CN106116734A - Aerobic composting device and aerobic composting method for organic solid waste - Google Patents
Aerobic composting device and aerobic composting method for organic solid waste Download PDFInfo
- Publication number
- CN106116734A CN106116734A CN201610455168.0A CN201610455168A CN106116734A CN 106116734 A CN106116734 A CN 106116734A CN 201610455168 A CN201610455168 A CN 201610455168A CN 106116734 A CN106116734 A CN 106116734A
- Authority
- CN
- China
- Prior art keywords
- grate
- leachate
- discharge
- solid waste
- organic solid
- 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.)
- Granted
Links
- 238000009264 composting Methods 0.000 title claims abstract description 68
- 238000000034 method Methods 0.000 title claims abstract description 44
- 239000002910 solid waste Substances 0.000 title claims abstract description 36
- 239000000463 material Substances 0.000 claims abstract description 89
- 230000018044 dehydration Effects 0.000 claims abstract description 50
- 238000006297 dehydration reaction Methods 0.000 claims abstract description 50
- 238000001125 extrusion Methods 0.000 claims abstract description 40
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 32
- 239000001301 oxygen Substances 0.000 claims abstract description 32
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 32
- 239000002361 compost Substances 0.000 claims abstract description 19
- 238000007599 discharging Methods 0.000 claims abstract description 17
- 238000005507 spraying Methods 0.000 claims abstract description 9
- 230000008569 process Effects 0.000 claims description 25
- 239000007921 spray Substances 0.000 claims description 21
- 239000007788 liquid Substances 0.000 claims description 12
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 12
- 238000005273 aeration Methods 0.000 claims description 9
- 230000032258 transport Effects 0.000 claims description 7
- 238000001914 filtration Methods 0.000 claims description 3
- 230000002093 peripheral effect Effects 0.000 claims description 3
- 230000000717 retained effect Effects 0.000 claims description 3
- 239000013072 incoming material Substances 0.000 claims description 2
- 239000000758 substrate Substances 0.000 abstract description 2
- 239000010802 sludge Substances 0.000 description 8
- 239000007789 gas Substances 0.000 description 7
- 239000002699 waste material Substances 0.000 description 6
- 238000002156 mixing Methods 0.000 description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 239000010865 sewage Substances 0.000 description 4
- 241001148470 aerobic bacillus Species 0.000 description 3
- 238000011081 inoculation Methods 0.000 description 3
- 244000005700 microbiome Species 0.000 description 3
- 239000005416 organic matter Substances 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 238000005054 agglomeration Methods 0.000 description 2
- 230000002776 aggregation Effects 0.000 description 2
- 230000001580 bacterial effect Effects 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 230000029087 digestion Effects 0.000 description 2
- 238000000855 fermentation Methods 0.000 description 2
- 230000004151 fermentation Effects 0.000 description 2
- 239000003337 fertilizer Substances 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 239000010806 kitchen waste Substances 0.000 description 2
- 238000002386 leaching Methods 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 239000010902 straw Substances 0.000 description 2
- 239000002028 Biomass Substances 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 238000005056 compaction Methods 0.000 description 1
- 230000008878 coupling Effects 0.000 description 1
- 238000010168 coupling process Methods 0.000 description 1
- 238000005859 coupling reaction Methods 0.000 description 1
- 210000000805 cytoplasm Anatomy 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000004880 explosion Methods 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 239000011810 insulating material Substances 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 239000003895 organic fertilizer Substances 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 229920000915 polyvinyl chloride Polymers 0.000 description 1
- 239000004800 polyvinyl chloride Substances 0.000 description 1
- 230000008092 positive effect Effects 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 230000007306 turnover Effects 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
- C05F17/90—Apparatus therefor
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
-
- 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
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Landscapes
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Biochemistry (AREA)
- Biotechnology (AREA)
- Health & Medical Sciences (AREA)
- General Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Organic Chemistry (AREA)
- Fertilizers (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
本发明公开了一种有机固体废弃物的好氧堆肥装置和好氧堆肥方法,包括堆肥仓,还包括炉排式送料装置、螺杆挤压脱水出料装置、供氧装置、渗滤液循环喷淋装置、排气管和测温装置;炉排式送料装置和螺杆挤压脱水出料装置设置在堆肥仓内部,且炉排式送料装置位于螺杆挤压脱水出料装置的下方。本发明的好氧堆肥装置采用炉排式送料装置与螺杆挤压脱水出料装置组合的结构,层递式送料和螺杆脱水出料的组合起到了高效、良好的翻堆作用,使物料充分混合均匀并且使得物料疏松,疏松物料加速了空气中氧与底物的结合,提高了供氧效率。
The invention discloses an aerobic composting device and an aerobic composting method for organic solid waste, comprising a compost bin, a grate-type feeding device, a screw extruding dehydration discharging device, an oxygen supply device, and leachate circulation spraying Device, exhaust pipe and temperature measuring device; the grate type feeding device and the screw extrusion dehydration discharge device are arranged inside the compost bin, and the grate type feed device is located below the screw extrusion dehydration discharge device. The aerobic composting device of the present invention adopts a combination structure of a grate feeding device and a screw extruding dehydration discharging device, and the combination of layer-by-layer feeding and screw dehydration discharging plays an efficient and good composting role, so that the materials are fully mixed It is uniform and makes the material loose. The loose material accelerates the combination of oxygen in the air and the substrate, and improves the oxygen supply efficiency.
Description
技术领域technical field
本发明涉及一种用于有机固体废弃物的处理装置和方法,具体涉及一种有机固体废弃物的好氧堆肥装置和堆肥方法。The invention relates to a treatment device and method for organic solid waste, in particular to an aerobic composting device and a composting method for organic solid waste.
背景技术Background technique
有机固体废弃物包括餐厨废弃物、城市污水处理厂污泥、秸秆、园林绿化垃圾等。过去处理有机固体废弃物的主要方式是填埋和焚烧,填埋容易污染地下水,焚烧则会严重污染大气。Organic solid waste includes kitchen waste, sludge from urban sewage treatment plants, straw, landscaping waste, etc. In the past, landfill and incineration were the main ways to deal with organic solid waste. Landfill could easily pollute groundwater, while incineration would seriously pollute the atmosphere.
