JP2000015233A - Apparatus for treating kitchen refuse and method for operating the apparatus - Google Patents
Apparatus for treating kitchen refuse and method for operating the apparatusInfo
- Publication number
- JP2000015233A JP2000015233A JP20115098A JP20115098A JP2000015233A JP 2000015233 A JP2000015233 A JP 2000015233A JP 20115098 A JP20115098 A JP 20115098A JP 20115098 A JP20115098 A JP 20115098A JP 2000015233 A JP2000015233 A JP 2000015233A
- Authority
- JP
- Japan
- Prior art keywords
- garbage
- treatment
- wastewater
- unit
- processing
- 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
- 238000000034 method Methods 0.000 title claims description 17
- 238000011282 treatment Methods 0.000 claims abstract description 37
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 22
- 244000005700 microbiome Species 0.000 claims abstract description 13
- 230000003647 oxidation Effects 0.000 claims abstract description 10
- 238000007254 oxidation reaction Methods 0.000 claims abstract description 10
- 238000004332 deodorization Methods 0.000 claims abstract description 7
- 238000000354 decomposition reaction Methods 0.000 claims abstract description 6
- 230000000873 masking effect Effects 0.000 claims abstract description 4
- 238000001179 sorption measurement Methods 0.000 claims abstract description 4
- 239000010813 municipal solid waste Substances 0.000 claims description 73
- 239000010806 kitchen waste Substances 0.000 claims description 27
- 238000012545 processing Methods 0.000 claims description 27
- 239000002351 wastewater Substances 0.000 claims description 25
- 238000000926 separation method Methods 0.000 claims description 15
- 241001465754 Metazoa Species 0.000 claims description 12
- 238000004065 wastewater treatment Methods 0.000 claims description 12
- 239000007788 liquid Substances 0.000 claims description 8
- 238000001035 drying Methods 0.000 claims description 5
- 230000000813 microbial effect Effects 0.000 claims description 5
- 241000902900 cellular organisms Species 0.000 claims description 4
- 239000012528 membrane Substances 0.000 claims description 4
- 230000001877 deodorizing effect Effects 0.000 claims description 3
- 238000001914 filtration Methods 0.000 claims description 2
- 239000002689 soil Substances 0.000 claims 1
- 230000007613 environmental effect Effects 0.000 abstract description 8
- 235000019645 odor Nutrition 0.000 abstract description 7
- 239000007787 solid Substances 0.000 abstract description 7
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 abstract description 5
- 238000003912 environmental pollution Methods 0.000 abstract description 5
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 abstract description 4
- 239000003054 catalyst Substances 0.000 abstract description 3
- 229910052799 carbon Inorganic materials 0.000 abstract 1
- 238000000197 pyrolysis Methods 0.000 abstract 1
- 239000010802 sludge Substances 0.000 description 12
- 238000004062 sedimentation Methods 0.000 description 7
- 239000007789 gas Substances 0.000 description 6
- 238000012805 post-processing Methods 0.000 description 5
- 239000002699 waste material Substances 0.000 description 5
- 238000010411 cooking Methods 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 238000004064 recycling Methods 0.000 description 3
- IKHGUXGNUITLKF-UHFFFAOYSA-N Acetaldehyde Chemical compound CC=O IKHGUXGNUITLKF-UHFFFAOYSA-N 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- FERIUCNNQQJTOY-UHFFFAOYSA-N Butyric acid Chemical compound CCCC(O)=O FERIUCNNQQJTOY-UHFFFAOYSA-N 0.000 description 2
- 238000005273 aeration Methods 0.000 description 2
- 230000006866 deterioration Effects 0.000 description 2
- XBDQKXXYIPTUBI-UHFFFAOYSA-N dimethylselenoniopropionate Natural products CCC(O)=O XBDQKXXYIPTUBI-UHFFFAOYSA-N 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 238000000855 fermentation Methods 0.000 description 2
- 230000004151 fermentation Effects 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 230000001699 photocatalysis Effects 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 238000003672 processing method Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000005979 thermal decomposition reaction Methods 0.000 description 2
