CN105948832B - A kind of small-sized kitchen garbage installation for fermenting - Google Patents

A kind of small-sized kitchen garbage installation for fermenting Download PDF

Info

Publication number
CN105948832B
CN105948832B CN201610266733.9A CN201610266733A CN105948832B CN 105948832 B CN105948832 B CN 105948832B CN 201610266733 A CN201610266733 A CN 201610266733A CN 105948832 B CN105948832 B CN 105948832B
Authority
CN
China
Prior art keywords
tank
anaerobic fermentation
stack retting
aerobic
positions
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.)
Expired - Fee Related
Application number
CN201610266733.9A
Other languages
Chinese (zh)
Other versions
CN105948832A (en
Inventor
吴川福
李悦宁
黄琪琪
杨民
汪群慧
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
University of Science and Technology Beijing USTB
Original Assignee
University of Science and Technology Beijing USTB
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by University of Science and Technology Beijing USTB filed Critical University of Science and Technology Beijing USTB
Priority to CN201610266733.9A priority Critical patent/CN105948832B/en
Publication of CN105948832A publication Critical patent/CN105948832A/en
Application granted granted Critical
Publication of CN105948832B publication Critical patent/CN105948832B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F9/00Fertilisers from household or town refuse
    • C05F9/02Apparatus for the manufacture
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F9/00Fertilisers from household or town refuse
    • C05F9/04Biological compost
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Manufacturing & Machinery (AREA)
  • Health & Medical Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Molecular Biology (AREA)
  • Processing Of Solid Wastes (AREA)
  • Fertilizers (AREA)

Abstract

本发明提供一种小型餐厨垃圾发酵装置,属于废弃物资源化领域。该装置包括进料系统、好氧堆肥系统,厌氧发酵系统和除臭系统,好氧堆肥系统包含六个堆沤槽,连接成环状,包裹着装置中心的厌氧发酵罐。当堆沤槽中餐厨垃圾填满后,堆沤槽转动至另一个空槽,以承接来自进料系统的餐厨垃圾。环状堆沤槽中特定位置配有喷淋和通气装置,以保证堆肥化的有效进行。经堆沤的餐厨垃圾进入厌氧发酵罐进行产甲烷发酵。发酵罐所产沼气用沼气袋收集后可作为家用燃气。发酵罐所产沼液和沼渣排入化粪池。本装置具有结构简单,环境污染小,废物资源化利用等优点,尤其适用于家庭或住宅小区所产餐厨垃圾的处理。

The invention provides a small kitchen garbage fermentation device, which belongs to the field of waste recycling. The device includes a feed system, an aerobic composting system, an anaerobic fermentation system and a deodorization system. The aerobic composting system includes six composting tanks connected in a ring and wrapping the anaerobic fermentation tank in the center of the device. When the food waste in the retting tank is full, the retting tank turns to another empty tank to receive the food waste from the feeding system. Specific positions in the ring-shaped retting tank are equipped with spraying and aeration devices to ensure effective composting. The composted food waste enters the anaerobic fermentation tank for methane fermentation. The biogas produced by the fermentation tank can be used as domestic gas after being collected with a biogas bag. The biogas slurry and biogas residue produced by the fermentation tank are discharged into the septic tank. The device has the advantages of simple structure, little environmental pollution, resource utilization of waste, etc., and is especially suitable for the treatment of kitchen waste produced by families or residential quarters.

Description

一种小型餐厨垃圾发酵装置A small food waste fermentation device

技术领域technical field

本发明涉及废弃物资源化领域,特别是指一种小型餐厨垃圾发酵装置。The invention relates to the field of waste recycling, in particular to a small kitchen waste fermentation device.

背景技术Background technique

餐厨垃圾是城市垃圾的主要组成部分,具有高油脂(5%~20%)、高盐分(湿基:0.8%~1.5%)、高水分(70%~90%)、高有机含量(干基:90%以上)以及易腐发臭、易酸化、易生物降解等特点。目前,城市居民家庭所产餐厨垃圾或直接抛弃、或经破碎后排入市政污水管网。此做法会增加填埋场气体和渗滤液的产生量,增加垃圾填埋场和城市污水厂负荷,造成二次污染防治费用大量增加。此外,餐厨垃圾中的高盐分将限制其作为堆肥产品长期使用于土壤。Food waste is the main component of urban waste, with high oil (5% to 20%), high salt (wet basis: 0.8% to 1.5%), high moisture (70% to 90%), high organic content (dry Base: more than 90%) and perishable odor, easy acidification, easy biodegradation and other characteristics. At present, the kitchen waste produced by urban households is either directly discarded, or discharged into the municipal sewage pipe network after being crushed. This approach will increase the production of landfill gas and leachate, increase the load on landfills and urban sewage plants, and cause a substantial increase in the cost of secondary pollution prevention and control. Furthermore, the high salinity in food waste will limit its long-term use in soil as a compost product.