微生物好氧堆肥是在有氧条件下,好氧菌对废物进行吸收、氧化、分解。微生物通过自身的生命活动,把一部分被吸收的有机物氧化成简单的无机物,同时释放出可供微生物生长活动所需的能量,而另一部分有机物则被合成新的细胞质,使微生物不断生长繁殖,产生出更多生物体的过程。Microbial aerobic composting means that aerobic bacteria absorb, oxidize, and decompose waste under aerobic conditions. Through their own life activities, microorganisms oxidize part of the absorbed organic matter into simple inorganic matter, and at the same time release the energy required for the growth of microorganisms, while the other part of the organic matter is synthesized into new cytoplasm, so that the microorganisms continue to grow and reproduce. The process of producing more living organisms.
与焚烧、填埋等处理方式相比较,使用微生物好氧堆肥处理有机固体废弃物避免了二次环境污染、食品安全风险以及甲烷爆炸风险,是解决有机固体废弃物问题的清洁技术之一。此外,有机固体废弃物中大量有机质和氮、磷等元素,这些物质不仅能够为作物提供必须的营养成分,而且能有效缓解土壤板结等问题;因此将有机固体废弃物进行堆肥处理制成有机肥料,是实现生物质废弃物的减量化、资源化、无害化的有效途径。Compared with incineration, landfill and other treatment methods, the use of microbial aerobic composting to treat organic solid waste avoids secondary environmental pollution, food safety risks, and methane explosion risks, and is one of the clean technologies to solve the problem of organic solid waste. In addition, there are a lot of organic matter and nitrogen, phosphorus and other elements in organic solid waste. These substances can not only provide necessary nutrients for crops, but also effectively alleviate problems such as soil compaction; therefore, composting organic solid waste into organic fertilizers , is an effective way to realize the reduction, recycling and harmlessness of biomass waste.
中国专利文献CN 101973795 B(申请号 201010514582.7)公开了一种利用堆肥复合菌剂进行污泥好氧堆肥的方法,先将菌液扩大培养和驯化得到复合菌剂A和B,然后将复合菌剂A接入污水厂脱水污泥中,混合后堆置,在堆体表面覆盖一层复合菌剂B,继续堆置,直至堆体温度达到环境温度,即完成污泥好氧堆肥。Chinese patent document CN 101973795 B (application number 201010514582.7) discloses a method for aerobic composting of sludge by using compost compound bacterial agents. A is connected to the dewatered sludge of the sewage plant, mixed and stacked, and a layer of compound bacterial agent B is covered on the surface of the pile, and the pile is continued until the temperature of the pile reaches the ambient temperature, that is, the aerobic composting of the sludge is completed.
中国专利文献CN 103539494 B(申请号 201310506314.4)公开了一种仓式污泥好氧堆肥方法,先建立一个仓式污泥好氧堆肥装置,在发酵仓内有孔盖板上均匀铺设聚氯乙烯球型悬浮料,然后将污水处理厂的脱水污泥和锯末混匀装入发酵仓内;然后控制通风量开始堆肥过程。Chinese patent document CN 103539494 B (application number 201310506314.4) discloses a bin-type sludge aerobic composting method. First, a bin-type sludge aerobic composting device is established, and polyvinyl chloride is evenly laid on the perforated cover plate in the fermentation bin. Spherical suspension material, and then mix the dewatered sludge and sawdust from the sewage treatment plant into the fermentation bin; then control the ventilation to start the composting process.
上述两种堆肥方法均是将有机固体废弃物均静置在堆肥仓中,这种堆肥方式存在原料混合不均匀,供氧不足,氧气利用率低的问题。Both of the above two composting methods place the organic solid waste in the composting bin. This composting method has the problems of uneven mixing of raw materials, insufficient oxygen supply, and low oxygen utilization rate.
另外,作为改进的,有些好氧堆肥装置采用搅拌桨对堆体进行混合与供氧,但是这种方式在混合的过程中容易出现物料结块、混合不均匀的情况,还是存在供氧不足的问题、氧气利用率低的问题。In addition, as an improvement, some aerobic composting devices use stirring paddles to mix and supply oxygen to the compost, but this method is prone to material agglomeration and uneven mixing during the mixing process, and there is still insufficient oxygen supply problems, low oxygen utilization.
发明内容Contents of the invention
本发明所要解决的技术问题是提供一种混料均匀、供氧效率高的有机固体废弃物的好氧堆肥装置和堆肥方法。The technical problem to be solved by the present invention is to provide an aerobic composting device and composting method for organic solid waste with uniform mixing and high oxygen supply efficiency.
实现本发明第一目的的技术方案是一种有机固体废弃物的好氧堆肥装置,包括堆肥仓,还包括炉排式送料装置、螺杆挤压脱水出料装置、供氧装置、渗滤液循环喷淋装置、排气管和测温装置;炉排式送料装置和螺杆挤压脱水出料装置设置在堆肥仓内部,且炉排式送料装置位于螺杆挤压脱水出料装置的下方。The technical solution to achieve the first purpose of the present invention is an aerobic composting device for organic solid waste, including a compost bin, a grate feeding device, a screw extrusion dehydration discharging device, an oxygen supply device, and a leachate circulation spraying device. shower device, exhaust pipe and temperature measuring device; the grate type feeding device and the screw extrusion dehydration discharge device are arranged inside the compost bin, and the grate type feed device is located below the screw extrusion dehydration discharge device.
所述堆肥仓包括仓体、集料槽、渗滤液存储槽、进出料口、仓门和卸料板,集料槽和渗滤液存储槽设置在仓体的底部,渗滤液存储槽位于炉排式送料装置的下方;进出料口设置在仓体侧壁的上部,进出料口既是仓体的进料口也是仓体的出料口。The compost bin includes a bin body, a collection tank, a leachate storage tank, a material inlet and outlet, a bin door and a discharge plate. The collection tank and the leachate storage tank are arranged at the bottom of the bin body, and the leachate storage tank is located at the grate The bottom of the type feeding device; the inlet and outlet are arranged on the upper part of the side wall of the warehouse body, and the inlet and outlet are both the inlet and outlet of the warehouse body.