- GETQZCLCWQTVFV-UHFFFAOYSA-N trimethylamine Chemical compound CN(C)C GETQZCLCWQTVFV-UHFFFAOYSA-N 0.000 description 2
- 241000934653 Dero Species 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 description 1
- 241000142935 Macrobiotus Species 0.000 description 1
- 241000180652 Philodina Species 0.000 description 1
- 241000868220 Vorticella Species 0.000 description 1
- 150000001299 aldehydes Chemical class 0.000 description 1
- 150000001412 amines Chemical class 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000011324 bead Substances 0.000 description 1
- 238000006065 biodegradation reaction Methods 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 238000009264 composting Methods 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 235000019256 formaldehyde Nutrition 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- WSFSSNUMVMOOMR-NJFSPNSNSA-N methanone Chemical compound O=[14CH2] WSFSSNUMVMOOMR-NJFSPNSNSA-N 0.000 description 1
- 238000001471 micro-filtration Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 235000005985 organic acids Nutrition 0.000 description 1
- 239000011368 organic material Substances 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000012071 phase Substances 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 235000019260 propionic acid Nutrition 0.000 description 1
- IUVKMZGDUIUOCP-BTNSXGMBSA-N quinbolone Chemical compound O([C@H]1CC[C@H]2[C@H]3[C@@H]([C@]4(C=CC(=O)C=C4CC3)C)CC[C@@]21C)C1=CCCC1 IUVKMZGDUIUOCP-BTNSXGMBSA-N 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000007790 solid phase Substances 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- 238000000108 ultra-filtration Methods 0.000 description 1
- 238000004069 wastewater sedimentation Methods 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
- 235000020681 well water Nutrition 0.000 description 1
- 239000002349 well water Substances 0.000 description 1
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)
- Processing Of Solid Wastes (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】本発明は家庭や、工場などで
発生する厨芥を処理する厨芥処理装置とその運転方法に
関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a garbage processing apparatus for processing garbage generated in homes and factories, and a method of operating the same.
【0002】[0002]
【従来の技術】各家庭で発生する厨芥を台所に設置した
粉砕機で粉砕した後、配管移送し、厨芥処理する方法と
して、特開平03ー89954号広報、特開平04ー3
05284号広報や、特開平06ー55158号広報に
開示される処理方法が知られている。2. Description of the Related Art As a method for treating kitchen waste generated by crushing kitchen waste generated in each home by a pulverizer installed in the kitchen, transferring the pipes, and processing the kitchen waste, JP-A-03-89954 and JP-A-Heisei 04-3 are known.
The processing methods disclosed in JP-A-05284 and JP-A-06-55158 are known.
【0003】また、粉砕機を用いない方法に特開平05
ー208186号広報に開示される方法がある。これら
の発明はすべて、厨芥を衛生的に処理することを主眼と
している。Further, a method without using a pulverizer is disclosed in
There is a method disclosed in -208186. All of these inventions focus on sanitary disposal of kitchen waste.
【0004】特開平03ー89954号広報や特開平0
4ー305284号広報に開示される厨芥処理装置は、
厨芥を粉砕機で粉砕し、後処理部へ移送した後、固液分
離により厨芥固形物を回収後、処理する。固液分離で粉
砕厨芥を回収した時に発生する排水はそのまま環境中に
放流される。Japanese Patent Application Laid-Open No. 03-89954 and Japanese Patent Application Laid-Open
The kitchen garbage disposal device disclosed in 4-305284 No.
After the garbage is crushed by a crusher and transferred to a post-processing section, the garbage solids are recovered by solid-liquid separation and then processed. Wastewater generated when the crushed garbage is collected by solid-liquid separation is discharged into the environment as it is.
【0005】特開平06ー55158号広報に開示され
る処理方法は、集合住宅の各家庭の台所に設置した厨芥
粉砕機で厨芥を粉砕し、水で配管移送させ、1ヶ所でま
とめて厨芥処理するものである。厨芥処理は、厨芥を含
む排水から固液分離で厨芥を回収し、固相発酵で堆肥化
してリサイクルをめざすもので、厨芥固形物の処理のみ
が行われる。[0005] A processing method disclosed in Japanese Patent Application Laid-Open No. 06-55158 discloses a method of crushing garbage with a garbage crusher installed in the kitchen of each household in an apartment complex, transferring the tubing with water, and collecting the garbage in one place. Is what you do. Garbage disposal involves collecting garbage from wastewater containing garbage by solid-liquid separation, composting it by solid-phase fermentation, and aiming for recycling. Only garbage solids are processed.
