KR19990064926A - Organic substance fertilizer(manure) for manufacturing method and system - Google Patents
Organic substance fertilizer(manure) for manufacturing method and system Download PDFInfo
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- KR19990064926A KR19990064926A KR1019990018584A KR19990018584A KR19990064926A KR 19990064926 A KR19990064926 A KR 19990064926A KR 1019990018584 A KR1019990018584 A KR 1019990018584A KR 19990018584 A KR19990018584 A KR 19990018584A KR 19990064926 A KR19990064926 A KR 19990064926A
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- fermentation
- compost
- pipe
- sewage
- sludge
- Prior art date
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- 238000004519 manufacturing process Methods 0.000 title claims description 9
- 239000000126 substance Substances 0.000 title description 3
- 210000003608 fece Anatomy 0.000 title description 2
- 239000010871 livestock manure Substances 0.000 title description 2
- 239000003337 fertilizer Substances 0.000 title 1
- 238000000855 fermentation Methods 0.000 claims abstract description 31
- 230000004151 fermentation Effects 0.000 claims abstract description 29
- 239000002361 compost Substances 0.000 claims abstract description 26
- 239000010802 sludge Substances 0.000 claims abstract description 19
- 238000011282 treatment Methods 0.000 claims abstract description 17
- 239000010865 sewage Substances 0.000 claims abstract description 16
- 239000003895 organic fertilizer Substances 0.000 claims abstract description 11
- 239000002699 waste material Substances 0.000 claims abstract description 8
- 238000002347 injection Methods 0.000 claims abstract description 7
- 239000007924 injection Substances 0.000 claims abstract description 7
- 150000007524 organic acids Chemical class 0.000 claims abstract description 7
- 230000003584 silencer Effects 0.000 claims abstract description 6
- 239000010794 food waste Substances 0.000 claims abstract description 4
- 240000007594 Oryza sativa Species 0.000 claims abstract description 3
- 235000007164 Oryza sativa Nutrition 0.000 claims abstract description 3
- 235000009566 rice Nutrition 0.000 claims abstract description 3
- 239000010903 husk Substances 0.000 claims abstract 2
- 230000032683 aging Effects 0.000 claims description 5
- 239000002994 raw material Substances 0.000 claims description 5
- 238000002156 mixing Methods 0.000 claims description 3
- 239000004615 ingredient Substances 0.000 claims 1
- 230000005070 ripening Effects 0.000 claims 1
- 238000000034 method Methods 0.000 abstract description 24
- 239000002351 wastewater Substances 0.000 abstract description 7
- 238000004065 wastewater treatment Methods 0.000 abstract description 3
- 230000018044 dehydration Effects 0.000 abstract description 2
- 238000006297 dehydration reaction Methods 0.000 abstract description 2
- 229910001385 heavy metal Inorganic materials 0.000 abstract description 2
- 230000003211 malignant effect Effects 0.000 abstract description 2
- 239000003643 water by type Substances 0.000 abstract description 2
- 239000003344 environmental pollutant Substances 0.000 abstract 1
- 238000003912 environmental pollution Methods 0.000 abstract 1
- 238000010438 heat treatment Methods 0.000 abstract 1
- 229910052500 inorganic mineral Inorganic materials 0.000 abstract 1
- 239000011707 mineral Substances 0.000 abstract 1
- 231100000719 pollutant Toxicity 0.000 abstract 1
- 238000009264 composting Methods 0.000 description 7
- 241000196324 Embryophyta Species 0.000 description 5
- 244000052616 bacterial pathogen Species 0.000 description 3
- 238000007689 inspection Methods 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 239000005416 organic matter Substances 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- 239000002689 soil Substances 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 241000238631 Hexapoda Species 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 235000013305 food Nutrition 0.000 description 2
- 230000012010 growth Effects 0.000 description 2
- 230000035800 maturation Effects 0.000 description 2
- 235000019645 odor Nutrition 0.000 description 2
- 239000010815 organic waste Substances 0.000 description 2
- 239000002023 wood Substances 0.000 description 2
- 241000251468 Actinopterygii Species 0.000 description 1
- 241001474374 Blennius Species 0.000 description 1
- 235000019738 Limestone Nutrition 0.000 description 1
- 206010027476 Metastases Diseases 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- -1 bark Substances 0.000 description 1
- 239000006227 byproduct Substances 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 235000013339 cereals Nutrition 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 235000013399 edible fruits Nutrition 0.000 description 1
- 235000013601 eggs Nutrition 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 235000013312 flour Nutrition 0.000 description 1
- 239000003864 humus Substances 0.000 description 1
- 239000002440 industrial waste Substances 0.000 description 1
- 238000010169 landfilling Methods 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 235000013372 meat Nutrition 0.000 description 1
- 230000009401 metastasis Effects 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 238000012858 packaging process Methods 0.000 description 1
- 239000010816 packaging waste Substances 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 244000052769 pathogen Species 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 230000008635 plant growth Effects 0.000 description 1
- 239000010909 process residue Substances 0.000 description 1
- 230000010349 pulsation Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 239000010801 sewage sludge Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000010902 straw Substances 0.000 description 1
- 235000013619 trace mineral Nutrition 0.000 description 1
- 239000011573 trace mineral Substances 0.000 description 1
- 235000013311 vegetables Nutrition 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D35/00—Filtering devices having features not specifically covered by groups B01D24/00 - B01D33/00, or for applications not specifically covered by groups B01D24/00 - B01D33/00; Auxiliary devices for filtration; Filter housing constructions
- B01D35/14—Safety devices specially adapted for filtration; Devices for indicating clogging
- B01D35/147—Bypass or safety valves
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/441—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Fertilizers (AREA)
Abstract
본 발명은 각종 하수 및 폐수처리 과정에서 생긴 슬러지를 발효시켜 유기질 비료(퇴비)를 제조하는 방법 및 장치에 관한 것이다.The present invention relates to a method and apparatus for producing organic fertilizer (compost) by fermenting sludge produced during various sewage and wastewater treatment processes.
현재까지의 각종 하수 및 폐수처리장에서 생긴 슬러지는 대게 활성 슬러지로서 1차 탈수과정을 지난후는 슬러지 소화조에서 1개월간 소화시킨후 다시 쓰레기 매립장에 매립하고 있으나 매립장에 강우가 있을 때에는 매입된 슬러지는 다량의 강우에 의해 재용해된 후 악성 폐수로 환원되어 주변의 공공 수역으로 유출되어 결국은 하폐수 처리하기 전과 동일한 상태로 환원되는 폐단이 있고 또한 하수처리장에서 발생된 슬리지를 매입하지 않고 소각처리 방법을 택하고 있는 경우도 있으나, 이 경우는 에너지 손실이 크고 대기를 오염시키는 폐단이 있을 뿐만 아니라 이 소각된 무기질 속에는 중금속이 함유되어 있어 제 2, 제 3의 환경공해를 유발하는 폐단이 있었던 것이다.Sludges from various sewage and wastewater treatment plants up to now are mostly activated sludges. After the first dehydration process, they are digested in sludge digesters for 1 month and then landfilled in landfills, but when there is rainfall in landfills, After being re-dissolved by heavy rain, the wastewater is reduced to malignant wastewater and is discharged to the surrounding public waters and eventually reduced to the same state as before the sewage treatment.In addition, the incineration treatment method is selected without purchasing sludge generated in the sewage treatment plant. In this case, not only are the energy losses large and pollutants that pollute the air, but also incinerated minerals contain heavy metals that cause secondary and third environmental pollution.
본 발명은 이상의 문제점을 해결하고자 발명한 것으로 이의 발명요지는 오수 및 하수처리장등에서 생성된 슬러지에 축분 톱밥 왕겨 또는 음식쓰레기등의 유기산 폐기물을 첨가 혼합한후 이를 발효조(12)에 투입하여 50∼65℃의 열을 가하면서 3∼5주간 발효시키고 발효가 끝난후는 숙성조(후숙조)에 투입하여 30일 이상 숙성하므로서 유기질 비료(퇴비)를 얻을수 있게 하고 이의 장치에 일어나는 기계실(1)과 발효창고(11)로 구분하되 기계실(1)에는 진동방지용 고무판(1')을 개재시켜 모터(2)와 송풍기(3)및 이에 진동흡수관(4')을 개재한 소음기(4)및 안절밸브(5')와 채크밸브(5)를 개재한 분배관(6)을 설치하고 분배관(6)에는 조절밸브(6)와 연결관(6')을 개재한 매인파이프(7)를 설치하되 이 매인파이프(7)에는 발효창고(11)의 바닥면에 형성된 발효조의 홈(11')에 끼움 배치되게한 다수의 파이프라인(8)이 연결되어 있고 이 파이프라인(8)에는 일정간격으로 다수의 분사관(8')이 설치되어 발효퇴비에 매입되어 지게한 것이다.The present invention has been invented to solve the above problems, the present invention is added to the sludge produced in sewage and sewage treatment plant and the like, mixed with organic acid waste, such as crushed sawdust rice husk or food waste, and then added to the fermenter (12) 50 ~ 65 Fermentation for 3 to 5 weeks with heating at ℃, and after fermentation is completed, it is put into a maturing tank (post-bath) and aged for more than 30 days to obtain organic fertilizer (compost), and the machine room (1) and fermentation occurring in the apparatus It is divided into a warehouse (11), but the machine room (1) through the anti-vibration rubber plate (1 ') through the motor (2) and the blower (3) and the silencer (4) and the rest valve through the vibration absorbing pipe (4') (5 ') and the distribution pipe (6) through the check valve (5) is installed and the distribution pipe (6) is installed the main pipe (7) via the control valve (6) and the connecting pipe (6') The main pipe 7 is inserted into the groove 11 'of the fermentation tank formed on the bottom surface of the fermentation warehouse 11. A plurality of pipelines (8) and is connected there is a pipeline (8) a plurality of injection pipe (8 ') being arranged at a predetermined interval a is provided to a become embedded in the fermented compost.
Description
본 발명은 각종 하수 및 폐수처리 과정에서 생성된 슬러지를 발효시켜 유기질비료(퇴비)로 제조하는 방법 및 이의 장치에 관한 것이다.The present invention relates to a method for producing organic fertilizer (compost) by fermenting sludge produced in various sewage and wastewater treatment processes and apparatus thereof.
현재 우리나라의 공장 폐수나 하수처리 공정에서 발생되는 슬러지는 대개 활성 슬러지로서 1차 탈수과정을 지나면 슬러지 소화조에서 1개월간 소화시킨후 다시 쓰레기 매립장에 매립하고 있는 실정이다.At present, sludge generated from the factory wastewater or sewage treatment process in Korea is activated sludge. After the first dehydration process, the sludge is digested in the sludge digester for one month and then landfilled in the landfill.
그리고 폐수 슬러지의 화학 및 활성 슬러지는 소화과정 전량 산업폐기물 매립지에 매립하고 있다. 그러나 매립장에 강우가 있을시는 매립된 슬러지는 다수의 강우(빗물)에 의해 재용해된 후 악성폐수로 환원되어 주변의 공공수역으로 유출되고 결국은 하폐수처리 하기전과 동일한 상태로 환원 되므로 현재 우리나라의 하폐수처리는 처리하기전과 동일한 상태로 환원 되어있어 이점은 최대의 사회적 문제점이 되고 있는 것이다.In addition, chemical and activated sludge from wastewater sludge is buried in industrial waste landfills. However, if there is rainfall in the landfill, the landfilled sludge is re-dissolved by a number of rainfalls (rainwater) and then reduced to malignant wastewater, which is discharged into the surrounding public waters and eventually reduced to the same state as before the sewage treatment. Sewage water treatment is reduced to the same state as before treatment, which is the biggest social problem.
그리고 매립장에서 발생되는 침출수의 성상은 매우 고농도(BOD 20,000㎎/ℓ이상)이므로 형식적으로 설치된 침출수 처리장에서 고농도 유기폐수(슬러지 요출액 포함)를 처리하기 위해서는 매우 어려운 점이 있기 때문에 하수 처리장에서 발생되는 슬러지를 매립하지 않고 처리할 수 있는 각종 기술들이 다각도로 연구된바 있으나 그중의 한 방법으로서 소각처리 방법을 체택하고 있는 것이다.Since the leachate generated from landfill is very high concentration (more than BOD 20,000mg / ℓ), it is very difficult to treat high concentration organic wastewater (including sludge effluent) in the formally installed leachate treatment plant. Various technologies that can be processed without landfilling have been studied in various ways, but one of them is the incineration method.
그러나 이와 같은 소각 처리방법에는 다단식 소각로가 도입되어 있는바 이는 에너지의 손실이 크고 대기를 오염시키는 폐단이 있고 특히 소각 잔재 속에는 거의 무기질로서 이속에는 중금속이 함유되어 있기 때문에 제 2, 제 3의 환경 오염을 유발케 하는 폐단이 있었던 것이다.However, the multi-stage incinerator has been introduced in such an incineration treatment method, which has a high energy loss and has a contaminated end that pollutes the air. In particular, incineration residues are almost inorganic, and heavy metals are contained in the second incineration residues. There was a pulsation that caused.
본 발명은 이상의 문제점을 해결하고자 발명한 것으로 이의 발명요지는 전통적으로 썩기쉬운 유기물들을 생태학적으로 안정화된 형태로 전환 시키고 유기병원체를 파괴시키는 원리인 퇴비로 만들게되면 식물의 병균, 잡초의 씨앗 곤충이나 곤충알등을 파괴할 수 있다는 점과 이와 같이 퇴비화 하게되면 이 퇴비화 과정에서 발생되는 냄새를 대폭 감소할 수 있고 퇴비화된 후 남아있는 유기물은 낮은 분해속도로 생태적으로 안정화 되어지기 때문이며 또한 하수 슬리지의 퇴비화는 도시하수 슬러지및 산업슬러지와 같은 함수 물질들을 건조하는데 발생되는 악취를 방지할 수 있을 뿐만 아니라 적은 에너지 사용으로 이의 처리가 가능케 함과 동시 토양의 지기 증진에도 크게 기여할 수 있다는 점에 주안점을 둔것으로 이의 제조공정은 퇴비원료의 선택공정, 유기산 폐기물 혼합공정, 발효공정, 숙성(후숙)공정 성분 검사공정, 포장공정을 거쳐 유기질비료화 한 것이며 이의 장치에 있어서는 기계실에 설치된 송풍기에서 배출된 깨끗한 공기가 분배관(햇드)에서 분배된 후 매인파이프를 거쳐 발효창고 내에 설치된 발효조의 바닥면홈에 일정간격으로 배치된 파이프라인의 분사관을 통해 분사되게하되 이 분사관은 발효실내에 적충된 발효물속에 매입되게하고 발효된 발효 퇴비는 다시 그 상대편에 설치된 숙성조(후숙조)에 보내어 30일 이상 숙성시켜 성분 검사과정을 거쳐 유기질 비료(퇴비)화 시킬수 있게한 것이다.The present invention has been invented to solve the above problems, the present invention is to convert the conventional perishable organic matter into an ecologically stabilized form and to make the compost which is the principle of destroying organic pathogens, plant germs, weed seeds insects or Insect eggs can be destroyed, and this composting can greatly reduce the odor generated during the composting process, and the organic matter remaining after the composting is ecologically stabilized at a low decomposition rate. The focus is on not only preventing the odors generated from drying hydrous substances such as municipal sewage sludge and industrial sludge, but also making it possible to treat them with less energy and at the same time, contribute greatly to the improvement of soil retention. Its manufacturing process is the selection of compost raw materials It is organic fertilizer through the purification process, fermentation process, fermentation process, aging process, and packaging process.In this device, clean air from the blower installed in the machine room is distributed in the distribution pipe (head). The main pipe is sprayed through the injection pipe of the pipeline arranged at regular intervals in the bottom groove of the fermentation tank installed in the fermentation warehouse through the main pipe, and the injection pipe is embedded in the fermented product accumulated in the fermentation chamber and the fermented fermentation compost is again It is sent to the maturation tank (post-bath) installed on the other side and aged for more than 30 days to be organic fertilizer (compost) through the component inspection process.
제 1도는 본 발명의 공정표시도1 is a process display diagram of the present invention
제 2도는 본 발명의 장치 개략도2 is a schematic view of the apparatus of the present invention.
제 3도는 본 발명의 실시예도3 is an embodiment of the present invention
제 4도는 본 발명의 장치 요부사시도4 is a main component perspective view of the present invention
제 5도는 본 발명의 기계실의 구성도5 is a configuration diagram of the machine room of the present invention
*도면의 중요부분에 대한 부호의 설명* Explanation of symbols on important parts of drawing
101-퇴비원료의 선택공정 102-유기산 폐기물 혼합공정 103-발효공정101-Selection process of compost raw materials 102-Organic waste mixing process 103- Fermentation process
104-숙성공정 105-성분검사공정 106-포장공정 107-제품환성공정104-Maturation process 105-Component inspection process 106-Packing process 107-Product conversion process
1-기계실 1'-고무판 1-유입구 1'-베기구1-machine room 1'-rubber plate 1-inlet 1'-between
2-모터 2'-풀리 2-밸트 2'-커버2-motor 2'-pulley 2-belt 2'-cover
3-송풍기 3'-로터 3-여과필터 3'-소음기3-blower 3'-rotor 3-filtration filter 3'-silencer
4-소음기 4'-진동흡수관 5-밸브 5'-안전밸브4-silencer 4'-vibration absorption pipe 5-valve 5'-safety valve
5-압력케이지 6-분배관(햇드) 6'-연결관 6-밸브5-Pressure cage 6-Distribution pipe (head) 6'-Connector 6-valve
7-매인파이프 7'-조절밸브 8-파이프라인 8'-분사관7-main pipe 7'-regulating valve 8-pipeline 8'-injector
9-드래인밸브 10-콘토롤박스 11-발효창고 11'-바닥홈9-Drain valve 10-Control box 11-Effective warehouse 11'-Floor groove
12-발효조 12'-발효퇴비 13-숙성조 13'-숙성퇴비12-fermentation tank 12'-fermentation compost 13-aging tank 13'-aging compost
이를 도면에 의거 상세히 설명하면 다음과 같다.This will be described in detail based on the drawings.
먼저 제조공정에 있어 설명하면First, in the manufacturing process
제 1공정 - 오수나 하수처리 과정에서 생긴 슬리지등을 퇴비원료로 선택한다.Step 1-Select sludge from sewage or sewage treatment as compost.
제 2공정 - 제 1공정에서 선정된 퇴비원료에 축분과 톱밥 및 왕겨나 음식물 쓰레기등의 유기산 폐기물을 3:1 이하로 혼합한다.Step 2-Mix the compost raw materials selected in the first step with organic acid wastes such as stockpile, sawdust and rice hulls or food waste at less than 3: 1.
제 3공정 - 제 2공정에서 얻어진 홉합물을 발효조에 투입하여 이 혼합물속에 파이프라인을 배치한 후 50∼65℃의 온도가 유지될수있게 송풍기에서 생선된 공기를 주입시켜 3∼5주간에 발효시킨다.Step 3-The mixture obtained in the second step is placed in a fermenter, the pipeline is placed in the mixture, and the air from the blower is introduced to ferment for 3 to 5 weeks so that the temperature of 50 to 65 ℃ can be maintained. .
제 4공정 - 제 3공정에서 발효가 완료되면 이를 숙성조(후숙조)에 이송시켜 30일 이상 자체 숙성시킨다.4th process-After fermentation is completed in the 3rd process, it is transferred to a maturation tank (post-bath) and aged for 30 days or more.
제 5공정 - 제 4공정의 숙성이 완료되면 이를 검사하여 유기질 비료로서 적당한가 여부를 분석한다.After completion of the 5th-4th process, it is examined to determine whether it is suitable as an organic fertilizer.
제 6공정 - 제 5공정의 검사공정에서 유기질 비료로서 적합하다고 인정될시는 실수요자들이 사용하기에 편리하게 소분포장한다.If it is deemed suitable as organic fertilizer in the inspection process of the 6th process-5th process, it is conveniently small packaged for the real users.
필요에 따라서는 운반용 트럭의 적재함에 적재한 후 덮개로 덮은 후 수요현장에 직송 할수도 있다.If necessary, it can be loaded into a loading box of a transport truck, covered with a cover, and sent directly to a demand site.
그리고 본 발명의 제조장치에 있어 제 2도 및 제 5도에 의거 설명하면 다음과 같다.And in the manufacturing apparatus of the present invention will be described based on Figures 2 and 5 as follows.
보온벽으로된 기계실(1)의 일축에는 공기유입구(1)이 형성되고 타축에는 배기구(1')가 형성되며 바닥면에는 지지대판위에 완충용 고무판(1')을 깔고 그위에 모터(2) 송풍기(3)및 소음기(4), 분배기(햇드)(6)가 설치되어 있으되 모터(2)의 풀리(2')에는 송풍기(3)의 로터(3')의 축에 설치된 풀리와 밸트(2)로 연결하되 이 밸트(2)는 커버(2')내에 수납되며 송풍기(3)내에 설치된 로터(3')는 3엽헬리컬기어 방식과 3엽수퍼기어방식 또는 2엽스퍼기어를 사용할 수 있게 하고 송풍기(3)의 상부에는 소음기(3')를 개재한 여과필터(3)가 설치되고 송풍기(3)와 소음기(4)의 사이에는 진동흡수관(4')이 연결되고 소음기(4)와 분배관(6)사이에는 안전밸브(5') 및 압력게이지(5)를 개재한 채크밸브(5)가 설치되며 분배관(6)의 일측에는 밸브(6)를 개재한 매인파이프(7)가 설치되어 있으되 이의 양단에는 드레인밸브(9)가 설치되고 이 매인파이프(7)의 표면에는 일정간격을 두고 다수의 파이프라인(8)이 연결되어 있으되 이 파이프라인은 발효창고(11)내에 일정간격으로 설치되어 있는 발효조(12) 바닥면에 요설된 바닥홈(11')에 배치되어 있고 이 파이프라인(8')에는 일정간격으로 다수의 분사관(8')을 설치하여 발효조(12)내에 적충된 발효퇴비(12')속에 매설할 수 있게하며 발효조(12)의 대항측에는 다수의 숙성조(13)를 설치하여 발효된 퇴비를 장시간 숙성할 수 있게한 것이다. 그리고 분배관(6)에 다수의 연결관(6')을 연결하면 이의 발효 시설규모를 크게할 수 있다.An air inlet 1 is formed at one axis of the machine room 1 as a heat insulating wall, and an exhaust port 1 'is formed at the other axis, and a cushioning rubber plate 1' is laid on the support plate on the bottom surface thereof, and the motor 2 is placed thereon. A blower (3), a silencer (4), and a distributor (head) (6) are provided, but the pulley (2 ') of the motor (2) has a pulley and a belt installed on the shaft of the rotor (3') of the blower (3). 2), but the belt (2) is stored in the cover (2 '), and the rotor (3') installed in the blower (3) can use a three-leaf helical gear type, three-leaf super gear type or two-leaf spur gear. In the upper part of the blower (3) is installed a filtration filter (3) via a silencer (3 '), between the blower (3) and the silencer (4) is connected to a vibration absorbing pipe (4') and the silencer (4 ) And a check valve (5) via a safety valve (5 ') and a pressure gauge (5) are installed between the distribution pipe (6) and one side of the distribution pipe (6). 7) is installed but Drain valves 9 are installed at both ends, and a plurality of pipelines 8 are connected to the surface of the main pipe 7 at regular intervals, and the pipelines are installed at regular intervals in the fermentation warehouse 11. Fermentation compost accumulated in fermentation tank 12 is arranged in the bottom groove 11 'concave on the bottom of fermentation tank 12, and a plurality of injection pipes 8' are installed in the pipeline 8 'at regular intervals. It is possible to bury in (12 ') and to install a plurality of aging tank 13 on the opposite side of the fermentation tank 12 to allow the fermentation of the fermented compost for a long time. And connecting a plurality of connecting pipes (6 ') to the distribution pipe (6) can increase the size of its fermentation facility.
이상과 같이 구성된 본 발명은 유기질 비료(퇴비)의 제조방법과 이의 장치인바 본 발명의 제 1공정에서는 오폐수나 하폐수처리 과정에서 발생된 슬리지를 퇴비제조원료로 하고 제 2공정의 유기산 첨가물로서는 도살장 및 고기 포장 폐기물, 음식물 쓰레기, 가축부산물, 과일 야채폐기물, 식품가공 폐기물, 나무, 석회석, 잔듸깎은것, 인분 계분 우분 돈분 및 해초와 기타 수생식물 그리고 완성된 퇴비, 정화조 고형물, 나무껍질, 밀짚 나무재, 생선가공시 폐기물등의 유기산 폐물들이 3:1 이하 범위로 혼합된 상태에서 발효조(12)에 투입되며 전기한 유기산폐기물의 배합비는 수집된 유기산폐기물의 성상에 따라 적절히 가감 배합한다.The present invention configured as described above is a method for manufacturing organic fertilizer (compost) and its apparatus. In the first step of the present invention, the sludge generated in the wastewater or sewage water treatment process is used as a compost manufacturing raw material, and as the organic acid additive of the second step, the slaughterhouse and Meat packaging waste, food waste, livestock by-products, fruit vegetable waste, food processing waste, wood, limestone, chips, servings, flour, manure and seaweed and other aquatic plants, and finished compost, septic solids, bark, straw wood , The organic acid wastes such as waste during fish processing is added to the fermentation tank 12 in a mixed state of less than 3: 1, and the mixing ratio of the organic acid wastes described above is appropriately added or subtracted according to the properties of the collected organic acid wastes.
그리고 이를 발효조(12)내에 투입할때에는 파이프라인(8)에 연결된 분사관(8')이 적충된 발효물의 중심부에 위치되게한 후 송풍기(3)를 통해 외부의 신선한 공기가 유입 분사되게 하되 이때의 발효온도는 50~65℃ 이내로되게 압력 및 온도계를 이용하여 조정하며 이와 같은 압력 및 온도조절은 콘토롤박스(10)내에서 자동으로 조정한다. 그리고 발효가 끝난 발효퇴비는 숙성조(13)에 투입하여 30일이상 숙성(후성)하게되면 양질의 퇴비(유기질비료)가 된다.And when it is injected into the fermentation tank 12, the injection pipe (8 ') connected to the pipeline (8) is located in the center of the loaded fermented product and then the fresh air from the outside through the blower (3) is injected into the injection The fermentation temperature of the 50 ~ 65 ℃ to be adjusted by using a pressure and a thermometer, such pressure and temperature control is automatically adjusted in the control box (10). And fermented compost after the fermentation is put into the aging tank (13) is aged (over 30 days) is a good compost (organic fertilizer).
이상의 유기질 퇴비는 생태학적으로 생성되는 자체의 열에의해 호열성의 온도 조건하에서 발효 숙성하여 퇴비화시켜 땅에 적용될수 있도록한 것이므로 생태학적 분해에도 안정성이 있는 것이다.The above organic compost is fertilized by fermentation under the thermophilic temperature condition by its own ecologically generated heat, so that it can be applied to the ground, so it is stable to ecological degradation.
이상과 같이 본 발명은 유기폐기물을 이용하여 이를 발효 숙성하였기 때문에 그간의 생활 하수처리 및 산업 하수처리 과정의 슬러지와 식품가공 및 음식물처리 과정의 유기산 폐기물의 매립 또는 소각처리 과정에서 발생한 제반 문제점을 극복할 수 있는 이점은 물론 이를 퇴비화 함으로서 다음과 같은 자원 재활용에 있어 산업적으로 큰 잇점이 있는 것이다.As described above, the present invention overcomes the problems caused by landfill or incineration of organic sludge during food and food processing and sludge of domestic and industrial sewage treatments, since fermentation and aging of organic wastes. The benefits of doing so, of course, are composting, which has the industrial advantage of recycling resources such as:
첫째 퇴비는 적당한 토양구조와 함수 능력에 필요한 부식토를 공급하고 유지하는데 있어 유기물의 근원으로 작용할 수 있고First, compost can serve as a source of organic matter for supplying and maintaining the humus required for proper soil structure and water capacity.
둘째 퇴비는 곡물의 성장속도를 향상시킬수 있고 생태적으로 안정된 퇴비화가 되므로서 식물의 병균 감소와 병균에 대한 식물의 저항력을 활성화시킬수 있을 뿐만 아니라 퇴비화의 종말처리에 있어서는 유용한 미세 유기 조직에 의한 전이증식은 식물성장에 유해한 병균을 억제하는 역할을 한다.Secondly, composting can improve the growth rate of grain and become ecologically stable composting, which can reduce the germs of the plant and activate the plant's resistance to the germ, and the metastasis growth by microorganisms useful for the end treatment of composting Suppresses germs harmful to plant growth.
셋째 퇴비는 질소, 인 그리고 여러 가지 중요한 미량원소들을 비롯한 유용한 영양분을 함유하고 있어 토양 개선에 크게 기여할 수 있다.Third, compost contains valuable nutrients, including nitrogen, phosphorus and several important trace elements, which can greatly contribute to soil improvement.
Claims (2)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| KR1019990018584A KR19990064926A (en) | 1999-05-17 | 1999-05-17 | Organic substance fertilizer(manure) for manufacturing method and system |
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| Application Number | Priority Date | Filing Date | Title |
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| KR1019990018584A KR19990064926A (en) | 1999-05-17 | 1999-05-17 | Organic substance fertilizer(manure) for manufacturing method and system |
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| Publication Number | Publication Date |
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| KR19990064926A true KR19990064926A (en) | 1999-08-05 |
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| Application Number | Title | Priority Date | Filing Date |
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| KR1019990018584A KR19990064926A (en) | 1999-05-17 | 1999-05-17 | Organic substance fertilizer(manure) for manufacturing method and system |
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR20010113416A (en) * | 2000-06-19 | 2001-12-28 | 박인호 | Food trash treating method |
| KR20160097551A (en) * | 2015-02-09 | 2016-08-18 | 주식회사 엠오에이 | A manufacturing apparatus for organic ferilizer and fermentation liquefied fertilizer using food garbage and sludge in sewage and a manufacturing method thereof |
-
1999
- 1999-05-17 KR KR1019990018584A patent/KR19990064926A/en not_active Application Discontinuation
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR20010113416A (en) * | 2000-06-19 | 2001-12-28 | 박인호 | Food trash treating method |
| KR20160097551A (en) * | 2015-02-09 | 2016-08-18 | 주식회사 엠오에이 | A manufacturing apparatus for organic ferilizer and fermentation liquefied fertilizer using food garbage and sludge in sewage and a manufacturing method thereof |
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