炉排式送料装置为往复式阶梯炉排,将物料从上向下运送至集料槽中;炉排式送料装置的炉排片呈阶梯式排布,最上端的活动炉排片位于进出料口下方,最下端的活动炉排片与集料槽连接。The grate-type feeding device is a reciprocating stepped grate, which transports the material from top to bottom into the collecting tank; the grate pieces of the grate-type feeding device are arranged in steps, and the uppermost movable grate is located below the inlet and outlet. The movable grate piece at the bottom is connected with the collecting tank.
螺杆挤压脱水出料装置包括电机、螺杆、套筒和出料导向板,螺杆和套筒倾斜设置,位于炉排式送料装置上方,螺杆和套筒的底端位于集料槽中,螺杆转动时带动集料槽中的物料由下向上输送。The screw extrusion dehydration discharge device includes a motor, a screw, a sleeve and a discharge guide plate. The screw and the sleeve are arranged obliquely and are located above the grate feeding device. The bottom ends of the screw and the sleeve are located in the collecting tank, and the screw rotates At the same time, it drives the material in the collection tank to be conveyed from bottom to top.
供氧装置包括曝气管和空气压缩机,曝气管位于渗滤液存储槽中的渗滤液中。The oxygen supply device includes an aeration pipe and an air compressor, and the aeration pipe is located in the leachate in the leachate storage tank.
渗滤液循环喷淋装置包括渗滤液排出管、循环泵、回流管、排放管和喷淋头,渗滤液排出管的进液端口与渗滤液存储槽的排液口相连通,喷淋头位于炉排式送料装置的最上端的炉排片上方;渗滤液排出管、循环泵、回流管和喷淋头依次连接。The leachate circulation spraying device includes a leachate discharge pipe, a circulation pump, a return pipe, a discharge pipe and a spray head. The liquid inlet port of the leachate discharge pipe is connected with the liquid discharge port of the leachate storage tank. The spray head is located in the furnace. Above the uppermost grate piece of the row-type feeding device; the leachate discharge pipe, the circulation pump, the return pipe and the spray head are connected in sequence.
上述仓体的外周表面设有保温层。The outer peripheral surface of the above-mentioned warehouse body is provided with an insulating layer.
上述排气管设置在仓体的顶端,测温装置水平设置在仓体的侧壁上。The above-mentioned exhaust pipe is arranged on the top of the bin body, and the temperature measuring device is arranged horizontally on the side wall of the bin body.
上述卸料板设置在进出料口的下方,卸料板与仓体可转动连接,卸料时该板撑开与螺杆挤压脱水出料装置的出料导向板连接形成斜面,进料及堆肥过程中该板靠放在仓体上。The above-mentioned unloading plate is arranged below the inlet and outlet, and the unloading plate is rotatably connected with the bin body. When unloading, the plate is stretched and connected with the discharge guide plate of the screw extrusion dehydration discharge device to form a slope, and the feeding and composting The plate rests on the bin body during the process.
进一步的,螺杆挤压脱水出料装置的出料导向板的一端转动连接在套筒的顶部端口的下方,将出料导向板的这端称作连接端,另一端称作自由端;出料导向板的自由端位于炉排式送料装置的最上端的炉排片上方,从螺杆挤压脱水出料装置输出的物料落在炉排式送料装置上;或者自由端与进出料口下方的卸料板连接组成一斜面,从螺杆挤压脱水出料装置输出的物料从仓体内输出进行卸料操作。Further, one end of the discharge guide plate of the screw extrusion dehydration discharge device is rotatably connected below the top port of the sleeve, and this end of the discharge guide plate is called the connection end, and the other end is called the free end; The free end of the guide plate is located above the uppermost grate piece of the grate feeding device, and the material output from the screw extrusion dehydration discharge device falls on the grate feeding device; or the free end and the unloading plate below the inlet and outlet The connection forms an inclined plane, and the material output from the screw extruding dehydration discharging device is output from the chamber body for unloading operation.
所述螺杆挤压脱水出料装置的套筒的筒壁上开设滤水小孔,孔径为3~5mm,相邻孔间距为20mm。The wall of the sleeve of the screw extruding dehydration discharging device is provided with small water filtering holes with a diameter of 3-5 mm and a distance between adjacent holes of 20 mm.
实现本发明第二目的的技术方案是一种如上所述的有机固体废弃物的好氧堆肥装置进行好氧堆肥的方法,包括以下步骤:The technical solution for realizing the second purpose of the present invention is a method for aerobic composting by an aerobic composting device for organic solid waste as described above, comprising the following steps:
①打开堆肥仓的仓门,启动炉排式送料装置和螺杆挤压脱水出料装置;将待处理的有机固体废弃物通入仓体内,通入的物料落在炉排式送料装置最上端的炉排片上,炉排片往复运动,将物料沿着各层的炉排片从上至下输送至集料槽内,待处理的有机固体废弃物进料完毕后关闭仓门。① Open the door of the compost bin, start the grate feeding device and the screw extrusion dehydration discharge device; pass the organic solid waste to be processed into the bin, and the incoming material falls on the furnace at the top of the grate feeding device On the grate, the grate reciprocates, and the material is transported from top to bottom along the grate of each layer to the collecting tank. After the organic solid waste to be processed is fed, the door of the bin is closed.
②螺杆挤压脱水出料装置的螺杆将集料槽内物料由下向上输送,物料在套筒内在螺杆旋转挤压下脱水,脱除的水分从套筒流出淋滤在套筒下方的炉排式送料装置上方的物料中,一部分水分留在物料中,剩余的水分汇集在渗滤液存储槽中。②The screw of the screw extrusion dehydration discharge device conveys the material in the collecting tank from bottom to top, and the material is dehydrated in the sleeve under the rotation and extrusion of the screw, and the removed water flows out from the sleeve and leaches on the grate below the sleeve In the material above the type feeding device, part of the moisture remains in the material, and the remaining moisture is collected in the leachate storage tank.
套筒中的物料从套筒顶端流出,在堆肥过程中,套筒内流出的物料又落在炉排式送料装置最上端的炉排片上。The material in the sleeve flows out from the top of the sleeve, and during the composting process, the material flowing out of the sleeve falls on the grate piece at the top of the grate feeding device.