餐厨垃圾中营养丰富,所含的微量元素等也比较适合微生物的生长需求,故适合于生物处理。而厌氧产甲烷技术具有对发酵物料的适应范围广(可降解复杂的底物成分)、目标产物(沼气)易分离、易于工程应用的特点,是目前最具潜力的有机废物资源化技术。Food waste is rich in nutrients and contains trace elements that are more suitable for the growth needs of microorganisms, so it is suitable for biological treatment. The anaerobic methanogenesis technology has the characteristics of wide adaptability to fermentation materials (degradable complex substrate components), easy separation of target products (biogas), and easy engineering application. It is currently the most potential organic waste recycling technology.

本发明提供一种结构简单,易操作,环境污染小,且可实现餐厨垃圾资源化的小型发酵装置,可应用于家庭或住宅小区所产餐厨垃圾的处理。The invention provides a small-scale fermentation device with simple structure, easy operation, less environmental pollution, and can realize the recycling of food waste, which can be applied to the treatment of food waste produced in families or residential quarters.

发明内容Contents of the invention

本发明要解决的技术问题是提供一种小型餐厨垃圾发酵装置。The technical problem to be solved by the present invention is to provide a small kitchen waste fermentation device.

该装置包括进料系统、好氧堆肥系统、厌氧发酵系统和除臭系统;The device includes feeding system, aerobic composting system, anaerobic fermentation system and deodorization system;

其中,进料系统位于餐厨垃圾发酵装置上部,进料系统包括水池、垃圾处理器进料口和垃圾处理器;好氧堆肥系统包含体积相同的六个好氧堆沤槽,六个好氧堆沤槽呈环状连接,六个好氧堆沤槽分别位于一号位、二号位、三号位、四号位、五号位和六号位;六个好氧堆沤槽之间有隔板,六个好氧堆沤槽由电机带动旋转;二号位、三号位、四号位和五号位堆沤槽通过铺设在底部的空气管道进行通气;堆沤槽所产臭气由臭气集气罩收集后,经臭气管道输送至除臭系统脱臭后排放;二号位、三号位、四号位、五号位和六号位堆沤槽顶部设有发酵液喷淋装置;垃圾处理器出口连接堆沤槽一号位的好氧堆沤槽进料口;堆沤槽一号位所产发酵液经底部发酵液排放管排入餐厨垃圾发酵装置底部的发酵液收集槽,发酵液收集槽内发酵液经发酵液喷淋管道和发酵液喷淋装置回喷至堆沤槽;堆沤槽六号位底部设有厌氧发酵罐进料口;Among them, the feeding system is located on the upper part of the food waste fermentation device, and the feeding system includes a water tank, a garbage processor inlet and a garbage processor; the aerobic composting system includes six aerobic composting tanks with the same volume, six aerobic The stacking retting tanks are connected in a ring shape, and the six aerobic stacking tanks are respectively located at No. 1, No. 2, No. 3, No. 4, No. 5 and No. 6 positions; between the six aerobic retting tanks There are partitions, and the six aerobic retting tanks are rotated by motors; the retting tanks at positions 2, 3, 4 and 5 are ventilated through the air pipes laid at the bottom; the odor produced by the retting tanks After the gas is collected by the odor gas collection hood, it is transported to the deodorization system through the odor pipeline for deodorization and then discharged; the top of the retting tanks at No. 2, No. 3, No. 4, No. 5 and No. 6 positions Spray device; the outlet of the garbage processor is connected to the feed port of the aerobic retting tank at the No. 1 stacking tank; the fermentation liquid produced at the No. 1 stacking tank is discharged into the bottom of the food waste fermentation device Fermentation liquid collection tank, the fermentation liquid in the fermentation liquid collection tank is sprayed back to the stacking retting tank through the fermentation liquid spraying pipeline and fermentation liquid spraying device; the bottom of the sixth position of the stacking retting tank is provided with an anaerobic fermentation tank feed port;

厌氧发酵系统中厌氧发酵罐内有搅拌器,由电机驱动;当厌氧发酵罐进料口开启时,搅拌器启动;当厌氧发酵罐进料口关闭时,搅拌器每天开启2次,每次3分钟;厌氧发酵罐所产沼气经沼气排放口和沼气管道进入沼气集气袋供燃气炉使用;厌氧发酵罐所产沼液沼渣经沼液沼渣排放口和沼液沼渣管道排入化粪池。In the anaerobic fermentation system, there is an agitator in the anaerobic fermentation tank, which is driven by a motor; when the inlet of the anaerobic fermentation tank is opened, the agitator is started; when the inlet of the anaerobic fermentation tank is closed, the agitator is started twice a day , 3 minutes each time; the biogas produced by the anaerobic fermentation tank enters the biogas collection bag through the biogas outlet and the biogas pipeline for use by the gas furnace; the biogas slurry and residue produced by the anaerobic fermentation tank pass through the biogas slurry outlet and The biogas residue is piped into the septic tank.