【0006】特開平05ー208186号広報に開示さ
れる処理方法は、厨芥をピストンで圧搾して脱水、体積
減容化して廃棄時の取り扱い性を改善するとともに、圧
搾された排水をオゾンで酸化して、水中に抽出された臭
気成分、汚濁成分を酸化処理するものである。[0006] The treatment method disclosed in Japanese Patent Application Laid-Open No. 05-208186 discloses a method in which kitchen waste is squeezed with a piston to dewater and reduce the volume to improve the handleability at the time of disposal, and the compressed wastewater is oxidized with ozone. Then, the odor component and the pollutant component extracted into the water are oxidized.
【0007】以上述べてきた通り、厨芥を粉砕して配管
移送し、その後体積減容化を図る厨芥処理方法は、厨芥
をその発生源で直接廃棄できることから、台所などの作
業場所の衛生性の向上が図れ、かつ、後処理による体積
減容で、最終的に廃棄される物量を削減して環境負荷を
軽減することができるため、環境調和型の厨芥処理方法
となり得る。As described above, the garbage disposal method for crushing garbage and transferring it to a pipe, and then reducing the volume of the garbage can be directly disposed of at the source thereof, so that the sanitary condition of a work place such as a kitchen can be reduced. Since the volume can be improved and the volume is reduced by the post-treatment, the amount of material finally discarded can be reduced and the environmental load can be reduced.
【0008】[0008]
【発明が解決しようとする課題】しかしながら、厨芥は
粉砕すると、厨芥中の有機性成分が溶けだし、水質の汚
濁の指標であるBOD(生物化学的酸素要求量)値が上
昇する。特開平03ー89954号、特開平04ー30
5284号や特開平06ー55158号広報に開示され
る処理装置では、粉砕厨芥を回収して厨芥固形物の処理
だけがなされ、排水中に溶けだした汚濁成分は未処理で
放流されるため、環境への負荷を増大させるという問題
があった。However, when garbage is crushed, organic components in the garbage are dissolved, and the BOD (biochemical oxygen demand), which is an index of water pollution, rises. JP-A-03-89954, JP-A-04-30
In the processing apparatus disclosed in Japanese Patent No. 5284 and JP-A-06-55158, only the refuse is collected and garbage solids are processed, and the polluted components dissolved in the wastewater are discharged without treatment. There is a problem of increasing the load on the device.
【0009】また、厨芥の処理では厨芥中有機物の分解
による臭気物質が発生し、環境汚染を引き起こし易いと
いった問題点を抱えている。臭気物資として酪酸、プロ
ピオン酸などの有機酸、ホルムアルデヒド、メチルアル
デヒド、エチルアルデヒドなどのアルデヒド類、アンモ
ニア、トリメチルアミンといったアミン類、硫化水素な
どが発生する。Further, in the treatment of kitchen garbage, there is a problem that odorous substances are generated due to decomposition of organic matter in the kitchen garbage, which easily causes environmental pollution. As odorous substances, organic acids such as butyric acid and propionic acid, aldehydes such as formaldehyde, methyl aldehyde and ethyl aldehyde, amines such as ammonia and trimethylamine, and hydrogen sulfide are generated.
【0010】さらに、厨芥処理に微生物処理を導入した
場合、厨芥が汚泥に変換され、大量の汚泥が発生してし
まうといった問題点を抱えている。大量の汚泥は、バキ
ュ−ムカ−等で車両搬送の後、メタン発酵、脱水、焼却
などの工程を経て埋め立て処分となるため、汚泥量が多
ければ多いほど、多くの後処理エネルギ−を要すことに
なる。[0010] Furthermore, when microbial treatment is introduced into the processing of kitchen waste, there is a problem that kitchen waste is converted into sludge and a large amount of sludge is generated. A large amount of sludge is transported to a vehicle by vaccum, etc., and then landfilled through processes such as methane fermentation, dehydration, and incineration. Therefore, the larger the amount of sludge, the more post-treatment energy is required. Will be.
【0011】本発明は、臭気による環境汚染を回避しつ
つ、環境負荷の増大を招くこともない、環境共生型の厨
芥処理装置を提供することを目的とする。SUMMARY OF THE INVENTION It is an object of the present invention to provide an environmentally friendly kitchen waste disposal apparatus which avoids environmental pollution due to odor and does not increase the environmental load.