③堆肥过程中重复上述步骤①和②,炉排式送料装置使物料从上至下层递式送料,螺杆挤压脱水出料装置将集料槽中的物料由下向上输送,物料从上至下、由下向上往复。③Repeat the above steps ① and ② during the composting process. The grate feeding device makes the materials transfer from top to bottom, and the screw extrusion dehydration and discharging device conveys the materials in the collecting tank from bottom to top, and the materials from top to bottom , Reciprocating from bottom to top.
④~天后,堆肥结束,进行卸料操作。④ After ~ days, the composting is over and the unloading operation is carried out.
处理第一批有机固体废弃物时,步骤①中向仓体内送料前,先向仓体内部输入水或有机固体废弃物的渗滤液,这些液体汇集在渗滤液存储槽中;前一批有机固体废弃物堆肥结束后渗滤液存储槽中的渗滤液保留。When processing the first batch of organic solid waste, before feeding the material into the bin in step ①, input water or leachate of organic solid waste into the bin, and these liquids are collected in the leachate storage tank; the first batch of organic solid The leachate is retained in the leachate storage tank after waste composting is complete.
步骤①中还打开供氧装置和渗滤液循环喷淋装置;渗滤液循环喷淋装置的喷淋头将液体喷淋在物料上;步骤②中供氧装置对渗滤液进行充分曝气充氧。In step ①, the oxygen supply device and leachate circulation spraying device are also turned on; the spray head of the leachate circulation spray device sprays the liquid on the material; in step ②, the oxygen supply device fully aerates and oxygenates the leachate.
每一次物料在炉排式送料装置上从上至下层递式送料的过程和螺杆挤压脱水出料装置将集料槽中的物料由下向上输送的过程耗时30~60分钟。It takes 30 to 60 minutes each time for the material to be fed from the top to the bottom on the grate feeding device and the screw extrusion dehydration and discharging device to transport the material in the collection tank from bottom to top.
本发明具有积极的效果:(1)本发明的好氧堆肥装置采用炉排式送料装置与螺杆挤压脱水出料装置组合的结构,炉排式送料装置使物料从上至下层递式送料,能使物料在送料过程中翻转分散、混合,混合过程中不会出现大面积结块的情况,而且使物料与氧气有更大的接触面积;螺杆挤压脱水出料装置将集料槽中的物料由下向上输送,在旋转螺杆的作用下物料进一步混匀和脱水;从而层递式送料和螺杆脱水出料的组合起到了高效、良好的翻堆作用,使物料充分混合均匀并且使得物料疏松,疏松物料加速了空气中氧与底物的结合,提高了供氧效率。The present invention has positive effects: (1) The aerobic composting device of the present invention adopts a combined structure of a grate-type feeding device and a screw extrusion dehydration discharging device. It can make the material turn over, disperse and mix during the feeding process, and there will be no large-area agglomeration during the mixing process, and it will make the material have a larger contact area with oxygen; The material is conveyed from bottom to top, and the material is further mixed and dehydrated under the action of the rotating screw; thus, the combination of layered feeding and screw dehydration discharge plays an efficient and good turning effect, so that the material is fully mixed and loosened , The loose material accelerates the combination of oxygen in the air and the substrate, improving the efficiency of oxygen supply.
(2)从螺杆挤压脱水出料装置输出的物料有两种情况下的出处,一是堆肥结束后物料从仓体的进出料口输出,装置的脱水功能使得出料含水率较低,螺杆出料方式使物料从出口快速排出。(2) The material output from the screw extrusion dehydration discharge device has two sources. One is that the material is output from the inlet and outlet of the bin body after the composting is completed. The dehydration function of the device makes the moisture content of the discharge material lower. The screw The discharge method enables the material to be quickly discharged from the outlet.
二是堆肥过程中物料重新落在炉排式送料装置的最上端的炉排片上,继续在仓体内进行堆肥过程。The 2nd, during the composting process, the material falls on the grate sheet at the top of the grate feeding device again, and continues to carry out the composting process in the bin body.
螺杆挤压脱水出料装置位于炉排式送料装置的上方,脱水后产生的渗滤液先淋滤在炉排式送料装置上的物料上,再下落集中在仓体底部的渗滤液存储槽。渗滤液中含有大量有益好氧菌种,淋滤过程使得这些好氧菌种与待处理的物料充分接触,起到很好的接种效果;淋滤过程也保证了物料的含水量和含氧量。The screw extrusion dehydration discharge device is located above the grate feeding device. The leachate produced after dehydration is first leached on the material on the grate feeding device, and then falls to the leachate storage tank concentrated at the bottom of the bin. The leachate contains a large number of beneficial aerobic bacteria, and the leaching process makes these aerobic bacteria fully contact with the material to be treated, which has a good inoculation effect; the leaching process also ensures the water content and oxygen content of the material .
(3)前次堆肥结束后,堆肥仓底部的渗滤液存储槽中的渗滤液保留,喷淋在新料中以调节新料的含水率,另外由于渗滤液含有大量菌种,对新料起到接种作用,大大加快后期进料的堆肥进程。(3) After the previous composting, the leachate in the leachate storage tank at the bottom of the compost bin is retained and sprayed on the new material to adjust the moisture content of the new material. In addition, because the leachate contains a large number of bacteria, it is harmful to the new material. The inoculation effect greatly speeds up the composting process of the later feeding.
渗滤液存储槽中的渗滤液中通有曝气管,对渗滤液进行充分曝气充氧,从而渗滤液中含有较充足的氧含量,促进渗滤液的好氧消化;另外,部分含氧充足的渗滤液输送到进料口喷淋在物料上时也增加了物料中的氧含量。The leachate in the leachate storage tank is connected with an aeration tube to fully aerate and oxygenate the leachate, so that the leachate contains sufficient oxygen content to promote the aerobic digestion of the leachate; in addition, part of the leachate contains sufficient oxygen When the leachate is transported to the feed port and sprayed on the material, it also increases the oxygen content in the material.
(4)本发明的装置和方法可将餐厨废弃物、城市污水处理厂污泥、秸秆、园林绿化垃圾等降解为固体有机肥,用于土壤改良。(4) The device and method of the present invention can degrade kitchen waste, sludge from urban sewage treatment plants, straw, landscaping waste, etc. into solid organic fertilizers for soil improvement.
