KR20020071283A - a food-rest treatment apparatus - Google Patents
a food-rest treatment apparatus Download PDFInfo
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- KR20020071283A KR20020071283A KR1020010011342A KR20010011342A KR20020071283A KR 20020071283 A KR20020071283 A KR 20020071283A KR 1020010011342 A KR1020010011342 A KR 1020010011342A KR 20010011342 A KR20010011342 A KR 20010011342A KR 20020071283 A KR20020071283 A KR 20020071283A
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- Prior art keywords
- food waste
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- odor
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- 230000008033 biological extinction Effects 0.000 claims abstract description 82
- 239000010794 food waste Substances 0.000 claims abstract description 64
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 33
- 239000005909 Kieselgur Substances 0.000 claims abstract description 29
- 244000005700 microbiome Species 0.000 claims abstract description 26
- 238000012545 processing Methods 0.000 claims abstract description 17
- 239000012190 activator Substances 0.000 claims abstract description 16
- 230000000813 microbial effect Effects 0.000 claims abstract description 15
- 239000007788 liquid Substances 0.000 claims abstract description 6
- 239000007921 spray Substances 0.000 claims abstract description 3
- 239000010805 inorganic waste Substances 0.000 claims 1
- 238000010791 quenching Methods 0.000 abstract description 14
- 230000000171 quenching effect Effects 0.000 abstract description 5
- 238000000034 method Methods 0.000 abstract description 3
- 230000007613 environmental effect Effects 0.000 abstract description 2
- 238000011049 filling Methods 0.000 abstract description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 abstract description 2
- 239000011707 mineral Substances 0.000 abstract description 2
- 239000011368 organic material Substances 0.000 abstract description 2
- 150000003839 salts Chemical class 0.000 abstract description 2
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 abstract 1
- 229910052802 copper Inorganic materials 0.000 abstract 1
- 239000010949 copper Substances 0.000 abstract 1
- 230000000052 comparative effect Effects 0.000 description 47
- 239000000919 ceramic Substances 0.000 description 24
- 239000002023 wood Substances 0.000 description 24
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 14
- 238000003756 stirring Methods 0.000 description 13
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- 230000008034 disappearance Effects 0.000 description 11
- 238000002474 experimental method Methods 0.000 description 5
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- 239000007924 injection Substances 0.000 description 5
- KZEVSDGEBAJOTK-UHFFFAOYSA-N 1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)-2-[5-[2-[[3-(trifluoromethoxy)phenyl]methylamino]pyrimidin-5-yl]-1,3,4-oxadiazol-2-yl]ethanone Chemical compound N1N=NC=2CN(CCC=21)C(CC=1OC(=NN=1)C=1C=NC(=NC=1)NCC1=CC(=CC=C1)OC(F)(F)F)=O KZEVSDGEBAJOTK-UHFFFAOYSA-N 0.000 description 3
- VZSRBBMJRBPUNF-UHFFFAOYSA-N 2-(2,3-dihydro-1H-inden-2-ylamino)-N-[3-oxo-3-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)propyl]pyrimidine-5-carboxamide Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C(=O)NCCC(N1CC2=C(CC1)NN=N2)=O VZSRBBMJRBPUNF-UHFFFAOYSA-N 0.000 description 3
- YJLUBHOZZTYQIP-UHFFFAOYSA-N 2-[5-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]-1,3,4-oxadiazol-2-yl]-1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C1=NN=C(O1)CC(=O)N1CC2=C(CC1)NN=N2 YJLUBHOZZTYQIP-UHFFFAOYSA-N 0.000 description 3
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- OHVLMTFVQDZYHP-UHFFFAOYSA-N 1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)-2-[4-[2-[[3-(trifluoromethoxy)phenyl]methylamino]pyrimidin-5-yl]piperazin-1-yl]ethanone Chemical compound N1N=NC=2CN(CCC=21)C(CN1CCN(CC1)C=1C=NC(=NC=1)NCC1=CC(=CC=C1)OC(F)(F)F)=O OHVLMTFVQDZYHP-UHFFFAOYSA-N 0.000 description 2
- HMUNWXXNJPVALC-UHFFFAOYSA-N 1-[4-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]piperazin-1-yl]-2-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)N1CCN(CC1)C(CN1CC2=C(CC1)NN=N2)=O HMUNWXXNJPVALC-UHFFFAOYSA-N 0.000 description 2
- LDXJRKWFNNFDSA-UHFFFAOYSA-N 2-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)-1-[4-[2-[[3-(trifluoromethoxy)phenyl]methylamino]pyrimidin-5-yl]piperazin-1-yl]ethanone Chemical compound C1CN(CC2=NNN=C21)CC(=O)N3CCN(CC3)C4=CN=C(N=C4)NCC5=CC(=CC=C5)OC(F)(F)F LDXJRKWFNNFDSA-UHFFFAOYSA-N 0.000 description 2
- VWVRASTUFJRTHW-UHFFFAOYSA-N 2-[3-(azetidin-3-yloxy)-4-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]pyrazol-1-yl]-1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound O=C(CN1C=C(C(OC2CNC2)=N1)C1=CN=C(NC2CC3=C(C2)C=CC=C3)N=C1)N1CCC2=C(C1)N=NN2 VWVRASTUFJRTHW-UHFFFAOYSA-N 0.000 description 2
- SXAMGRAIZSSWIH-UHFFFAOYSA-N 2-[3-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]-1,2,4-oxadiazol-5-yl]-1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C1=NOC(=N1)CC(=O)N1CC2=C(CC1)NN=N2 SXAMGRAIZSSWIH-UHFFFAOYSA-N 0.000 description 2