【0012】[0012]
【課題を解決するための手段およびその作用・効果】上
記課題を解決すべく、本発明に係わる厨芥処理装置で
は、粉砕機にて粉砕した厨芥は、水とともに配管移送し
た後、厨芥処理部で厨芥固形物を分解後、好気性微生物
で排水処理することで、効率的に排水中に溶出した厨芥
の汚濁成分を除去でき、かつ、厨芥処理、排水処理部で
発生する臭気は活性炭吸着、オゾン酸化、光触媒酸化、
酸化触媒処理、熱分解、プラズマ分解といった物理処
理、微生物を利用した微生物脱臭、マスキング処理を行
うことで、臭気による環境汚染を回避できるようにし
た。Means for Solving the Problems and Their Functions and Effects In order to solve the above problems, in the garbage disposal apparatus according to the present invention, after the garbage crushed by the crusher is transferred to the piping together with the water, the garbage is processed by the garbage processing section. After decomposing kitchen solids, wastewater treatment with aerobic microorganisms can efficiently remove the contaminant components of kitchen waste eluted in the wastewater, and the odor generated in the kitchen waste treatment and wastewater treatment section is activated carbon adsorption, ozone Oxidation, photocatalytic oxidation,
By carrying out physical treatments such as oxidation catalyst treatment, thermal decomposition, and plasma decomposition, and microbial deodorization and masking treatment using microorganisms, environmental pollution due to odors can be avoided.
【0013】さらに、厨芥を微生物により分解処理する
場合に発生する処理残滓、汚泥は、処理に関わる生物相
を微生物だけでなく、Vorticella,Carc
hesium,Epistytis,Oxytrich
aなどの原生動物、Philodina,Aeroso
ma,Dero,Macrobiotusなどの後生動
物を含む相とすることで、原生動物、後生動物に汚泥を
捕食せしめ、余剰汚泥発生量を削減して、維持管理が容
易で、処理残滓、汚泥の再処分に要するエネルギ−負
荷、環境負荷を軽減する環境調和型の厨芥処理装置を提
供する。本願の第6から第8発明である。[0013] Furthermore, the processing residue and sludge generated when the kitchen waste is decomposed by microorganisms are used to remove not only the microorganisms but also the microorganisms of Vorticella, Carc.
hesium, Epistytis, Oxytrich
Protozoa such as a, Philodina, Aeroso
Ma, Dero, Macrobiotus, and other phases that contain metazoans, allow the protozoa and metazoans to prey on sludge, reduce the amount of excess sludge generated, and are easy to maintain and re-dispose of processing residues and sludge. The present invention provides an environmentally friendly kitchen waste treatment apparatus that reduces the energy load and environmental load required for garbage disposal. This is the sixth to eighth inventions of the present application.
【0014】厨芥は沈殿分離、遠心分離、膜、スクリ−
ン、ストレ−ナによる濾過等の固液分離で、濃縮回収
し、熱、送風、微生物処理等による乾燥法により軽量
化、減容化して容易に再処分できる形態とすることでも
後処理が容易で、再処分に要するエネルギ−負荷、環境
負荷を軽減する環境調和型の厨芥処理装置を提供する。
本願の第4発明である。Garbage can be separated by sedimentation, centrifugation, membrane, screen
Concentration and recovery by solid-liquid separation such as filtration by means of a filter or a strainer, and post-treatment is also easy by reducing the weight and volume by a drying method using heat, air blowing, microbial treatment, etc., and reducing the volume. The present invention provides an environmentally friendly kitchen waste disposal apparatus that reduces the energy load and environmental load required for re-disposal.
This is the fourth invention of the present application.
【0015】厨芥などの有機性廃棄物が発生する住宅、
食堂、食品工場などにおいて、その発生場所近傍(台
所、調理場、食材、有機物処理ライン等)に設置された
厨芥の粉砕機にて厨芥を粉砕し、水で配管移送すること
で、厨芥の住宅、食品工場内への滞留を防止でき、厨芥
の腐敗に伴う、住環境、作業環境の悪化を防止できる。A house where organic waste such as kitchen waste is generated,
In a cafeteria, food factory, etc., the garbage is crushed by a garbage crusher installed near the place where the garbage is generated (kitchen, kitchen, foodstuff, organic material processing line, etc.), and the garbage house is transferred by piping with water. In addition, it is possible to prevent stagnation in food factories and prevent deterioration of the living environment and working environment due to the spoilage of kitchen garbage.
【0016】また、湿潤した廃棄物である厨芥と他の乾
燥した廃棄物が混合することなく、厨芥の発生場所で効
率的に分別できることから、他の廃棄物への厨芥付着に
よる取り扱い性の劣化、それに伴う分別再資源化効率の
低下を未然に防ぐことができ、これからのリサイクル社
会に貢献できる。In addition, since kitchen waste that is wet waste and other dry waste can be efficiently separated at the place where the kitchen waste is generated without mixing, the deterioration of handleability due to the adhesion of kitchen waste to other waste can be achieved. Thus, it is possible to prevent a decrease in the efficiency of sorting and recycling associated with it, and to contribute to a recycling society in the future.