附图说明Description of drawings
图1为本发明的好氧堆肥装置的结构示意图;Fig. 1 is the structural representation of aerobic composting device of the present invention;
图2为图1装置堆肥结束后卸料时的结构示意图;Fig. 2 is the structural representation when unloading after the composting of Fig. 1 device finishes;
上述附图中的标记如下:堆肥仓1,仓体10,集料槽11,渗滤液存储槽12,进出料口13,仓门14,卸料板15;The marks in the above drawings are as follows: compost bin 1, bin body 10, collecting tank 11, leachate storage tank 12, inlet and outlet 13, bin door 14, discharge plate 15;
炉排式送料装置2,炉排片21;Grate feeding device 2, grate piece 21;
螺杆挤压脱水出料装置3,电机31,螺杆32,套筒33,出料导向板34;Screw extrusion dehydration discharge device 3, motor 31, screw 32, sleeve 33, discharge guide plate 34;
供氧装置4,曝气管41,空气压缩机42;Oxygen supply device 4, aeration pipe 41, air compressor 42;
渗滤液循环喷淋装置5,渗滤液排出管51,循环泵52,回流管53,排放管54,喷淋头55;Leachate circulation spray device 5, leachate discharge pipe 51, circulation pump 52, return pipe 53, discharge pipe 54, spray head 55;
排气管6;Exhaust pipe 6;
测温装置7。Temperature measuring device 7.
具体实施方式detailed description
(实施例1)(Example 1)
见图1,本实施例的有机固体废弃物的好氧堆肥装置包括堆肥仓1、炉排式送料装置2、螺杆挤压脱水出料装置3、供氧装置4、渗滤液循环喷淋装置5、排气管6和测温装置7;炉排式送料装置2和螺杆挤压脱水出料装置3设置在堆肥仓1内部,且炉排式送料装置2位于螺杆挤压脱水出料装置3的下方。As shown in Figure 1, the aerobic composting device for organic solid waste in this embodiment includes a compost bin 1, a grate feeding device 2, a screw extrusion dehydration discharging device 3, an oxygen supply device 4, and a leachate circulating spray device 5 , exhaust pipe 6 and temperature measuring device 7; grate type feeding device 2 and screw extruding dehydration discharging device 3 are arranged inside compost bin 1, and grate type feeding device 2 is located at screw extruding dehydration discharging device 3 below.
所述堆肥仓1包括仓体10、集料槽11、渗滤液存储槽12、进出料口13、仓门14和卸料板15。仓体的外周表面设有保温层,例如覆盖一层保温材料。集料槽11和渗滤液存储槽12设置在仓体10的底部,集料槽11的截面为圆弧形,集料槽11和渗滤液存储槽12共用一部分槽壁。渗滤液存储槽12位于炉排式送料装置2的下方。The compost bin 1 includes a bin body 10 , a collection tank 11 , a leachate storage tank 12 , an inlet and outlet 13 , a bin door 14 and a discharge plate 15 . The outer peripheral surface of the warehouse body is provided with an insulating layer, for example covered with a layer of insulating material. The collecting tank 11 and the leachate storage tank 12 are arranged at the bottom of the bin body 10, the section of the collecting tank 11 is arc-shaped, and the collecting tank 11 and the leachate storage tank 12 share a part of the tank wall. The leachate storage tank 12 is located below the grate feeding device 2 .
进出料口13设置在仓体10侧壁的上部,进出料口13既是仓体10的进料口也是仓体10的出料口。在进出料口13的上方设有仓门14,仓门14闭合时仓体10内部是密闭空间。在进出料口13的下方还设有用于卸料的卸料板15,卸料板15与仓体10可转动连接,卸料时该板撑开(图中是撑开状态),进料及堆肥过程中该板靠放在仓体10上。The material inlet and outlet 13 is arranged on the upper part of the side wall of the bin body 10 , and the inlet and outlet 13 is not only the inlet of the bin body 10 but also the outlet of the bin body 10 . A bin door 14 is arranged above the inlet and outlet opening 13, and when the bin door 14 is closed, the interior of the bin body 10 is a closed space. Below the material inlet and outlet 13, there is also a discharge plate 15 for unloading. The discharge plate 15 is rotatably connected to the bin body 10. When unloading, the plate is stretched (the figure is a stretched state), and the feed and The board leans against the bin body 10 during the composting process.
炉排式送料装置2为往复式阶梯炉排,将物料从上向下运送至集料槽11中;包括框架(图中未画出)和炉排片;炉排片21呈阶梯式排布,包括一组固定炉排片和一组活动炉排片,最上端的活动炉排片21位于进出料口13下方,最下端的活动炉排片21与集料槽11连接。The grate feeding device 2 is a reciprocating stepped grate, which transports the material from top to bottom into the collecting tank 11; it includes a frame (not shown in the figure) and a grate piece; the grate pieces 21 are arranged in steps, including One set of fixed grate pieces and one set of movable grate pieces, the uppermost movable grate piece 21 is located below the inlet and outlet 13, and the lowermost movable fire grate piece 21 is connected with the collecting tank 11.
螺杆挤压脱水出料装置3包括电机31、螺杆32、套筒33和出料导向板34。电机31设置在仓体10外部,螺杆32、套筒33和出料导向板34设置在仓体10内部。螺杆32和套筒33倾斜设置,位于炉排式送料装置2上方。The screw extrusion dehydration discharge device 3 includes a motor 31 , a screw 32 , a sleeve 33 and a discharge guide plate 34 . The motor 31 is arranged outside the bin body 10 , and the screw rod 32 , the sleeve 33 and the discharge guide plate 34 are arranged inside the bin body 10 . The screw rod 32 and the sleeve 33 are arranged obliquely and located above the grate feeding device 2 .
电机31的电机轴通过联轴器与螺杆32连接,螺杆32位于套筒33内部中央。螺杆32和套筒33的底端位于集料槽11中,螺杆转动时带动集料槽11中的物料由下向上输送。套筒33的筒壁上开设滤水小孔,孔径为3~5mm,相邻孔间距为20mm。The motor shaft of the motor 31 is connected to the screw rod 32 through a coupling, and the screw rod 32 is located in the center of the sleeve 33 . The bottom ends of the screw rod 32 and the sleeve 33 are located in the collecting tank 11, and when the screw rotates, the materials in the collecting tank 11 are driven to be transported from bottom to top. On the cylinder wall of sleeve 33, offer water filtering aperture, aperture is 3~5mm, and the distance between adjacent holes is 20mm.
