方
法となる。又、微細生ゴミを液化分解槽で液体とした
後、好気処理槽で酸化分解されるため、分解処理が容易
にできる。以上の様に本発明は、厨芥排水を効率よく安
定して連続処理するため、液化分解槽及び好気処理槽に
ポリウレタンフォームを最も適した方法で担体として充
填利用する処理方法であって、従来技術より大巾な装置
の小型化と経済性の向上が図られると共に汚濁負荷の大
きな厨芥排水を清澄水とし、下水道又は河川へ放流でき
環境衛生上に寄与し得る。EFFECTS OF THE INVENTION According to the present invention, the fine garbage contained in the kitchen waste water crushed by the disposer and discharged from the kitchen is liquefied and decomposed by the carrier of polyurethane foam carrying anaerobic microorganisms in the liquefaction decomposition tank. The generation of scum was completely suppressed, and the retention efficiency was improved to about 20 days at room temperature (around 20 ° C). Further, since the high-concentration liquid is purified by the polyurethane foam carrier carrying the aerobic microorganisms, the treatment method can suppress the generation of excess sludge as much as possible. Further, since the fine garbage is liquefied in the liquefaction decomposition tank and then oxidatively decomposed in the aerobic treatment tank, the decomposition treatment can be facilitated. As described above, the present invention is a treatment method for filling and utilizing polyurethane foam as a carrier in the most suitable method in a liquefaction decomposition tank and an aerobic treatment tank in order to efficiently and stably continuously treat kitchen wastewater. It is possible to reduce the size of the equipment, which is much larger than that of technology, and to improve the economical efficiency, and to dispose of the kitchen wastewater, which has a large pollution load, as clear water and discharge it to the sewer or rivers, which can contribute to environmental hygiene.
【図1】本発明方法の実施に使用する排水処理装置の断
面図である。FIG. 1 is a cross-sectional view of a wastewater treatment equipment used for carrying out the method of the present invention.
1 液化分解槽 3 担体 5 好気処理槽 6 担体 9 沈澱槽 1 Liquefaction decomposition tank 3 Carrier 5 Aerobic treatment tank 6 Carrier 9 Precipitation tank
Claims (3)
処理工程より成る厨芥排水処理方法に於いて、厨芥粉砕
水に含まれる微細生ゴミを嫌気性分解菌により低分子に
液化させるに際し、液化分解槽内の略中央より上方部に
嫌気性微生物を担持するポリウレタンフォームの多数の
担体を緩やかに充填し、この担体の浮遊状態の濾床内に
微細生ゴミを含む厨芥粉砕水が通過し、濾過及び液化分
解を受けることを特徴とする厨芥排水処理方法。1. In a kitchen wastewater treatment method comprising a liquefaction decomposition treatment step, an aerobic treatment step, and a precipitation treatment step, when liquefying fine garbage contained in the kitchen crushed water into low molecular weight by anaerobic decomposition bacteria, The upper part of the liquefaction decomposition tank is gently filled with a large number of carriers of polyurethane foam supporting anaerobic microorganisms in the upper part of the liquefaction decomposition tank, and garbage crushed water containing fine garbage passes through the filter bed in a floating state of the carriers. A method for treating kitchen wastewater, characterized by being subjected to filtration and liquefaction decomposition.
処理工程より成る厨芥排水処理方法に於いて、液化分解
後の厨芥排水中の有機物を酸化分解するに際し、好気処
理槽内に好気性微生物を担持するポリウレタンフォーム
の担体を多数浮遊させ、この担体と担体の総量に対して
等量以上の液化分解後の厨芥排水とを曝気混合すること
を特徴とする厨芥排水処理方法。2. A kitchen wastewater treatment method comprising a liquefaction decomposition treatment step, an aerobic treatment step and a precipitation treatment step, which is preferably used in an aerobic treatment tank when oxidatively decomposing organic substances in the kitchen wastewater after liquefaction decomposition. A method for treating kitchen wastewater, characterized in that a large number of polyurethane foam carriers carrying gaseous microorganisms are suspended, and the carrier and the kitchen wastewater after liquefaction and decomposition in an amount equal to or more than the total amount of the carriers are aerated and mixed.
気処理工程から成ることを特徴とする厨芥排水処理方
法。3. A kitchen wastewater treatment method comprising the liquefaction decomposition step of claim 1 and the aerobic treatment step of claim 2.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP7347294A JPH09155385A (en) | 1995-12-13 | 1995-12-13 | Treatment of garbage waste water |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP7347294A JPH09155385A (en) | 1995-12-13 | 1995-12-13 | Treatment of garbage waste water |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH09155385A true JPH09155385A (en) | 1997-06-17 |
Family
ID=18389243
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP7347294A Pending JPH09155385A (en) | 1995-12-13 | 1995-12-13 | Treatment of garbage waste water |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH09155385A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO1999000332A1 (en) * | 1997-06-27 | 1999-01-07 | Chikashi Ishimaru | Waste water treatment apparatus and waste water treatment method |
KR100551045B1 (en) * | 2002-09-19 | 2006-02-09 | 재단법인 포항산업과학연구원 | Biological treatment method of wastewater contaminated with nitrate of high concentration |
CN104028040A (en) * | 2014-06-26 | 2014-09-10 | 董广星 | Kitchen garbage separation recycling device |
-
1995
- 1995-12-13 JP JP7347294A patent/JPH09155385A/en active Pending
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO1999000332A1 (en) * | 1997-06-27 | 1999-01-07 | Chikashi Ishimaru | Waste water treatment apparatus and waste water treatment method |
KR100551045B1 (en) * | 2002-09-19 | 2006-02-09 | 재단법인 포항산업과학연구원 | Biological treatment method of wastewater contaminated with nitrate of high concentration |
CN104028040A (en) * | 2014-06-26 | 2014-09-10 | 董广星 | Kitchen garbage separation recycling device |
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