【0017】また、本願発明の装置では、厨芥だけが選
択的に回収できることから、厨芥中の有用成分のリサイ
クルを図ることも可能となる。なお、粉砕機には、厨芥
だけでなく、その発生場所で合わせて生じる排水(台所
排水、調理排水、食材、有機物処理ライン排水等)を併
せて流すことで、これらの高汚濁成分を含む排水も本願
発明の厨芥処理装置で処理することも有効である。Further, in the apparatus according to the present invention, since only kitchen waste can be selectively recovered, it is possible to recycle useful components in the kitchen waste. In addition, not only kitchen waste but also wastewater (kitchen wastewater, cooking wastewater, foodstuffs, organic wastewater treatment line wastewater, etc.) generated at the place where the waste is generated flows into the crusher together with the wastewater containing these highly polluting components. It is also effective to treat the garbage with the garbage disposal apparatus of the present invention.
【0018】後処理工程に送られた厨芥も腐敗によっ
て、あるいは、生物分解、乾燥工程等で臭気を発生さ
せ、環境汚染を起こし易い。そこで、後処理工程には脱
臭のためのガス処理部を併設して環境への影響を起こさ
ない、環境調和型の厨芥処理装置を提供する。脱臭に
は、活性炭吸着、オゾン酸化、光触媒酸化、酸化触媒処
理、熱分解、プラズマ分解といった物理処理、微生物を
利用した微生物脱臭、マスキング処理を利用する。The garbage sent to the post-treatment process also generates odors due to putrefaction or biodegradation, drying processes, etc., and is liable to cause environmental pollution. In view of the above, an environmentally friendly kitchen waste treatment apparatus which does not affect the environment by providing a gas treatment section for deodorization in the post-treatment step is provided. For deodorization, physical treatments such as activated carbon adsorption, ozone oxidation, photocatalytic oxidation, oxidation catalyst treatment, thermal decomposition and plasma decomposition, microbial deodorization using microorganisms, and masking treatment are used.
【0019】また、厨芥処理部に原生動物、後生動物の
担体となる多孔質樹脂片、高分子ゲルビ−ズなどの流動
担体、接触濾材等を付加し、原生動物、後生動物の生育
環境を整えることにより、あるいは、厨芥処理部からの
処理水出口部に精密濾過膜、限外濾過膜、濾布、微細目
スクリ−ンを設置して、原生動物、後生動物を処理部内
に封じ込めることにより、原生動物、後生動物を含む生
物相を厨芥処理部内に形成し、厨芥を微生物により分解
処理する場合に発生する処理残滓、余剰汚泥量を原生動
物、後生動物に捕食せしめ、余剰汚泥発生量を削減し
て、維持管理が容易で、処理残滓、汚泥の再処分に要す
るエネルギ−負荷、環境負荷を軽減する環境調和型の厨
芥処理装置とする。排水は好気性の生物処理で水中の汚
濁成分の除去を行なって、下水道、浄化槽、環境中へ処
理水を放流しても放流先の環境負荷を上昇させないよう
にする。[0019] In addition, a porous resin piece serving as a carrier for protozoa and metazoan animals, a fluid carrier such as polymer gel beads, a contact filter medium, and the like are added to the garbage processing section to prepare a growth environment for protozoa and metazoans. By installing a microfiltration membrane, an ultrafiltration membrane, a filter cloth, and a fine mesh screen at the outlet of the treated water from the garbage processing section, and sealing the protozoa and metazoans in the processing section, A biota including protozoa and metazoans is formed in the garbage processing section, and the processing residues and excess sludge generated when the garbage is decomposed by microorganisms are eaten by the protozoa and metazoans to reduce the amount of excess sludge generated. In addition, an environmentally friendly kitchen waste disposal apparatus which is easy to maintain and reduces the energy load and the environmental load required for the disposal of processing residues and sludge is reduced. Wastewater is subjected to aerobic biological treatment to remove pollutants in the water, so that even if treated water is discharged into sewers, septic tanks, or the environment, the environmental load at the discharge destination is not increased.