出料导向板34的一端转动连接在套筒33的顶部端口下方,将出料导向板34的这端称作连接端,另一端称作自由端。出料导向板34的自由端位于炉排式送料装置2的最上端的炉排片上方,从螺杆挤压脱水出料装置3输出的物料落在炉排式送料装置2上,在仓体10内继续堆肥过程;或者见图2,自由端与进出料口13下方的卸料板15连接组成一斜面,从螺杆挤压脱水出料装置3输出的物料从仓体10内输出,进行卸料操作。One end of the discharge guide plate 34 is rotatably connected below the top port of the sleeve 33, and this end of the discharge guide plate 34 is called the connection end, and the other end is called the free end. The free end of the discharge guide plate 34 is positioned above the uppermost grate sheet of the grate feeding device 2, and the material output from the screw extruding dehydration discharging device 3 falls on the grate feeding device 2 and continues in the bin body 10. Composting process; or see Fig. 2, free end is connected with discharge plate 15 below inlet and outlet 13 to form an inclined plane, and the material output from screw extruding dehydration discharge device 3 is output from bin body 10, carries out discharging operation.
供氧装置4包括曝气管41和空气压缩机42。曝气管41上设有曝气孔,大部分管体位于渗滤液存储槽12中的渗滤液中,小部分管体从仓体10伸出与空气压缩机42的出气口连接。The oxygen supply device 4 includes an aeration pipe 41 and an air compressor 42 . The aeration tube 41 is provided with an aeration hole, most of the tube body is located in the leachate in the leachate storage tank 12 , and a small part of the tube body protrudes from the bin body 10 to connect with the air outlet of the air compressor 42 .
渗滤液循环喷淋装置5包括渗滤液排出管51、循环泵52、回流管53、排放管54和喷淋头55。渗滤液排出管51的进液端口与渗滤液存储槽12的排液口相连通,渗滤液排出管51上设有阀门;喷淋头55位于炉排式送料装置2的最上端的炉排片上方。The leachate circulation spraying device 5 includes a leachate discharge pipe 51 , a circulation pump 52 , a return pipe 53 , a discharge pipe 54 and a spray head 55 . The liquid inlet port of the leachate discharge pipe 51 is connected with the liquid discharge port of the leachate storage tank 12, and the leachate discharge pipe 51 is provided with a valve;
渗滤液排出管51、循环泵52、回流管53和喷淋头55依次连接,将渗滤液存储槽12中的渗滤液输送至炉排式送料装置2的最上端的炉排片上方。渗滤液排出管51、循环泵52和排放管54依次连接,将渗滤液存储槽12中的渗滤液排放出去。回流管53和排放管54共用一段管道。回流管53和排放管54上均设有阀门。The leachate discharge pipe 51 , circulating pump 52 , return pipe 53 and spray head 55 are sequentially connected to transport the leachate in the leachate storage tank 12 to the uppermost grate piece of the grate feeding device 2 . The leachate discharge pipe 51 , the circulation pump 52 and the discharge pipe 54 are sequentially connected to discharge the leachate in the leachate storage tank 12 . The return pipe 53 and the discharge pipe 54 share a section of pipeline. Both the return pipe 53 and the discharge pipe 54 are provided with valves.
排气管6设置在仓体10的顶端,排气管6的进气口与仓体10顶端的出气口连接,排气管6的出气口与气体处理装置连接。本发明堆肥产生的气体以二氧化碳为主,掺杂少量硫化氢等气体,例如排气管6排出的气体可以由活性炭吸附后放空。The exhaust pipe 6 is arranged on the top of the warehouse body 10, the air inlet of the exhaust pipe 6 is connected with the gas outlet at the top of the warehouse body 10, and the gas outlet of the exhaust pipe 6 is connected with the gas treatment device. The gas produced by the composting of the present invention is mainly carbon dioxide, mixed with a small amount of hydrogen sulfide and other gases. For example, the gas discharged from the exhaust pipe 6 can be emptied after being adsorbed by activated carbon.
测温装置7水平设置在仓体10的侧壁上,位于炉排式送料装置2的下方。测温装置7的温度传感端位于仓体10内部。The temperature measuring device 7 is horizontally arranged on the side wall of the bin body 10 and is located below the grate feeding device 2 . The temperature sensing end of the temperature measuring device 7 is located inside the chamber body 10 .
使用上述好氧堆肥装置对有机固体废弃物进行好氧堆肥时,包括以下步骤:When using the above-mentioned aerobic composting device to perform aerobic composting of organic solid waste, the following steps are included:
①打开堆肥仓1的仓门14,先向仓体10内部输入水或有机固体废弃物的渗滤液,这些液体汇集在渗滤液存储槽12中。① Open the bin door 14 of the compost bin 1, and first input water or leachate of organic solid waste into the bin body 10, and these liquids are collected in the leachate storage tank 12.
启动炉排式送料装置2、螺杆挤压脱水出料装置3、供氧装置4和渗滤液循环喷淋装置5;将待处理的含水率为30%±5%的有机固体废弃物从进出料口13通入仓体10内,通入的物料落在炉排式送料装置2最上端的炉排片上,渗滤液循环喷淋装置5的喷淋头55将液体喷淋在物料上,使得物料含水率为40%~60%。炉排片往复运动,将物料沿着各层的炉排片从上至下输送至集料槽11内。待处理的有机固体废弃物进料完毕后关闭仓门14。Start the grate feeding device 2, the screw extrusion dehydration discharge device 3, the oxygen supply device 4 and the leachate circulation spray device 5; the organic solid waste to be treated with a moisture content of 30%±5% is discharged from the inlet and outlet The mouth 13 leads into the bin body 10, and the material passed in falls on the grate sheet at the top of the grate feeding device 2, and the spray head 55 of the leachate circulating spray device 5 sprays the liquid on the material, so that the material contains water The rate is 40% to 60%. The grate pieces reciprocate, and the materials are transported into the collecting tank 11 from top to bottom along the grate pieces of each layer. Close the bin door 14 after the organic solid waste to be processed is fed.