- WWSJZGAPAVMETJ-UHFFFAOYSA-N 2-[4-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]-3-ethoxypyrazol-1-yl]-1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C=1C(=NN(C=1)CC(=O)N1CC2=C(CC1)NN=N2)OCC WWSJZGAPAVMETJ-UHFFFAOYSA-N 0.000 description 2
- WZFUQSJFWNHZHM-UHFFFAOYSA-N 2-[4-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]piperazin-1-yl]-1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)N1CCN(CC1)CC(=O)N1CC2=C(CC1)NN=N2 WZFUQSJFWNHZHM-UHFFFAOYSA-N 0.000 description 2
- JQMFQLVAJGZSQS-UHFFFAOYSA-N 2-[4-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]piperazin-1-yl]-N-(2-oxo-3H-1,3-benzoxazol-6-yl)acetamide Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)N1CCN(CC1)CC(=O)NC1=CC2=C(NC(O2)=O)C=C1 JQMFQLVAJGZSQS-UHFFFAOYSA-N 0.000 description 2
- ZRPAUEVGEGEPFQ-UHFFFAOYSA-N 2-[4-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]pyrazol-1-yl]-1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C=1C=NN(C=1)CC(=O)N1CC2=C(CC1)NN=N2 ZRPAUEVGEGEPFQ-UHFFFAOYSA-N 0.000 description 2
- JVKRKMWZYMKVTQ-UHFFFAOYSA-N 2-[4-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]pyrazol-1-yl]-N-(2-oxo-3H-1,3-benzoxazol-6-yl)acetamide Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C=1C=NN(C=1)CC(=O)NC1=CC2=C(NC(O2)=O)C=C1 JVKRKMWZYMKVTQ-UHFFFAOYSA-N 0.000 description 2
- YLZOPXRUQYQQID-UHFFFAOYSA-N 3-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)-1-[4-[2-[[3-(trifluoromethoxy)phenyl]methylamino]pyrimidin-5-yl]piperazin-1-yl]propan-1-one Chemical compound N1N=NC=2CN(CCC=21)CCC(=O)N1CCN(CC1)C=1C=NC(=NC=1)NCC1=CC(=CC=C1)OC(F)(F)F YLZOPXRUQYQQID-UHFFFAOYSA-N 0.000 description 2
- CONKBQPVFMXDOV-QHCPKHFHSA-N 6-[(5S)-5-[[4-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]piperazin-1-yl]methyl]-2-oxo-1,3-oxazolidin-3-yl]-3H-1,3-benzoxazol-2-one Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)N1CCN(CC1)C[C@H]1CN(C(O1)=O)C1=CC2=C(NC(O2)=O)C=C1 CONKBQPVFMXDOV-QHCPKHFHSA-N 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- AFCARXCZXQIEQB-UHFFFAOYSA-N N-[3-oxo-3-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)propyl]-2-[[3-(trifluoromethoxy)phenyl]methylamino]pyrimidine-5-carboxamide Chemical compound O=C(CCNC(=O)C=1C=NC(=NC=1)NCC1=CC(=CC=C1)OC(F)(F)F)N1CC2=C(CC1)NN=N2 AFCARXCZXQIEQB-UHFFFAOYSA-N 0.000 description 2
- 239000000969 carrier Substances 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 235000013305 food Nutrition 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 241000206761 Bacillariophyta Species 0.000 description 1
- 240000007124 Brassica oleracea Species 0.000 description 1
- 235000003899 Brassica oleracea var acephala Nutrition 0.000 description 1
- 235000011301 Brassica oleracea var capitata Nutrition 0.000 description 1
- 235000001169 Brassica oleracea var oleracea Nutrition 0.000 description 1
- 244000067456 Chrysanthemum coronarium Species 0.000 description 1
- -1 Earth Chemical compound 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 102000004190 Enzymes Human genes 0.000 description 1
- 108090000790 Enzymes Proteins 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 229910004298 SiO 2 Inorganic materials 0.000 description 1
- 235000009337 Spinacia oleracea Nutrition 0.000 description 1
- 244000300264 Spinacia oleracea Species 0.000 description 1
- 239000003082 abrasive agent Substances 0.000 description 1
- 239000002250 absorbent Substances 0.000 description 1
- 230000002745 absorbent Effects 0.000 description 1
- 239000013543 active substance Substances 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
- 239000002361 compost Substances 0.000 description 1
- 230000006378 damage Effects 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000000855 fermentation Methods 0.000 description 1
- 230000004151 fermentation Effects 0.000 description 1
- 239000000945 filler Substances 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 235000015134 garland chrysanthemum Nutrition 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 229910010272 inorganic material Inorganic materials 0.000 description 1
- 239000011147 inorganic material Substances 0.000 description 1
- 238000009413 insulation Methods 0.000 description 1
- 235000021109 kimchi Nutrition 0.000 description 1
- 235000021190 leftovers Nutrition 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
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Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