好氧堆肥系统和厌氧发酵系统密封于同一箱体内,箱体外壁和箱体内壁间设有保温材料,其中,保温材料的导热系数低于0.0005kW/(m2·℃)。The aerobic composting system and the anaerobic fermentation system are sealed in the same box, and an insulating material is provided between the outer wall of the box and the inner wall of the box, wherein the thermal conductivity of the insulating material is lower than 0.0005kW/(m 2 ·℃).

垃圾处理器用于破碎餐厨垃圾,垃圾处理器内还可以投加复合微生物菌剂,菌剂投加比例为餐厨垃圾干重的0.5%-1%。The garbage disposer is used to shred food waste, and a compound microbial agent can also be added to the garbage disposer. The dosage of the agent is 0.5%-1% of the dry weight of the food waste.

六个好氧堆沤槽每1-2天旋转60度;餐厨垃圾在每个堆沤槽内停留时间为5-14天。二号位、三号位、四号位和五号位堆沤槽每天通气速率为10-25L-空气/kg-有机物/d;二号位、三号位、四号位、五号位和六号位堆沤槽内有机物通过喷淋发酵液调节含水率,使其中的含水率不低于60%。The six aerobic retting tanks rotate 60 degrees every 1-2 days; food waste stays in each retting tank for 5-14 days. No. 2, No. 3, No. 4 and No. 5 stacking tanks have a daily ventilation rate of 10-25L-air/kg-organic matter/d; No. 2, No. 3, No. 4, No. 5 and The organic matter in the No. 6 retting tank is adjusted by spraying the fermentation liquid so that the moisture content is not lower than 60%.

厌氧发酵罐被六个好氧堆沤槽紧密环绕;厌氧发酵罐与六个好氧堆沤槽间隔板的导热系数为100-250kW/(m2·℃)。厌氧发酵罐内餐厨垃圾水力停留时间为15-30天。单个好氧堆沤槽与厌氧发酵罐的体积比为1:20-1:40。The anaerobic fermentation tank is closely surrounded by six aerobic retting tanks; the thermal conductivity of the spacer between the anaerobic fermentation tank and the six aerobic retting tanks is 100-250kW/(m 2 ·℃). The hydraulic retention time of food waste in the anaerobic fermentation tank is 15-30 days. The volume ratio of a single aerobic retting tank to anaerobic fermentation tank is 1:20-1:40.

厌氧发酵罐内接种经驯化的厌氧消化污泥。The acclimatized anaerobic digested sludge was inoculated in the anaerobic fermentation tank.

除臭系统中的除臭装置为生物脱臭装置或物化脱臭装置。The deodorization device in the deodorization system is a biological deodorization device or a physical and chemical deodorization device.

本发明的上述技术方案的有益效果如下:The beneficial effects of above-mentioned technical scheme of the present invention are as follows:

(1)本发明可减少由餐厨垃圾堆放所产生的臭气和废液量,改善环境卫生,减少餐厨垃圾收运难度和成本;(1) The present invention can reduce the amount of odor and waste liquid generated by the stacking of kitchen waste, improve environmental sanitation, and reduce the difficulty and cost of collecting and transporting kitchen waste;

(2)本装置回收有机废物好氧堆肥过程所产热量,可提高餐厨厌氧发酵系统的产气速率;(2) The device recycles the heat generated during the aerobic composting process of organic waste, which can increase the gas production rate of the anaerobic fermentation system in the kitchen;

(3)本装置中餐厨垃圾预先经过好氧堆沤降解部分易降解有机物,有利于避免厌氧发酵过程中的酸化现象,提高厌氧发酵系统稳定性;(3) The food waste in this device is degraded by aerobic retting in advance and part of the easily degradable organic matter is beneficial to avoid acidification in the anaerobic fermentation process and improve the stability of the anaerobic fermentation system;

(4)本装置运行费用低,耗水量少,同时可回收沼气能源;(4) The operating cost of the device is low, the water consumption is small, and biogas energy can be recovered at the same time;

(5)本装置处理餐厨垃圾过程中臭气产生量少,沼液沼渣可直接排入化粪池,有利于进一步回收化粪池中的生物质能源。(5) The device produces less odor during the process of treating kitchen waste, and the biogas slurry and residue can be directly discharged into the septic tank, which is conducive to the further recovery of biomass energy in the septic tank.