②螺杆挤压脱水出料装置3的螺杆32将集料槽11内物料由下向上输送,物料在套筒33内在螺杆旋转挤压下脱水,脱除的水分从套筒33上的小孔中流出淋滤在套筒33下方的炉排式送料装置2上方的物料中,一部分水分留在物料中,剩余的水分汇集在渗滤液存储槽12中。②The screw 32 of the screw extrusion dehydration discharge device 3 conveys the material in the collecting tank 11 from bottom to top, and the material is dehydrated in the sleeve 33 under the rotation and extrusion of the screw, and the removed moisture is released from the small hole on the sleeve 33 Out of the material above the grate feeding device 2 below the sleeve 33 , part of the moisture remains in the material, and the remaining moisture is collected in the leachate storage tank 12 .
供氧装置4对渗滤液进行充分曝气充氧,这样渗滤液含有较充足的氧含量,促进渗滤液的好氧消化。The oxygen supply device 4 fully aerates and oxygenates the leachate, so that the leachate contains sufficient oxygen content and promotes the aerobic digestion of the leachate.
套筒33中的物料从套筒顶端流出,在堆肥过程中,套筒33内流出的物料又落在炉排式送料装置2最上端的炉排片上。The material in the sleeve 33 flows out from the sleeve top, and during the composting process, the material flowing out in the sleeve 33 falls on the grate sheet at the top of the grate feeding device 2 again.
③堆肥过程中重复上述步骤①和②,炉排式送料装置2使物料从上至下层递式送料,螺杆挤压脱水出料装置3将集料槽中的物料由下向上输送,物料从上至下、由下向上往复;每一次物料由炉排式送料装置2从上至下层递式送料的过程和螺杆挤压脱水出料装置3将集料槽中的物料由下向上输送的过程耗时30~60分钟。③ Repeat the above steps ① and ② during the composting process. The grate type feeding device 2 makes the material transfer from the top to the bottom layer, and the screw extrusion dehydration discharge device 3 conveys the material in the collecting tank from the bottom to the top, and the material from the top to the bottom, reciprocating from bottom to top; every time the material is fed from the top to the bottom by the grate feeding device 2 and the process of conveying the material in the collecting tank from the bottom to the top by the screw extrusion dehydration discharge device 3 consumes 30-60 minutes.
堆肥过程中仓体10内温度控制在40℃~45℃,若测温装置7测得仓体10内温度高于45℃,提高供氧装置4向仓体10的进气量,若仓体10内温度低于40℃,则由供氧装置4向仓体10内鼓入热空气。During the composting process, the temperature in the bin body 10 is controlled at 40°C to 45°C. If the temperature in the bin body 10 measured by the temperature measuring device 7 is higher than 45°C, increase the air intake from the oxygen supply device 4 to the bin body 10. If the bin body If the temperature in the chamber 10 is lower than 40° C., hot air is blown into the chamber body 10 by the oxygen supply device 4 .
堆肥过程中产生的气体由排气管6排出,经活性炭吸附后排空。The gas produced in the composting process is discharged through the exhaust pipe 6, and is emptied after being adsorbed by activated carbon.
④15~20天后,堆肥结束,关闭炉排式送料装置2,打开仓门14,使螺杆挤压脱水出料装置3的出料导向板34的自由端与进出料口13下方的卸料板15连接组成一斜面,从螺杆挤压脱水出料装置3输出的物料从仓体10内输出,进行卸料操作。堆肥结束得到固体有机肥,含水率为25%~30%。④ After 15 to 20 days, the composting is finished, close the grate feeding device 2, open the door 14, and make the free end of the discharge guide plate 34 of the screw extrusion dehydration discharge device 3 and the discharge plate 15 below the inlet and outlet 13 The connection forms an inclined plane, and the material output from the screw extruding dehydration discharging device 3 is output from the bin body 10 for unloading operation. After composting, solid organic fertilizer is obtained with a moisture content of 25% to 30%.
⑤前一批有机固体废弃物处理完毕排空后,向仓体10内输入后一批待处理的废弃物。前一次堆肥过程中堆肥仓底部的渗滤液存储槽中的渗滤液保留,用于喷淋在后一批新料中以调节新料的含水率,另外由于渗滤液含有大量菌种,对新料起到接种作用,大大加快后期进料的堆肥进程。⑤ After the previous batch of organic solid wastes are processed and emptied, the next batch of wastes to be processed is input into the bin body 10 . During the previous composting process, the leachate in the leachate storage tank at the bottom of the compost bin was reserved for spraying in the next batch of new materials to adjust the moisture content of the new materials. In addition, because the leachate contains a large number of bacteria, it is harmful to the new materials. It plays the role of inoculation and greatly speeds up the composting process of later feeding.
若渗滤液存储槽中的渗滤液过量,打开渗滤液循环喷淋装置5的排放管54上的阀If the leachate in the leachate storage tank is excessive, open the valve on the discharge pipe 54 of the leachate circulation spraying device 5
门,放出部分渗滤液。door, release part of the leachate.