본 발명은 미생물을 통해 생물화학적으로 음식물 쓰레기를 분해하여 소멸시킬 수 있도록 하는 음식물 쓰레기 소멸장치에 관한 것으로, 종래의 음식물 쓰레기 소멸장치는 처리용 베이스로 대부분 유기물질을 사용하기 때문에 일정기간 사용하면 공극이 파괴되어 처리용 베이스의 수명이 짧게 되므로 수시로 처리용 베이스를 교환해주어야 할 뿐 아니라 처리용 베이스를 재활용할 수 없게 되는 문제가 있었고, 처리용 베이스가 음식물 쓰레기와 함께 부패하게 되므로 악취가 심하게 되어 냄새의 처리가 번거롭게 됨은 물론 처리용 베이스의 부피가 크기 때문에 소멸실의 용적이 증대되어 소멸장치의 전체 부피가 커지게 되는 문제가 있었던 바, 소멸실(12)에 음식물 쓰레기 처리용 베이스(21)로 함수능력이 탁월하고 경량의 무기물인 규조토를 충전하는 동시에 소멸실(21)의 상부 일측에 미생물 투입구(12a)를 마련하고, 투입구(12a)에 분사노즐(22) 및 미생물 공급펌프(24)를 설치하여 액상의 미생물 및 활성제, 악취제거제 등을 자동으로 투입할 수 있도록 한 것을 특징으로 하는 본 발명에 의하면 처리용 베이스(21)로 부피가 작고 잘 썩지 않는 무기질의 규조토를 사용함으로써 악취발생을 억제할 수 있게 되어 악취제거구조를 간편하게 구성할 수 있게 될 뿐 아니라 소멸실(12)의 부피 및 장치 전체 부피를 감소시켜 소형화 및 경량화를 도모할 수 있게 되고, 처리용 베이스(21)의 수명을 크게 연장할 수 있게 됨은 물론 처리용 베이스(21)에서 염분만을 제거한 후 재활용할 수 있게 되므로 환경보호에도 크게 이바지할 수 있게 하는 등의 효과를 얻을 수 있게 된다.The present invention relates to a food waste dissipation device that can disintegrate and extinguish food waste biochemically through microorganisms, and conventional food waste dissipation devices are voids when used for a certain period of time because most organic materials are used as a treatment base. As the base of the treatment base is destroyed and the life of the treatment base is shortened, there is a problem that the treatment base must be replaced at any time, and the treatment base cannot be recycled. Of course, there is a problem that the process of cumbersome treatment and the volume of the base for processing increases the volume of the quenching chamber, thereby increasing the total volume of the quenching apparatus. Copper filling diatomaceous earth, which is an excellent and lightweight mineral A microbial inlet 12a is provided at an upper side of the extinction chamber 21 and a spray nozzle 22 and a microbial supply pump 24 are installed at the inlet 12a to automatically supply liquid microorganisms, activators, and odor removers. According to the present invention, characterized in that it can be added to the treatment base 21 by using a small volume of inorganic diatomaceous earth that does not rot well, it is possible to suppress the occurrence of odor can be easily configured to remove the odor structure In addition to reducing the volume of the extinction chamber 12 and the total volume of the device can be reduced in size and weight, it is possible to greatly extend the life of the processing base 21 as well as in the processing base 21 Since only salt is removed and can be recycled, it is possible to contribute to environmental protection.
Description
본 발명은 미생물을 통해 생물화학적으로 음식물 쓰레기를 분해하여 소멸시킬 수 있도록 하는 음식물 쓰레기 소멸장치에 관한 것으로, 더 자세하게는 음식물의 쓰레기가 투입되는 소멸실에 미생물의 베이스로 규조토를 충전하는 한편 액상의 미생물, 활성제, 악취제거제 등을 소멸실에 자동으로 분사할 수 있도록 한 것에 관한 것이다.The present invention relates to a food waste dissipation device that can dissociate and destroy food wastes biochemically through microorganisms, and more particularly, to fill a diatomaceous earth with a base of microorganisms in a quench chamber into which food wastes are injected. The present invention relates to a method for automatically spraying microorganisms, activators, and malodor removing agents into an extinction chamber.
일반적으로 대부분이 유기물이 음식물 쓰레기는 그대로 매립 처리될 경우 매립장을 일종의 화학 반응장소로 만들게 되어 오염물질 농도가 높은 침출수를 배출시키게 될 뿐 아니라 악취와 유해물질로 오염된 매립지가스를 발생시키는 등 심각한 2차 오염문제를 야기하게 된다.In general, when most organic matter is disposed of in landfills, the landfill becomes a kind of chemical reaction site, which not only emits leachate with high pollutant concentration but also generates landfill gas contaminated with odor and harmful substances. It causes the problem of secondary pollution.
따라서 음식물 쓰레기는 감량 또는 재활용하는 것이 극히 바람직하게 되는 바, 음식물 쓰레기의 처리장치는 음식물 쓰레기를 잘게 부수고 물기를 제거하여 부피 및 무게를 줄일 수 있도록 하는 건조장치로부터 적당한 온도와 습도, 그리고 산소공급으로 음식물 쓰레기를 발효시켜 퇴비화를 도모하는 발효장치, 그리고 미생물로 음식물 쓰레기를 생물화학적으로 분해시켜 소멸시키는 소멸장치의 순서로 발전되고 있는 추세이다.Therefore, it is extremely desirable to reduce or recycle food waste. The food waste processing unit is supplied with a suitable temperature, humidity, and oxygen supply from a drying apparatus that can crush food waste, remove water, and reduce volume and weight. It is being developed in the order of the fermentation system for fermenting food waste to compost, and the extinction device for biochemical decomposition and extinction of food waste with microorganisms.
본 발명은 음식물 쓰레기 처리용 베이스가 충전된 소멸실에 미생물과 음식물 쓰레기를 투입하여 생물화학적으로 분해ㆍ소멸시킬 수 있도록 하는 음식물 쓰레기 소멸장치에 관계하는 것으로, 종래에 있어서 이와 같은 음식물 쓰레기 소멸장치는 적당한 온도와 습도가 유지되는 소멸실의 내부에 음식물 쓰레기 처리용 베이스로 톱밥이나 왕겨, 우드칩, 세라믹볼 등을 충전한 것이 주로 사용되었다.The present invention relates to a food waste extinguishing device which is capable of decomposing and extinguishing biochemically by injecting microorganisms and food waste into a quenching chamber filled with a food waste processing base. Filled with sawdust, rice hulls, wood chips, ceramic balls, etc., as a base for treating food waste inside the extinction chamber, where proper temperature and humidity are maintained.
그러나 상기 종래의 음식물 쓰레기 소멸장치는 처리용 베이스로 대부분 유기물질을 사용하기 때문에 일정기간 사용하면 공극이 파괴되어 처리용 베이스의 수명이 짧게 되므로 수시로 처리용 베이스를 교환해주어야 할 뿐 아니라 처리용 베이스를 재활용할 수 없게 되는 문제가 있었고, 처리용 베이스가 음식물 쓰레기와 함께부패하게 되므로 악취가 심하게 되어 냄새의 처리가 번거롭게 됨은 물론 처리용 베이스의 부피가 크기 때문에 소멸실의 용적이 증대되어 소멸장치의 전체 부피가 커지게 되는 문제가 있었다.However, since the conventional food waste extinguishing device uses most organic materials as a treatment base, if a certain period of use is used, the voids are destroyed and the life of the treatment base is shortened. Therefore, the treatment base must be replaced at any time. There was a problem that can not be recycled, because the processing base is decayed with food waste, the bad smell becomes severe, cumbersome processing of the smell, as well as the volume of the processing base increases the volume of the extinction chamber to increase the overall extinction device There was a problem of becoming bulky.