【0020】[0020]
【発明の実施の形態】本発明の内容をより理解しやすく
する為、以下に図表を用いて詳説する。DESCRIPTION OF THE PREFERRED EMBODIMENTS In order to make the contents of the present invention easier to understand, a detailed description will be given below with reference to the drawings.
【0021】[0021]
【実施例】表1に粉砕厨芥排水のBOD,SS濃度(固
形物濃度)を示す。厨芥を粉砕して下水道などに流す
と、排水の負荷が極めて大きくなることが、台所排水と
比較しても明らかである。EXAMPLES Table 1 shows the BOD and SS concentrations (solid matter concentrations) of the crushed kitchen wastewater. It is clear from the comparison with kitchen wastewater that when kitchen waste is crushed and drained into sewers or the like, the drainage load becomes extremely large.
【0022】[0022]
【表1】 [Table 1]
【0023】図1は、本願発明に係わる厨芥処理装置図
である。粉砕機1には移送水を供給できる移送水供給口
を有し、台所調理厨芥を粉砕して水を用いて通常の自然
流下配管2で後処理部まで流す。粉砕厨芥は、圧送ポン
プを介して圧送配管で移送してもよい。移送水供給は、
移送部である配管に定期的に行い、配管洗浄することも
有効である。その場合は、水道水、井戸水などの上水だ
けでなく、中水、排水処理水なども利用可能である。移
送された厨芥排水は、厨芥分解槽4で微生物により可溶
化分解を行う。その後排水処理槽粉砕厨芥と排水に分離
され、排水は接触ばっ気槽5,沈殿分離槽6を経て放流
される。沈殿分離槽5にて排水中の汚濁成分を浄化の
後、沈殿分離槽6を経て放流される。各槽の排気、発生
ガスはまとめて脱臭装置7を介して系外に排出される。FIG. 1 is a diagram of a kitchen waste treatment apparatus according to the present invention. The crusher 1 has a transfer water supply port capable of supplying transfer water, crushes kitchen cooking garbage, and uses water to flow to the post-processing section through a normal natural flow pipe 2. The crushed garbage may be transferred by a pressure feed pipe via a pressure feed pump. Transfer water supply
It is also effective to periodically clean the piping, which is the transfer unit, to clean the piping. In this case, not only tap water and well water but also middle water and wastewater can be used. The transferred kitchen wastewater is solubilized and decomposed by microorganisms in the kitchen decomposition tank 4. Thereafter, the waste water is separated into crushed waste and wastewater, and the wastewater is discharged through the contact aeration tank 5 and the sedimentation separation tank 6. After the polluted components in the wastewater are purified in the sedimentation separation tank 5, they are discharged through the sedimentation separation tank 6. The exhaust gas and generated gas from each tank are collectively discharged out of the system via the deodorizing device 7.
【0024】排水処理部とHRTと処理水質との関係を
表2に示す。表中に組成を示す標準厨芥を微生物により
HRT2日で可溶化の後、上澄みを種々のHRTの担体
流動床で浄化処理した。処理性能はBODを指標として
評価し、HRT24時間以上で、目標性能が得られるこ
とを見いだした。Table 2 shows the relationship between the wastewater treatment section, the HRT, and the quality of the treated water. After the standard garbage having the composition shown in the table was solubilized by microorganisms for 2 days of HRT, the supernatant was purified by a fluidized bed of various HRT carriers. The processing performance was evaluated using BOD as an index, and it was found that the target performance was obtained when the HRT was 24 hours or more.
【0025】[0025]
【表2】 [Table 2]
【0026】図2には、本願第4発明に係わる厨芥処理
装置図である。粉砕機1には移送水を供給できる移送水
供給口を有し、台所調理厨芥を粉砕して水を用いて通常
の自然流下配管2で後処理部まで流す。移送された厨芥
排水は、一旦調整槽8に貯留の後、固液分離・厨芥乾燥
機9に送り厨芥を乾燥して厨芥乾燥貯留部10に貯留す
る。貯留部では、袋詰めすることも有効である。その場
合厨芥の水分率を10%以下とすることで、貯留時の腐
敗を防げる。排水接触ばっ気槽5,沈殿分離槽6を経て
放流される。沈殿分離槽5にて排水中の汚濁成分を浄化
の後、沈殿分離槽6を経て放流される。各槽の排気、発
生ガスはまとめて脱臭装置7を介して系外に排出され
る。FIG. 2 is a view of a kitchen waste disposal apparatus according to the fourth invention of the present application. The crusher 1 has a transfer water supply port capable of supplying transfer water, crushes kitchen cooking garbage, and uses water to flow to the post-processing section through a normal natural flow pipe 2. The transferred garbage wastewater is once stored in the adjustment tank 8 and then sent to a solid-liquid separation / garbage dryer 9 to dry the garbage and stored in the garbage drying and storage unit 10. In the storage unit, bagging is also effective. In this case, the water content of the kitchen garbage can be reduced to 10% or less to prevent rot during storage. The wastewater is discharged through the drainage contact aeration tank 5 and the sedimentation separation tank 6. After the polluted components in the wastewater are purified in the sedimentation separation tank 5, they are discharged through the sedimentation separation tank 6. The exhaust gas and generated gas from each tank are collectively discharged out of the system via the deodorizing device 7.
【0027】以上に説明したごとく、本願発明に係わる
厨芥処理装置では、厨芥発生場所から厨芥を選択的、衛
生的に除去し、後処理部で減容化して貯留することで、
半年から1年に1回の汚泥処分で厨芥処理ができる装置
を提供するものである。また、本願発明の装置は、放流
水も浄化して放流することから、環境負荷の増大を招く
こともない、環境共生型の装置である。As described above, in the garbage disposal apparatus according to the present invention, the garbage is selectively and sanitarily removed from the garbage generating location, and the volume is stored and reduced in the post-processing section.
An object of the present invention is to provide an apparatus capable of processing garbage by sludge disposal once every six months to one year. Further, the device of the present invention is an environment-symbiotic device that does not cause an increase in environmental load because the discharged water is purified and discharged.
【図1】厨芥排水処理装置図(厨芥生物処理)Fig. 1 Kitchen wastewater treatment equipment diagram (garbage biological treatment)
【図2】厨芥排水処理装置図(厨芥固液分離、乾燥処
理)Fig. 2 Garbage wastewater treatment equipment diagram (garbage solid-liquid separation, drying treatment)
1…粉砕機、2…移送部、3…後処理部、4…厨芥処理
部、5…排水処理部、6…排水沈殿分離部、7…ガス処
理部、8…調整槽、9…固液分離・厨芥乾燥機、10…
厨芥乾燥貯留部DESCRIPTION OF SYMBOLS 1 ... Crusher, 2 ... Transfer part, 3 ... Post-processing part, 4 ... Garbage processing part, 5 ... Wastewater treatment part, 6 ... Wastewater sedimentation separation part, 7 ... Gas treatment part, 8 ... Adjustment tank, 9 ... Solid liquid Separation / garbage dryer, 10 ...
Kitchen waste storage
Claims (8)
水供給部と、粉砕厨芥、水よりなる厨芥排水を移送する
移送部と、移送された厨芥排水中の厨芥を処理する厨芥
処理部と、排水を浄化処理する排水処理部とを有する厨
芥処理装置において、発生する臭気ガスを脱臭処理する
ためのガス処理部を有することを特徴とする厨芥処理装
置。1. A crushing unit for crushing garbage, a water supply unit for supplying water, a transfer unit for transferring garbage wastewater composed of crushed garbage and water, and a garbage processing unit for processing garbage in the transferred garbage wastewater. A garbage processing apparatus comprising: a wastewater treatment section for purifying wastewater; and a gas treatment section for deodorizing generated odor gas.
水力学的滞留時間(HRT)を24時間以上とすること
を特徴とする請求項1に記載の厨芥処理装置の運転方
法。2. The wastewater treatment section is an aerobic biological treatment,
The method according to claim 1, wherein the hydraulic residence time (HRT) is 24 hours or more.
あるいは、好気性と嫌気性を組み合わせた微生物処理と
することを特徴とする請求項1および2に記載の厨芥処
理装置の運転方法。3. The method for operating a garbage disposal apparatus according to claim 1, wherein the garbage disposal section is aerobic or anaerobic or a combination of aerobic and anaerobic microorganism treatment.
処理部とから成ることを特徴とする請求項1から3に記
載の厨芥処理装置。4. The garbage processing apparatus according to claim 1, wherein the garbage processing section includes a solid-liquid separation section and a garbage drying processing section.
いった物理処理、微生物脱臭、土壌脱臭、マスキングを
単独で、または組み合わせて利用することを特徴とする
請求項1から4に記載の厨芥処理装置の運転方法。5. The kitchen garbage according to claim 1, wherein the gas processing unit uses physical treatments such as adsorption, oxidation, and decomposition, microbial deodorization, soil deodorization, and masking alone or in combination. The operation method of the processing device.
るいは両方に原生動物、後生動物を含む生物相を形成せ
しめることを特徴とする請求項1から5に記載の厨芥処
理装置の運転方法。6. The method according to claim 1, wherein a biota including a protozoan and a metazoan is formed in the garbage disposal unit and / or the wastewater treatment unit.
部あるいは両方に原生動物、後生動物の固定化担体を付
加することにより原生動物、後生動物を含む生物相を形
成せしめることを特徴とする請求項6に記載の厨芥処理
装置の運転方法。7. A biota including protozoa and metazoa is formed by adding an immobilized carrier for protozoa and metazoa to the garbage processing unit and / or the wastewater treatment unit. Item 7. An operation method of the garbage disposal device according to Item 6.
部、あるいは両方に濾過膜、スクリ−ン等の原生動物、
後生動物の封じ込め機能部を付加せしめることにより原
生動物、後生動物を含む生物相を形成せしめることを特
徴とする請求項6に記載の厨芥処理装置の運転方法。8. A protozoan such as a filtration membrane or a screen in the kitchen waste treatment section, the wastewater treatment section, or both.
The method according to claim 6, wherein a biota including protozoa and metazoa is formed by adding a metazoa containment function unit.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP20115098A JP2000015233A (en) | 1998-06-30 | 1998-06-30 | Apparatus for treating kitchen refuse and method for operating the apparatus |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP20115098A JP2000015233A (en) | 1998-06-30 | 1998-06-30 | Apparatus for treating kitchen refuse and method for operating the apparatus |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2000015233A true JP2000015233A (en) | 2000-01-18 |
Family
ID=16436225
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP20115098A Pending JP2000015233A (en) | 1998-06-30 | 1998-06-30 | Apparatus for treating kitchen refuse and method for operating the apparatus |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP2000015233A (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20030001987A (en) * | 2001-06-28 | 2003-01-08 | (주) 티엔케이텍 | Analysis Device For Treating The Food Wastes |
KR100444528B1 (en) * | 2001-06-28 | 2004-08-21 | 주식회사 월드코아 | Device For Removing The Smell The Food Wastes Treatment Machine |
WO2005044741A1 (en) * | 2003-11-11 | 2005-05-19 | Ebara Corporation | Water treatment method and apparatus using fish |
JP2009226353A (en) * | 2008-03-25 | 2009-10-08 | Clean Tec Kk | Dry garbage treatment apparatus |
WO2014079167A1 (en) * | 2012-11-23 | 2014-05-30 | 华南再生资源(中山)有限公司 | Apparatus for food waste oxygenation, deodorization, inactivation, salt-reduction by rinsing |
CN105502806A (en) * | 2015-12-03 | 2016-04-20 | 合肥工业大学 | Efficient pesticide removing system and method based on plasma and multi-group SBR (sequencing batch reactor) reaction tanks |
WO2019010722A1 (en) * | 2017-07-13 | 2019-01-17 | 广州弗特瑞环保科技有限公司 | Kitchen waste disposing machine and kitchen waste disposing method therefor |
-
1998
- 1998-06-30 JP JP20115098A patent/JP2000015233A/en active Pending
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20030001987A (en) * | 2001-06-28 | 2003-01-08 | (주) 티엔케이텍 | Analysis Device For Treating The Food Wastes |
KR100444528B1 (en) * | 2001-06-28 | 2004-08-21 | 주식회사 월드코아 | Device For Removing The Smell The Food Wastes Treatment Machine |
WO2005044741A1 (en) * | 2003-11-11 | 2005-05-19 | Ebara Corporation | Water treatment method and apparatus using fish |
JP2009226353A (en) * | 2008-03-25 | 2009-10-08 | Clean Tec Kk | Dry garbage treatment apparatus |
WO2014079167A1 (en) * | 2012-11-23 | 2014-05-30 | 华南再生资源(中山)有限公司 | Apparatus for food waste oxygenation, deodorization, inactivation, salt-reduction by rinsing |
CN105502806A (en) * | 2015-12-03 | 2016-04-20 | 合肥工业大学 | Efficient pesticide removing system and method based on plasma and multi-group SBR (sequencing batch reactor) reaction tanks |
WO2019010722A1 (en) * | 2017-07-13 | 2019-01-17 | 广州弗特瑞环保科技有限公司 | Kitchen waste disposing machine and kitchen waste disposing method therefor |
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