附图说明Description of drawings

图1为本发明的一种小型餐厨垃圾发酵装置结构示意图;Fig. 1 is the structural representation of a kind of small kitchen waste fermentation device of the present invention;

图2为本发明的一种小型餐厨垃圾发酵装置的俯视图。Fig. 2 is a top view of a small-scale food waste fermentation device of the present invention.

其中:1-水池;2-垃圾处理器进料口;3-垃圾处理器;4-好氧堆沤槽进料口;5-一号位;6-二号位;7-三号位;8-四号位;9-五号位;10-六号位;11-隔板;12-箱体外壁;13-箱体内壁;14-厌氧发酵罐;15-搅拌器;16-电机;17-发酵液收集槽;18-发酵液喷淋管道;19-发酵液喷淋装置;20-沼液沼渣排放口;21-沼气排放口;22-沼气管道;23-沼气集气袋;24-燃气炉;25-厌氧发酵罐进料口;26-空气管道;27-沼液沼渣管道;28-臭气集气罩;29-臭气管道;30-发酵液排放管。Among them: 1-water pool; 2-garbage processor inlet; 3-garbage processor; 4-aerobic retting tank inlet; 5-position one; 6-position two; 7-position three; 8-position four; 9-position five; 10-position six; 11-partition; 12-outer wall of the box; 13-inner wall of the box; 14-anaerobic fermentation tank; 15-stirrer; 16-motor ;17-fermentation liquid collection tank; 18-fermentation liquid spray pipe; 19-fermentation liquid spray device; 20-biogas slurry and residue discharge port; 21-biogas discharge port; 22-biogas pipeline; 23-biogas collection bag ; 24- gas furnace; 25- anaerobic fermentation tank feed port; 26- air pipeline; 27- biogas slurry and residue pipeline; 28- odor gas collection hood;

具体实施方式Detailed ways

为使本发明要解决的技术问题、技术方案和优点更加清楚,下面将结合附图及具体实施例进行详细描述。In order to make the technical problems, technical solutions and advantages to be solved by the present invention clearer, the following will describe in detail with reference to the drawings and specific embodiments.

本发明提供一种小型餐厨垃圾发酵装置。The invention provides a small kitchen waste fermentation device.

如图1和图2所示,图1为该装置结构示意图,同时也是图2中A-A剖面结构示意图。该装置分为进料系统、好氧堆肥系统、厌氧发酵系统和除臭系统;其中,进料系统包括水池1、垃圾处理器进料口2、垃圾处理器3;好氧堆肥系统包含体积相同的六个好氧堆沤槽,呈环状连接,六个好氧堆沤槽分别位于一号位5、二号位6、三号位7、四号位8、五号位9和六号位10;六个好氧堆沤槽间有隔板11,可由电机16带动旋转;二号位6、三号位7、四号位8和五号位9堆沤槽可通过铺设在底部的空气管道26进行通气;堆沤槽所产臭气由臭气集气罩28收集后,经臭气管道29输送至除臭系统脱臭后排放;二号位6、三号位7、四号位8、五号位9和六号位10堆沤槽顶部设有发酵液喷淋装置19;垃圾处理器3出口连接堆沤槽一号位5的好氧堆沤槽进料口4;堆沤槽一号位5所产发酵液经底部发酵液排放管30排入发酵液收集槽17,槽内发酵液经发酵液喷淋管道18和发酵液喷淋装置19回喷至相应堆沤槽;堆沤槽六号位10底部设有厌氧发酵罐进料口25;As shown in Figures 1 and 2, Figure 1 is a schematic structural diagram of the device, and is also a schematic structural schematic diagram of the A-A section in Figure 2 . The device is divided into feeding system, aerobic composting system, anaerobic fermentation system and deodorization system; among them, the feeding system includes pool 1, garbage processor inlet 2, garbage processor 3; the aerobic composting system contains volume The same six aerobic retting tanks are connected in a ring, and the six aerobic retting tanks are respectively located at the first position 5, the second position 6, the third position 7, the fourth position 8, the fifth position 9 and the sixth position. No. 10; there are partitions 11 between the six aerobic retting tanks, which can be driven by a motor 16 to rotate; No. 2 position 6, No. 3 position 7, No. 4 position 8 and No. Air pipe 26 for ventilation; the odor produced by the retting tank is collected by the odor gas collection hood 28, and then sent to the deodorization system through the odor pipeline 29 for deodorization; the second position 6, the third position 7, and the fourth position The top of the retting tank at position 8, position 9 at position 5 and position 10 at position 6 is provided with a fermentation liquid spraying device 19; the outlet of garbage disposer 3 is connected to the feed port 4 of the aerobic retting tank at position 5 of the first position of the retting tank; The fermented liquid produced at No. 5 of the retting tank is discharged into the fermented liquid collection tank 17 through the bottom fermented liquid discharge pipe 30, and the fermented liquid in the tank is sprayed back to the corresponding stacking retting tank through the fermented liquid spraying pipeline 18 and the fermented liquid spraying device 19 ; The bottom of No. 6 position 10 of the retting tank is provided with an anaerobic fermentation tank feed port 25;

厌氧发酵系统中厌氧发酵罐14内有搅拌器15,由电机16驱动;当厌氧发酵罐进料口25开启时,搅拌器15启动;当厌氧发酵罐进料口25关闭时,搅拌器15每天开启2次,每次3分钟;厌氧发酵罐14所产沼气经沼气排放口21和沼气管道22进入沼气集气袋23供燃气炉24使用;厌氧发酵罐14所产沼液沼渣经沼液沼渣排放口20和沼液沼渣管道27排入化粪池;本餐厨垃圾发酵装置中好氧堆肥系统和厌氧发酵系统密封于同一箱体内,箱体外壁12和箱体内壁13间设有保温材料。In the anaerobic fermentation system, there is an agitator 15 in the anaerobic fermentation tank 14, which is driven by a motor 16; when the feed port 25 of the anaerobic fermentation tank is opened, the agitator 15 starts; when the feed port 25 of the anaerobic fermentation tank is closed, The agitator 15 is turned on twice a day for 3 minutes each time; the biogas produced by the anaerobic fermentation tank 14 enters the biogas collection bag 23 through the biogas discharge port 21 and the biogas pipeline 22 for use by the gas furnace 24; the biogas produced by the anaerobic fermentation tank 14 The liquid biogas residue is discharged into the septic tank through the biogas slurry and biogas residue discharge port 20 and the biogas slurry and biogas residue pipeline 27; the aerobic composting system and the anaerobic fermentation system in this food waste fermentation device are sealed in the same box, and the outer wall of the box is 12 Insulation material is provided between and casing inner wall 13.

进料系统位于餐厨垃圾发酵装置上部;发酵液收集槽17位于餐厨垃圾发酵装置底部;垃圾处理器3除破碎餐厨垃圾功能外还可在此投加复合微生物菌剂;厌氧发酵罐14内接种经驯化的厌氧消化污泥。The feeding system is located on the upper part of the food waste fermentation device; the fermentation liquid collection tank 17 is located at the bottom of the food waste fermentation device; the garbage processor 3 can also add compound microbial agents here in addition to the function of crushing food waste; anaerobic fermentation tank The acclimatized anaerobic digested sludge was inoculated within 14 days.

实施例1Example 1

采用上述装置对家庭所产餐厨垃圾进行处理。发酵装置箱体外壁12导热系数为0.00048kW/(m2·℃)。装置每日处理餐厨垃圾量约为2kg。垃圾与复合菌剂(投加量为餐厨垃圾干重的0.5%)混合破碎后进入好氧堆沤槽。餐厨垃圾在每个堆沤槽内停留时间为10天;二号位6、三号位7、四号位8和五号位9堆沤槽内每天通气速率为25L-空气/kg-有机物/d,堆沤槽所产臭气经生物脱臭装置净化后排放;二号位6、三号位7、四号位8、五号位9和六号位10堆沤槽内有机物含水率通过喷淋发酵液调节含水率,使之不低于60%。经堆沤的餐厨垃圾由厌氧发酵罐进料口25进入厌氧发酵罐14。厌氧发酵罐14与六个好氧堆沤槽间隔板的导热系数为136kW/(m2·℃);单个好氧堆沤槽与厌氧发酵罐14的体积比为1:30;餐厨垃圾在厌氧发酵罐14内水力停留时间为20天。在本发酵装置中,按上述操作条件,装置产气率为420-520mL-甲烷/g-vs。The above-mentioned device is used to process the food waste produced by the family. The thermal conductivity of the outer wall 12 of the fermentation device box is 0.00048kW/(m 2 ·°C). The device processes about 2kg of food waste per day. Garbage and composite bacteria agent (dosing amount is 0.5% of the dry weight of kitchen waste) are mixed and crushed and then enter the aerobic stack retting tank. The residence time of food waste in each retting tank is 10 days; the daily ventilation rate in the retting tanks at No. 2 6, No. 3 7, No. 4 8 and No. 5 9 is 25L-air/kg-organic matter /d, the odor produced by the retting tank is discharged after being purified by the biological deodorization device; the moisture content of the organic matter in the retting tank at No. 6, No. 3, 8, No. 5, No. 9 and No. Spray the fermentation broth to adjust the moisture content so that it is not less than 60%. The retting kitchen waste enters the anaerobic fermentation tank 14 through the feed port 25 of the anaerobic fermentation tank. The thermal conductivity of anaerobic fermentation tank 14 and six aerobic retting tank partitions is 136kW/(m 2 ·℃); the volume ratio of a single aerobic retting tank to anaerobic fermentation tank 14 is 1:30; The hydraulic retention time of the garbage in the anaerobic fermentation tank 14 is 20 days. In this fermentation device, according to the above operating conditions, the gas production rate of the device is 420-520mL-methane/g-vs.

实施例2Example 2

使用实施例1相同的装置,餐厨垃圾在进入垃圾处理器3前混入定量菌糠,餐厨垃圾:菌糠=5:1;餐厨垃圾在每个堆沤槽内停留时间为5天;餐厨垃圾在厌氧发酵罐14内水力停留时间为30天。其他条件与实施例1相同。按上述操作条件,装置产气率为490-580mL-甲烷/g-vs。Using the same device of embodiment 1, kitchen waste is mixed into quantitative bacterial chaff before entering garbage disposer 3, kitchen waste: bacterial chaff=5:1; The residence time of food waste in each retting tank is 5 days; The hydraulic retention time of food waste in the anaerobic fermentation tank 14 is 30 days. Other conditions are identical with embodiment 1. According to the above operating conditions, the gas production rate of the device is 490-580mL-methane/g-vs.

实施例3Example 3

使用实施例1相同的装置,餐厨垃圾量日处理量约为20kg;单个好氧堆沤槽与厌氧发酵罐14的体积比为1:25;餐厨垃圾在每个堆沤槽内停留时间为7天。其他条件与实施例2相同。按上述操作条件,装置产气率为510-590mL-甲烷/g-vs。Using the same device as in Example 1, the daily processing capacity of kitchen waste is about 20kg; the volume ratio of a single aerobic retting tank to anaerobic fermentation tank 14 is 1:25; food waste stays in each retting tank The time is 7 days. Other conditions are identical with embodiment 2. According to the above operating conditions, the gas production rate of the device is 510-590mL-methane/g-vs.

本发明将好氧堆沤装置设置于厌氧发酵装置外围,可利用好氧发酵过程所产热量,提高厌氧发酵速率。此外,餐厨垃圾经好氧堆沤后,易降解有机物可被分解,可有效缓解厌氧发酵过程中的酸化问题,提高系统稳定性。最后,本装置所产二次污染较少,还可回收生物质能源,装置结构合理,易操作,是较为合适的家用餐厨垃圾处理装置。In the present invention, the aerobic stacking retting device is arranged on the periphery of the anaerobic fermentation device, and the heat generated in the aerobic fermentation process can be utilized to increase the rate of anaerobic fermentation. In addition, after aerobic composting of food waste, easily degradable organic matter can be decomposed, which can effectively alleviate the acidification problem in the anaerobic fermentation process and improve system stability. Finally, the device produces less secondary pollution and can also recover biomass energy. The device has a reasonable structure and is easy to operate. It is a more suitable device for treating household kitchen waste.

以上所述是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明所述原理的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。The above description is a preferred embodiment of the present invention, it should be pointed out that for those of ordinary skill in the art, without departing from the principle of the present invention, some improvements and modifications can also be made, these improvements and modifications It should also be regarded as the protection scope of the present invention.

Claims (5)

1. a kind of small-sized kitchen garbage installation for fermenting, it is characterised in that: including feed system, aerobic composting system, anaerobic fermentation System and deodoration system;
Wherein, feed system is located at kitchen garbage installation for fermenting top, and feed system includes pond (1), garbage disposer charging Mouth (2) and garbage disposer (3);Aerobic composting system includes the identical six aerobic stack retting slots of volume, six aerobic stack retting slots Connection annular in shape, six aerobic stack retting slots are located at No.1 position (5), No. two positions (6), third place (7), No. four positions (8), No. five Position (9) and No. six positions (10);Have partition (11) between six aerobic stack retting slots, six aerobic stack retting slots are driven by motor (16) to be revolved Turn;No. two positions (6), third place (7), No. four positions (8) and No. five position (9) stack retting slots are by being laid on the air pipeline (26) of bottom It ventilates;After the produced foul smell of stack retting slot is collected by foul smell gas gathering mask (28), it is de- that deodoration system is delivered to through foul smell pipeline (29) Discharge after smelly;No. two positions (6), third place (7), No. four positions (8), No. five positions (9) and No. six position (10) stack retting groove top portions are equipped with hair Zymotic fluid spray equipment (19);The aerobic stack retting slot feed inlet (4) of garbage disposer (3) outlet connection stack retting slot No.1 position (5);Heap Macerate the fermentation liquid that slot No.1 position (5) produced fermentation liquid is discharged into kitchen garbage installation for fermenting bottom through submerged fermentation liquid delivery pipe (30) Collecting tank (17), the fermented liquid spray piping (18) of fermentation liquid collecting tank (17) interior fermentation liquid and fermentation liquid spray equipment (19) return It is sprayed onto stack retting slot;Stack retting slot No. six positions (10) bottom is equipped with anaerobic fermentation tank feed inlet (25);
There are blender (15) in anaerobic fermentation tank (14) in anaerobic fermentation system, is driven by motor (16);When anaerobic fermentation tank into When material mouth (25) is opened, blender (15) starting;When anaerobic fermentation tank feed inlet (25) are closed, blender (15) is opened daily 2 times, every time 3 minutes;Anaerobic fermentation tank (14) produced biogas enters biogas collection through firedamp drainage mouth (21) and biogas pipeline (22) Airbag (23) is used for gas furnace (24);Anaerobic fermentation tank (14) produced biogas slurry and biogas residue is through biogas slurry and biogas residue discharge outlet (20) and biogas slurry Biogas residue pipeline (27) is discharged into septic tank;
Rotate 60 degree within described six aerobic stack retting slots every 1-2 days;Kitchen garbage residence time in each stack retting slot is 5-14 days;
No. two positions (6), third place (7), No. four positions (8) and No. five daily Ventilation Rates of position (9) stack retting slot are 10-25L- empty Gas/kg- organic matter/d;Have in No. two positions (6), third place (7), No. four positions (8), No. five positions (9) and No. six position (10) stack retting slots Machine object adjusts moisture content by spray fermentation liquid, makes moisture content therein not less than 60%;
The anaerobic fermentation tank (14) is closely surround by six aerobic stack retting slots;Anaerobic fermentation tank (14) and six aerobic stack retting slots The thermal coefficient of spacing board is 100-250kW/ (m2·℃);
The interior kitchen garbage hydraulic detention time of anaerobic fermentation tank (14) is 15-30 days;
The volume ratio of each aerobic stack retting slot and anaerobic fermentation tank (14) is 1:20-1:40.
2. small-sized kitchen garbage installation for fermenting according to claim 1, it is characterised in that: the aerobic composting system and detest Aerobe fermentation system sealing is equipped with thermal insulation material in same cabinet between cabinet exterior (12) and cabinet wall (13), wherein heat preservation The thermal coefficient of material is lower than 0.0005kW/ (m2·℃)。
3. small-sized kitchen garbage installation for fermenting according to claim 1, it is characterised in that: the garbage disposer (3) is used In adding complex micro organism fungicide in broken kitchen garbage, garbage disposer (3), it is kitchen garbage dry weight that microbial inoculum, which adds ratio, 0.5%-1%.
4. small-sized kitchen garbage installation for fermenting according to claim 1, it is characterised in that: in the anaerobic fermentation tank (14) It is inoculated with the anaerobically digested sludge through taming.
5. small-sized kitchen garbage installation for fermenting according to claim 1, it is characterised in that: the deodorization in the deodoration system Device is biological deodorizer or materialization deodorization device.
CN201610266733.9A 2016-04-26 2016-04-26 A kind of small-sized kitchen garbage installation for fermenting Expired - Fee Related CN105948832B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610266733.9A CN105948832B (en) 2016-04-26 2016-04-26 A kind of small-sized kitchen garbage installation for fermenting

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610266733.9A CN105948832B (en) 2016-04-26 2016-04-26 A kind of small-sized kitchen garbage installation for fermenting

Publications (2)

Publication Number Publication Date
CN105948832A CN105948832A (en) 2016-09-21
CN105948832B true CN105948832B (en) 2019-08-06

Family

ID=56916530

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610266733.9A Expired - Fee Related CN105948832B (en) 2016-04-26 2016-04-26 A kind of small-sized kitchen garbage installation for fermenting

Country Status (1)

Country Link
CN (1) CN105948832B (en)

Families Citing this family (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106431517A (en) * 2016-12-01 2017-02-22 北京科技大学 Kitchen waste treatment device for coupling aerobic composting with anaerobic fermentation
CN107935653B (en) * 2017-12-29 2023-05-12 浙江浦江加百列生态科技有限公司 Organic liquid fertilizer fermentation process and fermentation system
CN110655188B (en) * 2019-10-11 2020-08-11 重庆大学 Domestic garbage leachate and landfill gas cooperative treatment device and method thereof
CN111604356A (en) * 2020-05-25 2020-09-01 上海巷西环境科技有限公司 Self-degradable and environmentally friendly intelligent treatment equipment and method for household kitchen waste
CN112625874B (en) * 2021-01-22 2023-08-25 浙江师范大学 Anaerobic digestion treatment system for kitchen waste
CN112845531B (en) * 2021-01-22 2022-03-25 浙江师范大学 Anaerobic digestion treatment method for kitchen waste
CN114160556B (en) * 2021-12-02 2022-09-06 深圳市复绿生物环保科技有限公司 Kitchen waste liquid wastewater treatment equipment, organic fertilizer and preparation method
CN114590981B (en) * 2022-01-17 2024-03-15 上海市机电设计研究院有限公司 Device for aerobic stabilization of kitchen waste anaerobic digestion residues
CN114410696A (en) * 2022-02-08 2022-04-29 北京科技大学 Method for producing methane by co-fermenting kitchen waste and mushroom bran at high temperature
CN114873838B (en) * 2022-04-13 2024-06-07 扬州金威环保科技有限公司 A kind of restaurant kitchen waste water treatment equipment and treatment method
CN114854541A (en) * 2022-06-14 2022-08-05 中国农业大学烟台研究院 Special horizontal anaerobic fermentation device of domestic kitchen garbage

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101560466A (en) * 2009-06-01 2009-10-21 北京科技大学 Integrated methane dry fermentation device
CN102476959A (en) * 2010-11-30 2012-05-30 中国环境科学研究院 Anaerobic quick start and anaerobic-aerobic integrated fermentation method under low temperature condition
CN204342630U (en) * 2014-12-09 2015-05-20 北京智创环绿科技有限公司 A kind of sludge from wastewater treatment plant combined bio treatment system

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07214037A (en) * 1994-02-10 1995-08-15 Akira Ito Organic waste treatment equipment

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101560466A (en) * 2009-06-01 2009-10-21 北京科技大学 Integrated methane dry fermentation device
CN102476959A (en) * 2010-11-30 2012-05-30 中国环境科学研究院 Anaerobic quick start and anaerobic-aerobic integrated fermentation method under low temperature condition
CN102476959B (en) * 2010-11-30 2014-07-16 中国环境科学研究院 Anaerobic rapid starting and anaerobic-aerobic integrated fermentation method at low temperature
CN204342630U (en) * 2014-12-09 2015-05-20 北京智创环绿科技有限公司 A kind of sludge from wastewater treatment plant combined bio treatment system

Also Published As

Publication number Publication date
CN105948832A (en) 2016-09-21

Similar Documents

Publication Publication Date Title
CN105948832B (en) A kind of small-sized kitchen garbage installation for fermenting
CN101724655B (en) Method for producing methane as clean energy source by utilizing catering organic waste
CN104384170B (en) A kind of organic garbage of city and the agricultural technique of debirs and device of carrying out a biological disposal upon
CN106431517A (en) Kitchen waste treatment device for coupling aerobic composting with anaerobic fermentation
CN104774044A (en) Organic waste recycling method and sterilization apparatus used in method
CN102336508A (en) Rapid dehydration and resource treatment method and system for urban domestic sludge
CN102443537A (en) Organic waste aerobic fermentation device and method
CN206298517U (en) The food waste treatment device that a kind of aerobic compost is coupled with anaerobic fermentation
CN204171071U (en) A kind of device being applicable to biological treatment organic garbage of city and agriculture debirs
CN101792339A (en) Organic solid waste film covering high-temperature aerobic fermentation method
CN105152508B (en) Enhance sludge anaerobic installation for fermenting
CN105057307A (en) Domestic rubbish treatment system
CN102212561A (en) Processing method for fermenting straws in dry-process and wet-process combined way
CN201648259U (en) High-temperature aerobic fermentation device covered by organic solid waste films
CN103923821B (en) Anaerobic digestion device and digestion method for kitchen waste
CN202415542U (en) Aerobic fermentation device for organic waste
CN206502756U (en) A kind of device of excess sludge mixture rubbish from cooking methane phase organic fertilizer
CN101215049A (en) A Co-processing Process of Ecological Rural Sewage and Organic Solid Waste
CN101948336B (en) Apparatus and method for completely-mixed fermentation treatment of kitchen/bathroom organic wastes
CN102976809A (en) Planetary type full-automatic sludge aerobic fermentation device and system
CN112355032A (en) Distributed kitchen garbage storage, dehydration and biochemical integrated treatment device for residential buildings
CN202700937U (en) Organic waste source separation management system
CN206940900U (en) A kind of novel household garbage enzyme preparation dry type anaerobic digestion device
CN207567126U (en) A kind of animal faeces wastes resource utilization system
Saleh et al. The potential of sustainable biogas production from animal waste

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20190806