본 발명은 상기와 같은 종래의 음식물 쓰레기 소멸장치의 제결함을 감안하여 안출한 것이며, 그 목적이 처리용 베이스의 부피를 감소시키는 것에 의해 소멸실의 부피 및 소멸장치 전체 부피를 줄일 수 있도록 함은 물론 처리용 베이스를 재활용할 수 있도록 하고, 소멸실에 미생물 및 활성제, 악취제거제 등을 보다 용이하게 투입할 수 있도록 하는 음식물 쓰레기 소멸장치를 제공하는 데에 있는 것이다.The present invention has been made in view of the deficiency of the conventional food waste extinction device as described above, the object is to reduce the volume of the extinction chamber and the total volume of the extinction device by reducing the volume of the processing base is Of course, it is to provide a food waste extinction device that allows the treatment base to be recycled and to more easily add microorganisms and activators, odor removers, etc. to the extinction chamber.
도 1은 본 발명의 한 실시예의 정면도1 is a front view of one embodiment of the present invention
도 2는 동 실시예의 측면도2 is a side view of the embodiment
도 3은 동 실시예의 요부 구성도3 is a main configuration diagram of the embodiment
< 도면의 주요 부분에 대한 부호의 설명 ><Description of Symbols for Main Parts of Drawings>
10 : 음식물 쓰레기 처리장치11 : 본체10: food waste disposal apparatus 11: the main body
12 : 소멸실 12a : 미생물 투입구12: extinction chamber 12a: microorganism inlet
12b : 음식물 쓰레기 투입구21 : 처리용 베이스12b: food waste inlet 21: treatment base
22 : 분사노즐23 : 연결파이프22: injection nozzle 23: connection pipe
24 : 미생물 공급펌프24: microbial supply pump
본 발명은 상기의 목적을 달성하기 위하여 소멸실에 함수능력이 탁월하고 경량의 무기물인 규조토를 충전하는 동시에 소멸실의 일측에 미생물 투입구를 마련하여 액상의 미생물 및 활성제, 악취제거제 등을 자동으로 투입하는 것을 특징으로 하며, 이하 그 구체적인 기술내용을 첨부도면에 의거하여 더욱 자세히 설명하면 다음과 같다.The present invention is filled with a microorganism inlet on one side of the extinction chamber at the same time filling the diatomaceous earth with excellent water capacity and lightweight minerals in the extinction chamber in order to achieve the above object is automatically added to the liquid microorganism and activator, odor remover, etc. Characterized in detail, hereinafter, the specific technical details will be described in more detail based on the accompanying drawings.
즉, 도 1 및 도 2에는 본 발명의 한 실시예가 도시되어 있는 바, 본 발명은 본체(11)의 내부에 음식물 쓰레기 처리용 베이스(21)가 충전되는 소멸실(12)이 마련되는 음식물 쓰레기 처리장치(10)를 구성함에 있어서, 상기 소멸실(12)에 음식물 쓰레기 처리용 베이스(21)로 함수능력이 탁월하고 경량의 무기물인 규조토를 충전하는 동시에 소멸실(21)의 상부 일측에 미생물 투입구(12a)를 마련하고,투입구(12a)에 분사노즐(22) 및 미생물 공급펌프(24)를 설치하여 액상의 미생물 및 활성제, 악취제거제를 자동으로 투입할 수 있도록 하여서 되는 것이다.That is, one embodiment of the present invention is shown in Figures 1 and 2, the present invention is a food waste is provided with a extinction chamber 12 is filled with a base 21 for processing food waste in the body (11) In constructing the treatment apparatus 10, the decay chamber 12 is filled with the food waste processing base 21, and the diatomaceous earth, which is excellent in water capacity and lightweight, is filled with microorganisms at the upper side of the decay chamber 21. The inlet 12a is provided, and the injection nozzle 22 and the microorganism supply pump 24 are installed in the inlet 12a so as to automatically inject the liquid microorganism, the active agent, and the odor removing agent.
도시된 실시예는 미생물 투입구(12a)에 결합된 분사노즐(22)과 공급펌프(24)의 사이에 연결파이프(23)가 설치된 형태를 갖으며, 도면부호중 미설명부호 12b는 음식물 쓰레기 투입구, 13은 교반모터, 14는 교반체, 25는 미생물 저장용기이다.The illustrated embodiment has a form in which a connecting pipe 23 is installed between the injection nozzle 22 and the supply pump 24 coupled to the microbial inlet 12a, and reference numeral 12b in the drawing denotes a food waste inlet. , 13 is a stirring motor, 14 is a stirring body, 25 is a microorganism storage container.
상기와 같이 구성된 본 발명에 있어서는 음식물 쓰레기 처리용 베이스(21)로 일정량의 규조토가 충전된 소멸실(11)에 일정량의 음식물 쓰레기를 투입한 후 분사노즐(22)을 통해 액상의 미생물 및 활성제, 악취제거제 등을 투입하고, 소멸실(11)의 내부온도를 일정온도로 유지시키면서 일정한 시간간격으로 일정시간동안 처리용 베이스(21)와 음식물 쓰레기를 교반하여 주면 소멸실(11) 내부에서 생물화학적인 반응이 일어나게 되어 점차적으로 음식물 쓰레기가 소멸하게 되는 것인 바, 소멸실(11)에 처리용 베이스(21)로 충전된 규조토는 무기질이어서 썩지 않으므로 본 발명에 있어서는 음식물 쓰레기 소멸과정에서 악취의 발생이 적게 되고, 일정기간 경과 후 그에 포함된 염분만을 제거하면 재사용이 가능하게 된다.In the present invention configured as described above, after putting a certain amount of food waste into the extinction chamber 11 filled with a predetermined amount of diatomaceous earth as the food waste processing base 21, the liquid microorganisms and the activator through the injection nozzle 22, If the odor remover is added and the internal temperature of the extinction chamber 11 is maintained at a constant temperature, the processing base 21 and the food waste are stirred for a predetermined time at a predetermined time interval. Phosphorus reaction occurs and gradually the food waste disappears. Since the diatomaceous earth filled with the treatment base 21 in the extinction chamber 11 is inorganic and does not rot, in the present invention, odor is generated during the food waste extinction process. It becomes less, and after a certain period of time only by removing the salt contained therein becomes possible to reuse.
본 발명에서 사용되는 규조토(SiO2: Diatomite, Earth, Kieselguhr)는 규조라고 일컫는 단세포 수중식물의 유해가 호수나 바다에 가라앉아 형성된 회백색의 퇴적물로서, 규조화석의 연구에 따르면 규조류는 1억년전 공룡시대부터 존재하였으며, 서식조건에 따라 원반형, 타원형, 침상형, 원통형 등 여러 가지 형태와 10~15 미크론의 다양한 크기로 존재하고 있다.Diatomite (SiO 2 : Diatomite, Earth, Kieselguhr) used in the present invention is an off-white sediment formed by the destruction of single-celled aquatic plants called diatoms in a lake or the sea. It has existed since the times, and it has various forms such as disk, oval, needle, cylindrical, and various sizes of 10 ~ 15 microns.
이러한 규조토는 대부분 비정질의 실리카로 되어 있는 바, 물리화학적으로 안정한 무기물로 다공성이며, 가볍고, 흡수성과 단열성이 뛰어나기 때문에 여과조제, 충전제, 촉매제, 흡수제, 연마제, 담체 등 인류 생활에 다양하게 이용되는 우수한 재료이다.Since diatomaceous earth is mostly made of amorphous silica, it is a physicochemically stable inorganic material. It is porous, lightweight, and has excellent absorbency and heat insulation. Therefore, it is widely used in human life such as filtration aids, fillers, catalysts, absorbents, abrasives, and carriers. It is an excellent material.
규조토의 품질은 규조세포의 종류, 발달상태, 보존상태, 불순물질 함유량 화학적 조성, 그리고 안정성 등에 따라 결정되며, 제품의 물리화학적 특성에 따라 용도가 구분된다.The quality of diatomaceous earth is determined by the type of diatom cell, developmental state, preservation state, impurity content chemical composition, and stability, and its use is classified according to the physical and chemical properties of the product.
또한 규조토는 효소 및 미생물의 고정화가 필요한 생물공학산업을 포함하여 여러 용도에 적합하며, 높은 다공성과 불규칙한 모양의 입자구조를 가진 분말형태의 경량체로서 구조적 변형작용을 감소시켜 규조토를 사용하는 경우 반응조의 설계를 경제적으로 할 수 있게 될 뿐 아니라 활성촉매를 더 많이 고정시킬 수 있기 때문에 보다 효율적으로 촉매물질을 분산할 수 있게 되고, 다른 불활성 담체와 비교할 때에 상대적으로 넓은 표면적과 작은 기공구조로 인하여 촉매고정으로 효과적으로 할 수 있게 되며, 고온에서의 강도와 안정성이 우수하고 압축강도가 높음은 물론 마모에 대한 저항력이 크다.In addition, diatomaceous earth is suitable for various uses including biotechnology industry that requires the immobilization of enzymes and microorganisms, and is a powder-type lightweight body with high porosity and irregularly shaped particle structure. In addition to making the design economical, the more active catalysts can be immobilized, which leads to more efficient dispersion of the catalyst material and the relatively large surface area and small pore structure compared to other inert carriers. It can be effectively fixed, high strength and stability at high temperature, high compressive strength and high resistance to wear.
그리고 규조토는 높은 공극부피 때문에 자신의 무게의 2~3배(부피의 5배)나 되는 액체를 흡수하며, 냄새제거 및 지력보강제(bedding supplement), 암모니아 조절제로도 이용된다.And because of its high pore volume, diatomaceous earth absorbs two to three times its own weight (five times its volume), and is also used as an odor remover, bedding supplement, and ammonia regulator.
한편 본 발명의 음식물 소멸장치 소멸실에 규조토를 충전한 경우의 소멸율을 알아보기 위하여 다음과 같이 실험하였다.Meanwhile, the following experiment was conducted to determine the extinction rate when diatomaceous earth was filled in the extinction chamber of the food extinction device of the present invention.
<실험예1>Experimental Example 1
규조토 100g이 충전된 소멸실에 음식물 쓰레기 100g과 물 50g, 그리고 미생물 100ml을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.100g of food waste, 50g of water, and 100ml of microorganisms were added to the extinction chamber filled with 100g of diatomaceous earth, and stirred for 5 minutes at 25-minute intervals while maintaining the internal temperature of the extinction chamber at 20-35 ℃. The odor state was confirmed by, and the extinction rate was measured after 24 hours.
<실험예2>Experimental Example 2
규조토 150g이 충전된 소멸실에 음식물 쓰레기 100g과 물 50g, 그리고 미생물 100ml을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.100g of food waste, 50g of water, and 100ml of microorganisms were added to the extinction chamber filled with 150g of diatomaceous earth, and stirred for 5 minutes at 25-minute intervals while maintaining the internal temperature of the extinction chamber at 20-35 ℃. The odor state was confirmed by, and the extinction rate was measured after 24 hours.
<실험예3>Experimental Example 3
규조토 200g이 충전된 소멸실에 음식물 쓰레기 100g과 물 50g, 그리고 미생물 100ml을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.100 g of food waste, 50 g of water, and 100 ml of microorganisms were added to the extinction chamber filled with 200 g of diatomaceous earth, and stirred for 5 minutes at 25-minute intervals while maintaining the internal temperature of the extinction chamber at 20-35 ° C. The odor state was confirmed by, and the extinction rate was measured after 24 hours.
<실험예4>Experimental Example 4
규조토 250g이 충전된 소멸실에 음식물 쓰레기 100g과 물 50g, 그리고 미생물 100ml을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.100 g of food waste, 50 g of water, and 100 ml of microorganisms were put in a quench chamber filled with 250 grams of diatomaceous earth, and stirred for 5 minutes at 25-minute intervals while maintaining the internal temperature of the quench chamber at 20-35 ° C. The odor state was confirmed by, and the extinction rate was measured after 24 hours.
<실험예5>Experimental Example 5
규조토 300g이 충전된 소멸실에 음식물 쓰레기 100g과 물 50g, 그리고 미생물 150ml을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.100g of food waste, 50g of water, and 150ml of microorganisms were added to the extinction chamber filled with 300g of diatomaceous earth, and stirred for 5 minutes at 25-minute intervals while maintaining the internal temperature of the extinction chamber at 20-35 ℃. The odor state was confirmed by, and the extinction rate was measured after 24 hours.
이상의 실험예1에서 실험예5까지에 사용된 음식물 쓰레기의 주요 내용물은 밥, 김치, 시금치, 미역줄기, 김, 생선, 계란말이, 대구탕이었으며, 그 실험결과를 표1에 나타내었다.The main contents of the food waste used in the above Experimental Example 1 to Experimental Example 5 were rice, kimchi, spinach, seaweed stem, seaweed, fish, egg roll, Daegu-tang, and the experimental results are shown in Table 1.
<표1><Table 1>
소멸실에 우드칩을 충전한 경우의 소멸율을 알아보기 위하여 다음과 같이 실험하였다.In order to determine the extinction rate when the wood chip was charged to the extinction chamber, the following experiment was conducted.
<비교예1-1>Comparative Example 1-1
우드칩 160g이 충전된 소멸실에 음식물 쓰레기 200g을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 48시간 경과 후 소멸율을 측정하였다.200g of food waste was put into the extinction chamber filled with 160g of wood chips and stirred for 5 minutes at 25-minute intervals while maintaining the internal temperature of the extinction chamber at 20 ~ 35 ℃. After 10 hours, the smell test was confirmed by olfactory test. After 48 hours, the extinction rate was measured.
<비교예2-1><Comparative Example 2-1>
우드칩 160g이 충전된 소멸실에 음식물 쓰레기 200g을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 공기를 주입하면서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 48시간 경과 후 소멸율을 측정하였다.200g of food waste was put into the extinction chamber filled with 160g of wood chips and stirred for 5 minutes at 25 minute intervals while injecting air while maintaining the internal temperature of the extinction chamber at 20-35 ℃. The odor was checked and the disappearance rate was measured after 48 hours.
<비교예3-1><Comparative Example 3-1>
우드칩 160g이 충전된 소멸실에 음식물 쓰레기 200g과 물 20g을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 48시간 경과 후 소멸율을 측정하였다.Put 200g of food waste and 20g of water in the extinction chamber filled with 160g of wood chips, stir for 5 minutes at intervals of 25 minutes while maintaining the internal temperature of the extinction chamber at 20 ~ 35 ℃ The state was confirmed and the disappearance rate was measured after 48 hours.
<비교예4-1><Comparative Example 4-1>
우드칩 160g이 충전된 소멸실에 음식물 쓰레기 200g과 물 20g을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 공기를 주입하면서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 48시간 경과 후 소멸율을 측정하였다.Put 200g of food waste and 20g of water into the extinction chamber filled with 160g of wood chips and stir for 5 minutes at 25 minute intervals while injecting air while maintaining the internal temperature of the extinction chamber at 20 ~ 35 ℃. The smell was confirmed by the test, and the disappearance rate was measured after 48 hours.
<비교예5-1><Comparative Example 5-1>
우드칩 100g이 충전된 소멸실에 음식물 쓰레기 100g을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.Put 100g of food waste into the extinction chamber filled with 100g of wood chips and stir for 5 minutes at 25min intervals while maintaining the internal temperature of the extinction chamber at 20 ~ 35 ℃, and check the smell after 10 hours by olfactory test. After 24 hours, the extinction rate was measured.
<비교예6-1><Comparative Example 6-1>
우드칩 100g이 충전된 소멸실에 음식물 쓰레기 100g을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 공기를 주입하면서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.100g of food waste was put into the quenching chamber filled with 100g of wood chips and stirred for 5 minutes at 25 minute intervals while injecting air while maintaining the internal temperature of the quenching chamber at 20 ~ 35 ℃. The odor was checked and the extinction rate was measured after 24 hours.
<비교예7-1><Comparative Example 7-1>
우드칩 200g이 충전된 소멸실에 음식물 쓰레기 100g과 물 20ml를 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 30분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.Put 100g of food waste and 20ml of water in the extinction chamber filled with 200g of wood chips, stir for 5 minutes at intervals of 30 minutes while maintaining the internal temperature of the extinction chamber at 20 ~ 35 ℃ The state was confirmed and the disappearance rate was measured after 24 hours.
<비교예8-1><Comparative Example 8-1>
우드칩 150g이 충전된 소멸실에 음식물 쓰레기 300g을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 30분 간격으로 10분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.Put 300g of food waste into the extinction chamber filled with 150g of wood chips and stir for 10 minutes at intervals of 30 minutes while maintaining the internal temperature of the extinction chamber at 20 ~ 35 ℃. After 24 hours, the extinction rate was measured.
<비교예9-1><Comparative Example 9-1>
우드칩 150g이 충전된 소멸실에 음식물 쓰레기 300g을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 공기를 주입하면서 30분 간격으로 10분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.After putting 300g of food waste into the extinction chamber filled with 150g of wood chips and injecting air while maintaining the internal temperature of the extinction chamber at 20 ~ 35 ℃, stirring for 10 minutes at intervals of 10 minutes, and then by olfactory test. The odor was checked and the extinction rate was measured after 24 hours.
이상의 비교예1-1에서 비교예9-1까지에 사용된 음식물 쓰레기는 일반 식당의 잔반이었으며, 그 실험결과를 표2에 나타내었다.The food waste used in Comparative Example 1-1 to Comparative Example 9-1 was the residue of a general restaurant, and the experimental results are shown in Table 2.
<표2><Table 2>
소멸실에 세라믹볼을 충전한 경우의 소멸율을 알아보기 위하여 다음과 같이 실험하였다.In order to determine the decay rate when the ceramic ball was filled in the decay chamber, the experiment was as follows.
<비교예1-2><Comparative Example 1-2>
세라믹볼 840g이 충전된 소멸실에 음식물 쓰레기 200g, 미생물 활성제 5ml를 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 48시간 경과 후 소멸율을 측정하였다.200g of food waste and 5ml of microbial activator were added to the decay chamber filled with 840g of ceramic balls, and stirred for 5 minutes at intervals of 25 minutes while maintaining the internal temperature of the decay chamber at 20-35 ℃. The odor was checked and the disappearance rate was measured after 48 hours.
<비교예2-2><Comparative Example 2-2>
세라믹볼 840g이 충전된 소멸실에 음식물 쓰레기 200g, 미생물 활성제 10ml를 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 공기를 주입하면서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 48시간 경과 후 소멸율을 측정하였다.After putting 200g of food waste and 10ml of microbial activator into the decay chamber filled with 840g of ceramic balls and injecting air while maintaining the internal temperature of the decaying chamber at 20 ~ 35 ℃, stirring for 5 minutes at 25 minute intervals after 10 hours Odor status was confirmed by olfactory test, and the disappearance rate was measured after 48 hours.
<비교예3-2><Comparative Example 3-2>
세라믹볼 840g이 충전된 소멸실에 음식물 쓰레기 200g과 물 20g, 미생물 활성제 20ml를 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 48시간 경과 후 소멸율을 측정하였다.200g of food waste, 20g of water, and 20ml of microbial activator were put into a Balls filled with Ceramic Ball 840g and stirred for 5 minutes at intervals of 25 minutes while maintaining the internal temperature at 20 ~ 35 ℃. The smell was confirmed by the test, and the disappearance rate was measured after 48 hours.
<비교예4-2><Comparative Example 4-2>
세라믹볼 840g이 충전된 소멸실에 음식물 쓰레기 200g과 물 20g, 미생물 활성제 10ml를 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 공기를 주입하면서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 48시간 경과 후 소멸율을 측정하였다.Put 200g of food waste, 20g of water, and 10ml of microbial activator into the decay chamber filled with 840g of ceramic balls, and inject air while maintaining the internal temperature of the decaying chamber at 20 ~ 35 ℃ and stir for 5 minutes at 25 minutes intervals. After the passage of time, the smell was confirmed by an olfactory test, and the disappearance rate was measured after 48 hours.
<비교예5-2><Comparative Example 5-2>
세라믹볼 100g이 충전된 소멸실에 음식물 쓰레기 100g, 미생물 활성제 5ml를 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.100g of food waste and 5ml of microbial activator were put into a decay chamber filled with 100g of ceramic balls, and stirred for 5 minutes at intervals of 25 minutes while maintaining the internal temperature of the decay chamber at 20-35 ° C. The odor was checked and the extinction rate was measured after 24 hours.
<비교예6-2><Comparative Example 6-2>
세라믹볼 100g이 충전된 소멸실에 음식물 쓰레기 100g, 미생물 활성제 10ml를 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 공기를 주입하면서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.After putting 100g of food waste and 10ml of microbial activator into a decay chamber filled with 100g of ceramic balls, stirring for 5 minutes at 25 minute intervals while injecting air while maintaining the internal temperature of the decaying chamber at 20-35 ° C, and after 10 hours Odor status was confirmed by olfactory test, and the extinction rate was measured after 24 hours.
<비교예7-2><Comparative Example 7-2>
세라믹볼 200g이 충전된 소멸실에 음식물 쓰레기 100g과 물 20ml, 미생물 활성제 10ml를 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 공기를 주입하면서 30분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.Put 100g of food waste, 20ml of water, and 10ml of microbial activator into the decay chamber filled with 200g of ceramic balls, and inject the air at 30 ~ 35 ℃ while maintaining the internal temperature of 20. After a lapse of time, the smell was confirmed by an olfactory test, and the extinction rate was measured after 24 hours.
<비교예8-2><Comparative Example 8-2>
세라믹볼 150g이 충전된 소멸실에 음식물 쓰레기 300g, 미생물 활성제 10ml를 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 30분 간격으로 10분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.300g of food waste and 10ml of microbial activator were added to the extinction chamber filled with 150g of ceramic balls, and stirred for 10 minutes at intervals of 30 minutes while maintaining the internal temperature of the extinction chamber at 20-35 ℃. The odor was checked and the extinction rate was measured after 24 hours.
<비교예9-2><Comparative Example 9-2>
세라믹볼 150g이 충전된 소멸실에 음식물 쓰레기 300g, 미생물 활성제 20ml를 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 공기를 주입하면서 30분 간격으로 10분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.After putting 300g of food waste and 20ml of microbial activator into the quench chamber filled with 150g of ceramic balls, stirring for 10 minutes at 30 minute intervals while injecting air while maintaining the internal temperature of the quench chamber at 20-35 ℃, and after 10 hours Odor status was confirmed by olfactory test, and the extinction rate was measured after 24 hours.
이상의 비교예1-2에서 비교예9-2까지에 사용된 음식물 쓰레기는 일반 식당의 잔반, 라면, 커피 등이었으며, 그 실험결과를 표3에 나타내었다.Food wastes used in Comparative Examples 1-2 and Comparative Example 9-2 were leftovers, ramen, coffee, and the like of a general restaurant, and the experimental results are shown in Table 3.
<표3><Table 3>
규조토의 소멸율과 우드칩의 소멸율 및 세라믹볼의 소멸율과 비교하기 위하여 다음과 같이 실험하였다.In order to compare the disappearance rate of diatomaceous earth, wood chip and ceramic ball, the following experiments were carried out.
<실험예6>Experimental Example 6
규조토 200g이 충전된 소멸실에 음식물 쓰레기 200g과 그리고 미생물 100ml을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.200g of food waste and 100ml of microorganisms were put in the extinction chamber filled with 200g of diatomaceous earth and stirred for 5 minutes at 25min intervals while maintaining the internal temperature of the extinction chamber at 20 ~ 35 ℃. The state was confirmed and the disappearance rate was measured after 24 hours.
<비교예10-1><Comparative Example 10-1>
우드칩 200g이 충전된 소멸실에 음식물 쓰레기 200g을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.Put 200g of food waste into the extinction chamber filled with wood chips 200g and stir for 5 minutes at intervals of 25 minutes while maintaining the internal temperature of the extinction chamber at 20 ~ 35 ℃ and check the smell after 10 hours by olfactory test. After 24 hours, the extinction rate was measured.
<비교예10-2><Comparative Example 10-2>
세라믹볼 200g이 충전된 소멸실에 음식물 쓰레기 200g, 미생물 50ml을 투입하고 소멸실의 내부온도를 20~35℃로 유지한 상태에서 25분 간격으로 5분간 교반하여 10시간 경과 후 후각테스트에 의해 악취상태를 확인하고, 24시간 경과 후 소멸율을 측정하였다.200g of food waste and 50ml of microorganisms were put in a quench chamber filled with 200g of ceramic balls and stirred for 5 minutes at intervals of 25 minutes while maintaining the internal temperature of the quench chamber at 20-35 ℃. The state was confirmed and the disappearance rate was measured after 24 hours.
이상의 실험예6, 비교예6-1, 비교예6-2에 사용된 음식물의 주요 내용물은 밥, 무생채, 어묵볶음, 쑥갓무침, 생선, 김, 계란말이, 양배추쌈, 생태탕이었으며, 그 실험결과를 표에 나타내었다.The main contents of the foods used in the above Experimental Example 6, Comparative Example 6-1, Comparative Example 6-2 were rice, unsalted vegetables, fried fish cakes, garland chrysanthemum, fish, seaweed, egg rolls, cabbage ssam, eco-tang, and the results of the experiment Shown in the table.
<표5><Table 5>
이상의 실험예 및 비교예와 같이 동일한 조건이라면 처리용 베이스(11)로 무기질의 규조토를 사용하는 것이 유기질의 우드칩이나 세라믹볼을 사용하는 것보다 음식물 쓰레기 소멸효과가 뛰어나고 악취발생도 적음을 알 수 있다.Under the same conditions as in the above experimental and comparative examples, it can be seen that using inorganic diatomaceous earth as the treatment base 11 has better food waste extinction effect and less odor generation than using organic wood chips or ceramic balls. have.
이상에서 설명한 바와 같이 본 발명은 소멸실(12)에 규조토를 음식물 쓰레기 처리용 베이스(21)로 충전하고, 분사노즐(22)을 통해 소멸실(12) 내부에 액상의 미생물과 활성제, 악취제거제 등을 자동으로 분사할 수 있도록 한 것으로, 본 발명에 의하면 처리용 베이스(21)로 부피가 작고 잘 썩지 않는 무기질의 규조토를 사용함으로써 악취발생을 억제할 수 있게 되어 악취제거구조를 간편하게 구성할 수 있게 될 뿐 아니라 소멸실(12)의 부피 및 장치 전체 부피를 감소시켜 소형화 및 경량화를 도모할 수 있게 되고, 처리용 베이스(21)의 수명을 크게 연장할 수 있게 됨은 물론 처리용 베이스(21)에서 염분만을 제거한 후 재활용할 수 있게 되므로 환경보호에도 크게 이바지할 수 있게 하는 등의 효과를 얻을 수 있게 된다.As described above, the present invention fills the quench chamber 12 with diatomaceous earth as a food waste treatment base 21, and the liquid microorganisms, activator, and odor remover inside the quench chamber 12 through the injection nozzle 22. It is possible to automatically spray, etc., according to the present invention by using a small volume of inorganic diatomaceous earth as the base 21 for treatment, it is possible to suppress the occurrence of odor can be easily configured odor removal structure In addition to reducing the volume of the extinction chamber 12 and the total volume of the device can be miniaturized and lightened, it is possible to greatly extend the life of the processing base 21, as well as the processing base 21 Since only salinity can be removed and recycled, it is possible to contribute to environmental protection.
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| KR1020010011342A KR20020071283A (en) | 2001-03-06 | 2001-03-06 | a food-rest treatment apparatus |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| KR20160015673A (en) | 2014-07-31 | 2016-02-15 | 한온시스템 주식회사 | Evaporator |
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| KR19980023840A (en) * | 1996-09-25 | 1998-07-06 | 권승구 | Aging and manufacturing methods of organic fertilizers and materials that minimize the input of moisture regulators such as sawdust and rice hulls |
| KR19980076169A (en) * | 1997-04-07 | 1998-11-16 | 박경수 | Fertilizer manufacturing method using siliceous porous body and shaft powder |
| JPH11128889A (en) * | 1997-10-31 | 1999-05-18 | Hitachi Taga Technol Co Ltd | Garbage disposal machine |
| KR20010035064A (en) * | 2000-12-12 | 2001-05-07 | 유규재 | Organic nutritional agent for plants and the preparation method thereof |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR19980023840A (en) * | 1996-09-25 | 1998-07-06 | 권승구 | Aging and manufacturing methods of organic fertilizers and materials that minimize the input of moisture regulators such as sawdust and rice hulls |
| KR19980076169A (en) * | 1997-04-07 | 1998-11-16 | 박경수 | Fertilizer manufacturing method using siliceous porous body and shaft powder |
| JPH11128889A (en) * | 1997-10-31 | 1999-05-18 | Hitachi Taga Technol Co Ltd | Garbage disposal machine |
| KR20010035064A (en) * | 2000-12-12 | 2001-05-07 | 유규재 | Organic nutritional agent for plants and the preparation method thereof |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| KR20160015673A (en) | 2014-07-31 | 2016-02-15 | 한온시스템 주식회사 | Evaporator |
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