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201610455168.0A CN106116734B (en) | 2016-06-21 | 2016-06-21 | Aerobic composting device and aerobic composting method for organic solid waste |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201610455168.0A CN106116734B (en) | 2016-06-21 | 2016-06-21 | Aerobic composting device and aerobic composting method for organic solid waste |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN106116734A true CN106116734A (en) | 2016-11-16 |
| CN106116734B CN106116734B (en) | 2021-11-16 |
Family
ID=57268449
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201610455168.0A Active CN106116734B (en) | 2016-06-21 | 2016-06-21 | Aerobic composting device and aerobic composting method for organic solid waste |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN106116734B (en) |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107382385A (en) * | 2017-08-30 | 2017-11-24 | 山东农业大学 | Intelligent sunlight garbage compost room |
| CN107954766A (en) * | 2017-12-18 | 2018-04-24 | 朱兆明 | A kind of natural organic fertilizer preparation system and its method of work |
| CN109704827A (en) * | 2019-02-03 | 2019-05-03 | 王英宾 | It can rotten organic solid waste fast degradation method |
| CN110590415A (en) * | 2019-10-14 | 2019-12-20 | 张俊杰 | Deodorizing device for composting fermentation of food waste |
| CN112358340A (en) * | 2020-11-26 | 2021-02-12 | 湖北同晟生物能源科技有限公司 | Organic solid waste's good oxygen composting device convenient to clearance |
| CN112608204A (en) * | 2021-01-13 | 2021-04-06 | 张占淼 | Suspension type chicken manure fertilizer processingequipment |
Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20040206698A1 (en) * | 2001-08-29 | 2004-10-21 | Chang Ho Nam | On-site treatment method of food waste generated from collective residence or institutional food service facilities |
| CN102219569A (en) * | 2011-03-25 | 2011-10-19 | 浙江工商大学 | Decentralized treatment system and treatment method for rural domestic refuse |
| WO2013173567A1 (en) * | 2012-05-17 | 2013-11-21 | Shell Oil Company | Methods and systems for processing biomass material |
| CN104211460A (en) * | 2014-08-29 | 2014-12-17 | 南开大学 | Fast aerobic composting reaction device and application thereof |
| CN104690017A (en) * | 2015-02-09 | 2015-06-10 | 大连泰达环保有限公司 | Novel multi-stage treatment process for leaching and compressing household garbage |
| CN205774176U (en) * | 2016-06-21 | 2016-12-07 | 江苏理工学院 | Aerobic composting device for organic solid waste |
-
2016
- 2016-06-21 CN CN201610455168.0A patent/CN106116734B/en active Active
Patent Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20040206698A1 (en) * | 2001-08-29 | 2004-10-21 | Chang Ho Nam | On-site treatment method of food waste generated from collective residence or institutional food service facilities |
| CN102219569A (en) * | 2011-03-25 | 2011-10-19 | 浙江工商大学 | Decentralized treatment system and treatment method for rural domestic refuse |
| WO2013173567A1 (en) * | 2012-05-17 | 2013-11-21 | Shell Oil Company | Methods and systems for processing biomass material |
| CN104211460A (en) * | 2014-08-29 | 2014-12-17 | 南开大学 | Fast aerobic composting reaction device and application thereof |
| CN104690017A (en) * | 2015-02-09 | 2015-06-10 | 大连泰达环保有限公司 | Novel multi-stage treatment process for leaching and compressing household garbage |
| CN205774176U (en) * | 2016-06-21 | 2016-12-07 | 江苏理工学院 | Aerobic composting device for organic solid waste |
Non-Patent Citations (2)
| Title |
|---|
| ASHOKE DAVID MALIKI,ETAL: "Design and application of a pre-composting test step to determine the effect of high fat food wastes on an industrial scale in-vessel composting system", 《INTERNATIONAL BIODETERIORATION & BIODEGRADATION》 * |
| 郭伟: "城市垃圾处理方法的研究", 《科技信息》 * |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107382385A (en) * | 2017-08-30 | 2017-11-24 | 山东农业大学 | Intelligent sunlight garbage compost room |
| CN107954766A (en) * | 2017-12-18 | 2018-04-24 | 朱兆明 | A kind of natural organic fertilizer preparation system and its method of work |
| CN109704827A (en) * | 2019-02-03 | 2019-05-03 | 王英宾 | It can rotten organic solid waste fast degradation method |
| CN110590415A (en) * | 2019-10-14 | 2019-12-20 | 张俊杰 | Deodorizing device for composting fermentation of food waste |
| CN112358340A (en) * | 2020-11-26 | 2021-02-12 | 湖北同晟生物能源科技有限公司 | Organic solid waste's good oxygen composting device convenient to clearance |
| CN112608204A (en) * | 2021-01-13 | 2021-04-06 | 张占淼 | Suspension type chicken manure fertilizer processingequipment |
Also Published As
| Publication number | Publication date |
|---|---|
| CN106116734B (en) | 2021-11-16 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN106116734B (en) | Aerobic composting device and aerobic composting method for organic solid waste | |
| CN204454910U (en) | Fruits and vegetables class organic garbage disposal | |
| CN111333440B (en) | Vehicle-mounted organic garbage rapid decomposition and fertilization system and method | |
| CN102557368A (en) | High-temperature aerobic composting treatment process for municipal sludge | |
| CN203999292U (en) | A kind of device of intelligent high-temperature aerobic fermentation sludge treatment | |
| CN107021794A (en) | A kind of composting high-efficiency aerobic composting device and method | |
| CN204265656U (en) | Intelligence high-temperature environmental-protection composting all-in-one | |
| CN111454086B (en) | A rail car type anaerobic-aerobic combined fermentation and composting device | |
| CN202482231U (en) | Device for preparing fertilizer by aerobic fermentation of organic solid waste | |
| CN103922816A (en) | Bio-drying system and method for excrement in livestock farm | |
| CN103626538B (en) | Trench type composting method for treating breeding sewage and solid wastes simultaneously | |
| CN207175805U (en) | A kind of composting high-efficiency aerobic composting device | |
| CN118561633B (en) | Environment-friendly aerobic composting device and aerobic composting method | |
| CN102515886B (en) | Process for producing biological bacterial fertilizer by taking domestic sewage plant dewatered sludge as raw material | |
| CN109265206A (en) | Device and method for reducing nitrogen dioxide release in solid waste composting process by utilizing decomposed sludge | |
| CN102976809B (en) | Planetary type full-automatic sludge aerobic fermentation device and system | |
| CN204162624U (en) | A kind of unpowered self ventilated type aerobic composting device | |
| CN102303988A (en) | Method for preparing garden and park nutrient soil by adopting dewatered sludge through fermentation | |
| CN205774176U (en) | Aerobic composting device for organic solid waste | |
| CN213623900U (en) | Kitchen waste aerobic composting equipment | |
| CN204644363U (en) | A kind of integrated form biomass waste associating two-phase dry-type anaerobic fermentation device | |
| CN107827509A (en) | It is a kind of to consolidate the integrated production facility of solution fertilizer and production method | |
| CN207086545U (en) | A kind of house refuse is reduced recycling buried type integrated device | |
| CN216472958U (en) | An integrated device for efficient treatment of kitchen waste | |
| CN110104898A (en) | A kind of rubbish anaerobism, aerobic compost, purification of waste water processing system |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| CB02 | Change of applicant information |
Address after: No. 1801 Zhong Wu Avenue, Changzhou, Jiangsu Province, Jiangsu Applicant after: Jiangsu University of Technology Address before: 213001 1801 Zhong Wu Avenue, Zhong Lou District, Changzhou, Jiangsu Applicant before: Jiangsu University of Technology |
|
| CB02 | Change of applicant information | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant |