CN110407424A - A method for treating animal and plant manure in an ectopic fermentation bed - Google Patents
A method for treating animal and plant manure in an ectopic fermentation bed Download PDFInfo
- Publication number
- CN110407424A CN110407424A CN201910787977.5A CN201910787977A CN110407424A CN 110407424 A CN110407424 A CN 110407424A CN 201910787977 A CN201910787977 A CN 201910787977A CN 110407424 A CN110407424 A CN 110407424A
- Authority
- CN
- China
- Prior art keywords
- fermentation
- tank
- litter
- ectopic
- fermentation bed
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 238000000855 fermentation Methods 0.000 title claims abstract description 124
- 230000004151 fermentation Effects 0.000 title claims abstract description 124
- 210000003608 fece Anatomy 0.000 title claims abstract description 91
- 241001465754 Metazoa Species 0.000 title claims abstract description 18
- 238000000034 method Methods 0.000 title claims abstract description 18
- 239000010871 livestock manure Substances 0.000 title claims description 64
- 239000000463 material Substances 0.000 claims abstract description 21
- 238000003860 storage Methods 0.000 claims abstract description 14
- 239000003895 organic fertilizer Substances 0.000 claims abstract description 6
- 238000012545 processing Methods 0.000 claims abstract description 4
- 239000010865 sewage Substances 0.000 claims description 38
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 34
- 239000007921 spray Substances 0.000 claims description 33
- 241000894006 Bacteria Species 0.000 claims description 22
- 238000009423 ventilation Methods 0.000 claims description 22
- 241000196324 Embryophyta Species 0.000 claims description 13
- 239000007789 gas Substances 0.000 claims description 13
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 11
- 239000001301 oxygen Substances 0.000 claims description 11
- 229910052760 oxygen Inorganic materials 0.000 claims description 11
- 235000008331 Pinus X rigitaeda Nutrition 0.000 claims description 10
- 235000011613 Pinus brutia Nutrition 0.000 claims description 10
- 241000018646 Pinus brutia Species 0.000 claims description 10
- 239000003864 humus Substances 0.000 claims description 10
- 238000006073 displacement reaction Methods 0.000 claims description 9
- 239000003795 chemical substances by application Substances 0.000 claims description 6
- 239000000203 mixture Substances 0.000 claims description 6
- 238000005507 spraying Methods 0.000 claims description 6
- 238000003756 stirring Methods 0.000 claims description 6
- 239000004927 clay Substances 0.000 claims description 5
- NLYAJNPCOHFWQQ-UHFFFAOYSA-N kaolin Chemical compound O.O.O=[Al]O[Si](=O)O[Si](=O)O[Al]=O NLYAJNPCOHFWQQ-UHFFFAOYSA-N 0.000 claims description 5
- 239000010902 straw Substances 0.000 claims description 5
- 229910052902 vermiculite Inorganic materials 0.000 claims description 5
- 239000010455 vermiculite Substances 0.000 claims description 5
- 235000019354 vermiculite Nutrition 0.000 claims description 5
- 230000001580 bacterial effect Effects 0.000 claims description 4
- 235000013399 edible fruits Nutrition 0.000 claims description 4
- 230000005611 electricity Effects 0.000 claims description 4
- 229910052622 kaolinite Inorganic materials 0.000 claims description 4
- 238000012423 maintenance Methods 0.000 claims description 4
- 239000013589 supplement Substances 0.000 claims description 4
- 238000012546 transfer Methods 0.000 claims description 4
- 235000013311 vegetables Nutrition 0.000 claims description 4
- 239000004568 cement Substances 0.000 claims description 3
- 238000010276 construction Methods 0.000 claims description 3
- 239000003651 drinking water Substances 0.000 claims description 3
- 235000020188 drinking water Nutrition 0.000 claims description 3
- 230000003203 everyday effect Effects 0.000 claims description 3
- 230000000813 microbial effect Effects 0.000 claims description 3
- 210000002700 urine Anatomy 0.000 claims description 3
- 240000007594 Oryza sativa Species 0.000 claims description 2
- 235000007164 Oryza sativa Nutrition 0.000 claims description 2
- 239000010903 husk Substances 0.000 claims description 2
- 235000009566 rice Nutrition 0.000 claims description 2
- 229910001385 heavy metal Inorganic materials 0.000 abstract description 10
- 241001148470 aerobic bacillus Species 0.000 abstract description 3
- 125000004122 cyclic group Chemical group 0.000 abstract 1
- 244000005700 microbiome Species 0.000 description 7
- 238000004064 recycling Methods 0.000 description 6
- 238000009825 accumulation Methods 0.000 description 3
- 238000005054 agglomeration Methods 0.000 description 3
- 230000002776 aggregation Effects 0.000 description 3
- 238000009395 breeding Methods 0.000 description 3
- 230000001488 breeding effect Effects 0.000 description 3
- 238000000354 decomposition reaction Methods 0.000 description 3
- 230000021962 pH elevation Effects 0.000 description 3
- 239000002023 wood Substances 0.000 description 3
- 241000607479 Yersinia pestis Species 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 230000035699 permeability Effects 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000005995 Aluminium silicate Substances 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 235000012211 aluminium silicate Nutrition 0.000 description 1
- -1 and leaves Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 238000005056 compaction Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000004146 energy storage Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000011010 flushing procedure Methods 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 230000008635 plant growth Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 238000003900 soil pollution Methods 0.000 description 1
- 241000894007 species Species 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/02—Biological treatment
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D9/00—Other inorganic fertilisers
-
- 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
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F3/00—Fertilisers from human or animal excrements, e.g. manure
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05G—MIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/20—Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
-
- 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)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Molecular Biology (AREA)
- Health & Medical Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Environmental & Geological Engineering (AREA)
- Biochemistry (AREA)
- Biotechnology (AREA)
- General Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Pest Control & Pesticides (AREA)
- Processing Of Solid Wastes (AREA)
- Fertilizers (AREA)
Abstract
Description
技术领域technical field
本发明涉及粪污处理技术领域,具体的涉及一种异位发酵床处理动植物粪污方法。The invention relates to the technical field of manure treatment, in particular to a method for treating animal and plant manure in an ectopic fermentation bed.
背景技术Background technique
养殖业作为我国的一个重要产业,该产业的产量以及对环境的影响是人们最主要关心的方面,养殖的动物每天都会产生大量的粪便和冲刷养殖场产生的粪污,而粪污若没有经过适当处理,直接排到土坑里或河流中,则会严重污染土壤和水源。Breeding is an important industry in our country. The output of this industry and its impact on the environment are the main concerns of people. Farmed animals will produce a lot of manure every day and the manure produced by flushing the farm. If the manure has not passed through If it is properly disposed of and discharged directly into pits or rivers, it will seriously pollute soil and water sources.
近年来,越来越多的养殖场开始采用异位发酵床这项技术措施来对养殖场粪污进行处理,虽然一定程度上对粪污进行了处理,但该技术从根本上来说,任然存在一定的问题。In recent years, more and more farms have begun to use the technical measure of ectopic fermentation bed to treat farm manure. Although manure has been treated to a certain extent, this technology is fundamentally still There are certain problems.
现有的异位发酵床通过将养殖场与粪污分离,再通过微生物对粪污进行发酵分解,但发酵过程中会产生大量的热气,直接排放到环境中不仅会存在一定的资源浪费,而且也会因热气中的一些有害元素对环境造成影响,而且现有的异位发酵床大多直接采用木屑或谷壳作为垫料,垫料种类较为单一,吸水透气性不佳,极易造成垫料含水量过多,微生物无法完全分解粪污降低发酵效率的问题,极易使得多余的粪水溢出进入土壤造成土壤的污染,同时现有的异位发酵床在发酵过程中极易造成重金属富集,产生垫料板结或死床现象,从而影响垫料的回收再利用,使得垫料成为了另一种污染物。The existing ectopic fermentation bed separates the farm from the manure, and then ferments and decomposes the manure through microorganisms. However, a large amount of heat will be generated during the fermentation process, and it will not only waste resources to a certain extent if it is directly discharged into the environment. It will also affect the environment due to some harmful elements in the hot air, and most of the existing ectopic fermentation beds directly use wood chips or chaff as bedding materials. If the water content is too high, microorganisms cannot completely decompose the manure and reduce the fermentation efficiency, which will easily cause excess manure to overflow into the soil and cause soil pollution. At the same time, the existing ectopic fermentation bed will easily cause heavy metal enrichment during the fermentation process , resulting in litter compaction or dead bed phenomenon, thus affecting the recycling of litter, making litter another pollutant.
发明内容Contents of the invention
1.要解决的技术问题1. Technical problems to be solved
本发明要解决的技术问题在于提供一种异位发酵床处理动植物粪污方法,能有效降低养殖场的成本,避免集污池粪便堆积结块,避免异位发酵床因重金属含量过高产生的死床现象,能有效对粪污进行充分分解,减少粪污对环境的污染。The technical problem to be solved by the present invention is to provide a method for treating animal and plant manure in an ectopic fermentation bed, which can effectively reduce the cost of the farm, avoid the accumulation and agglomeration of feces in the sewage collection pool, and avoid the occurrence of excessive heavy metal content in the ectopic fermentation bed. The dead bed phenomenon can effectively decompose the manure and reduce the environmental pollution caused by manure.
2.技术方案2. Technical solution
为解决上述问题,本发明采取如下技术方案:In order to solve the above problems, the present invention takes the following technical solutions:
一种异位发酵床处理动植物粪污方法,包括如下步骤:A method for treating animal and plant manure in an ectopic fermentation bed, comprising the steps of:
步骤一,异位发酵床的建设:Step 1, construction of ectopic fermentation bed:
A、在养殖场附近通过水泥建立斜坡式异位发酵床,异位发酵床的中间为喷淋池,喷淋池两侧至少设有2个发酵池;A. Establish a slope type ectopic fermentation bed by cement near the farm. The middle of the ectopic fermentation bed is a spray pool, and at least 2 fermentation pools are arranged on both sides of the spray pool;
B、将垫料均匀铺撒在发酵池内部,并在垫料表面均匀撒上菌种,菌种铺撒量为1kg/2.5m3;B. Spread the litter evenly inside the fermentation tank, and evenly spread the bacteria on the surface of the litter, and the amount of bacteria spread is 1kg/2.5m 3 ;
C、在喷淋池内部均匀固定搅拌机,将发酵池两侧顶部均设置有滑轨,在滑轨之间滑动安装位移机,再于位移机上方安装自动喷淋机,自动喷淋机一端安装抽污泵,在移机下方安装槽式翻抛机,槽式翻抛机的宽度与发酵池宽度相等;C. Fix the mixer evenly inside the spray tank, set slide rails on the top of both sides of the fermentation tank, slide and install the displacement machine between the slide rails, and then install the automatic spray machine above the displacement machine, and install the automatic spray machine at one end Sewage pump, install a trough turner under the transfer machine, the width of the trough turner is equal to the width of the fermentation tank;
D、在异位发酵床上方建立密封阳光棚,密封阳光棚的两侧均固定有通风风机,再于异位发酵床附近建立集气罐,将一侧通风风机通过管道与通风风机相连通,另一侧通风风机与外界环境相连通;D. Set up a sealed sun shed above the ectopic fermentation bed. Ventilation fans are fixed on both sides of the sealed sun shed, and then a gas collecting tank is built near the ectopic fermentation bed, and the ventilation fan on one side is connected with the ventilation fan through a pipeline. The ventilation fan on the other side is connected with the external environment;
步骤二,粪污收集处理:Step 2, manure collection and treatment:
A、在养殖场下方建立集污池,并在集污池附近设立蓄水箱,通过蓄水箱为养殖场提供饮用水;A. Set up a sewage collection tank under the farm, and set up a water storage tank near the sewage collection tank, and provide drinking water for the farm through the water storage tank;
B、在集污池内部安装切割泵,通过切割泵将收集的粪尿进行高速破碎搅拌,保持集污池内部粪污的均匀性,再通过蓄水箱为集污池提供额外补水,保持集污池的含水量达到50~60%;B. Install a cutting pump inside the sewage collection tank, and use the cutting pump to crush and stir the collected feces and urine at a high speed to maintain the uniformity of the feces and sewage inside the sewage collection tank, and then provide additional water for the sewage collection tank through the water storage tank to maintain the collection The water content of the sewage pool reaches 50-60%;
C、在集污池与异位发酵床之间铺设管道,通过抽液泵将集污池中混合均匀的粪水抽入步骤一中的喷淋池内部;C. Lay a pipeline between the sewage collection tank and the ectopic fermentation bed, and pump the uniformly mixed dung in the sewage collection tank into the inside of the spray tank in step 1 through a liquid suction pump;
步骤三,异位发酵:Step 3, ectopic fermentation:
A、打开步骤一中密封阳光棚两侧的通风风机,保持密封阳光棚内部通风性,保持棚内含氧量不低于环境含氧量的80%,在发酵池中均匀喷洒发酵剂对垫料进行初步发酵,发酵时间为5~6天;A. Turn on the ventilation fans on both sides of the sealed sun shed in step 1, maintain the ventilation inside the sealed sun shed, keep the oxygen content in the shed not lower than 80% of the ambient oxygen content, and evenly spray the fermentation agent on the mat in the fermentation tank The material is initially fermented, and the fermentation time is 5 to 6 days;
B、打开步骤一中喷淋池内部的搅拌机,通过搅拌机对喷淋池内部粪水进行持续搅拌,保持粪水的均匀性,再通过抽污泵将粪水抽入自动喷淋机中并均匀喷洒在垫料上,控制位移机在滑轨上移动,通过槽式翻抛机不断地对喷洒过粪水的垫料进行翻动,翻动频率为3~4次/天;B. Turn on the mixer inside the spray tank in step 1, and continuously stir the dung water inside the spray tank through the mixer to maintain the uniformity of the dung water, and then use the sewage pump to pump the dung water into the automatic spray machine and make it evenly Spray on the litter, control the displacement machine to move on the slide rail, and continuously turn the litter sprayed with dung water through the trough turning machine, and the turning frequency is 3 to 4 times per day;
C、对密封阳光棚内部进行升温,通过高温异位发酵床对粪污进行发酵,发酵过程中保持发酵池的中心温度在55℃以上,保持异位发酵床发酵池在发酵时垫料的含水量在40~45%;C. Heat up the temperature inside the sealed sun shed, and ferment the manure through the high-temperature ectopic fermentation bed. During the fermentation process, keep the center temperature of the fermentation tank above 55°C, and keep the content of the litter in the ectopic fermentation bed fermentation tank during fermentation. The water volume is 40-45%;
D、将发酵产生的热量和气体通过一侧通风风机导入集气罐中储存,为养殖场提供一定的能源储备,供养殖场发电使用。D. The heat and gas generated by fermentation are introduced into the gas collecting tank through the ventilation fan on one side for storage, so as to provide a certain energy reserve for the farm to generate electricity for the farm.
步骤四,定期处理和维护:Step four, regular processing and maintenance:
A、每个月补充1~2次菌种,补充的菌种含量不超过初次铺撒菌种量的5%;A. Supplement the bacteria 1-2 times a month, and the content of the supplemented bacteria should not exceed 5% of the amount of the bacteria that was spread for the first time;
B、每隔6~8个月清理出垫料总量的一半作为蔬菜、果树以及其它农作物的有机肥料循环使用,再补充一定含量的垫料,保持垫料总高度不低于原垫料高度的90%。B. Clean up half of the total amount of litter every 6 to 8 months as organic fertilizer for vegetables, fruit trees and other crops, and then add a certain amount of litter to keep the total height of the litter not lower than the height of the original litter 90% of.
具体地,步骤一A中所述发酵池底部均设置6~8个排水沟。Specifically, 6 to 8 drainage ditches are arranged at the bottom of the fermentation tank in step 1A.
具体地,步骤一B中所述垫料为树叶、木屑、秸秆碎料、橘皮碎料、谷壳以及蛭石碎料、高岭石粘土中的至少两种物料,且相邻两种物料之间均撒有一层松针腐殖土。Specifically, the litter in Step 1B is at least two kinds of materials among leaves, sawdust, straw scraps, orange peel scraps, rice husks, vermiculite scraps, and kaolinite clay, and the adjacent two materials A layer of pine needle humus was sprinkled between them.
具体地,所述垫料的总高度为1.2~1.5m,且每层松针腐殖土的厚度不超过0.2m。Specifically, the total height of the litter is 1.2-1.5m, and the thickness of each layer of pine needle humus is no more than 0.2m.
具体地,步骤一B中所述菌种为高温腐熟菌和好氧性微生物菌剂的混合物。Specifically, the bacterial species described in Step 1B is a mixture of high-temperature decomposing bacteria and aerobic microbial bacterial agents.
具体地,步骤三B中所述自动喷淋机的喷洒量为1T/50m3。 Specifically, the spraying amount of the automatic spraying machine described in Step 3B is 1T/50m 3 .
具体地,步骤三C中所述发酵过程中密封阳光棚内部含氧量不足时,保持每平米垫料每天获得10~15m3的空气补充。Specifically, when the oxygen content inside the sealed sun shed is insufficient during the fermentation process described in step 3C, 10-15 m 3 of air is maintained per square meter of litter per day.
3.有益效果3. Beneficial effect
(1)本发明通过在异位发酵床上方建立密封阳光棚,并在异位发酵床附近建立集气罐,通过管道将密封阳光棚一侧的通风风机与集气罐相连通,能有效将异位发酵床发酵过程中产生的热量和气体通入集气罐中储存,从而为养殖场提供一定的能源储备,供养殖场发电使用,有效避免了传统露天式发酵床在发酵时产生的热气对环境的影响,并有效将能源回收利用,节省了能源支出,降低了养殖场的成本;(1) The present invention establishes a sealed sunlight shed above the ectopic fermentation bed, and builds an air collecting tank near the ectopic fermentation bed, and connects the ventilation fan on one side of the sealed sun shed with the air collecting tank through a pipeline, which can effectively The heat and gas generated during the fermentation process of the ectopic fermentation bed are stored in the gas collection tank, thereby providing a certain energy reserve for the farm to generate electricity for the farm, effectively avoiding the heat generated by the traditional open-air fermentation bed during fermentation The impact on the environment, and the effective recycling of energy, saves energy expenses and reduces the cost of the farm;
(2)本发明通过采用切割泵对集污池中的动物粪污进行破碎切割后再发酵,有效避免了传统集污池长期集污后,粪便堆积结块的现象,并通过喷淋池内部的搅拌机对粪污进行二次搅拌,进一步保证粪水的均匀性,从而保证粪污能与垫料充分发酵,减少粪污残留,避免了垫料板结或造成异位发酵床死床的现象;(2) The invention uses a cutting pump to crush and cut the animal manure in the sewage collection tank before fermenting, which effectively avoids the phenomenon of accumulation and agglomeration of feces after long-term sewage collection in the traditional sewage collection tank, and passes through the inside of the spray tank The advanced mixer performs secondary stirring on the manure to further ensure the uniformity of the manure, thereby ensuring that the manure can be fully fermented with the litter, reducing the residue of manure, and avoiding the phenomenon of hardening of the bedding or causing dead beds in the ectopic fermentation bed;
(3)本发明通过采用多种物料混合而成的垫料与发酵相结合的处理方法,有效提高了传统垫料的吸水性和透气性,并有效通过垫料吸附粪污中的臭气和重金属,从而解决了传统异位发酵床因重金属含量过高产生的死床现象,同时能有效通过松针腐殖土中和粪污中的碱性物质,减少垫料盐度富集,从而有效改善垫料pH值,避免垫料pH值过度碱化,提高垫料的活性,提升发酵效率,抑制粪污中害虫和病菌的繁殖,便于垫料的回收利用,减少了垫料回收利用时对环境的二次污染;(3) The present invention effectively improves the water absorption and air permeability of the traditional litter by adopting a treatment method combining litter mixed with various materials and fermentation, and effectively absorbs the odor and odor in the manure through the litter. Heavy metals, thus solving the dead bed phenomenon caused by the high content of heavy metals in the traditional ectopic fermentation bed, and at the same time, it can effectively neutralize the alkaline substances in the manure through the pine needle humus, reduce the salinity enrichment of the litter, and effectively improve The pH value of the litter material can avoid excessive alkalinization of the litter material, improve the activity of the litter material, improve the fermentation efficiency, inhibit the reproduction of pests and bacteria in the manure, facilitate the recycling of the litter material, and reduce the impact on the environment when the litter material is recycled. secondary pollution;
(4)本发明通过将粪污均匀喷洒到异位发酵床中的发酵池内进行升温发酵,并通过定期对垫料进行翻动,有效提高粪污与垫料的接触面积,从而有效通过好氧微生物对粪污进行分解,使得粪污达到无害化处理的目的,避免了养殖场粪污直接排放对环境造成的影响,同时垫料通过发酵后能有效提供微生物所需的生态环境平衡,使粪便分解可持续进行,有效便于粪污的综合化治理,极大的减少了养殖场的养殖污水,有效减轻了养殖行业对环境的污染;(4) In the present invention, the manure is evenly sprayed into the fermentation tank in the ectopic fermentation bed for heating and fermentation, and the litter is turned over regularly to effectively increase the contact area between the manure and the litter, thereby effectively passing aerobic microorganisms Decompose the manure so that the manure can achieve the purpose of harmless treatment, avoiding the impact on the environment caused by the direct discharge of manure from the farm, and at the same time, the litter can effectively provide the ecological environment balance required by microorganisms after fermentation, so that the manure The decomposition can be carried out sustainably, effectively facilitating the comprehensive treatment of manure, greatly reducing the breeding sewage of the farm, and effectively reducing the pollution of the breeding industry to the environment;
(5)本发明通过定期对异位发酵床进行处理和维护,有效保证了异位发酵床的含菌量,保证了发酵环境的含氧浓度,便于好氧菌的充分繁殖,从而有效通过好氧微生物充分分解粪污中的有机物,进而保证粪污的充分分解处理,减少粪污对环境的污染,同时能有效通过垫料与粪污的发酵,使得垫料可作为生物有机肥回收利用,有效为蔬菜、果树以及其它农作物提供营养,促进植物的生长,达到垫料循环利用的目的;(5) The present invention effectively guarantees the bacterial content of the heterotopic fermentation bed and the oxygen concentration of the fermentation environment through regular treatment and maintenance of the heterotopic fermentation bed, which facilitates the full reproduction of aerobic bacteria, thereby effectively passing the good Oxygen microorganisms fully decompose the organic matter in the manure, thereby ensuring the full decomposition and treatment of the manure, reducing the pollution of the manure to the environment, and at the same time, it can effectively ferment the bedding and manure, so that the bedding can be recycled as bio-organic fertilizer. Effectively provide nutrients for vegetables, fruit trees and other crops, promote the growth of plants, and achieve the purpose of litter recycling;
综上,本发明所提供的一种异位发酵床处理动植物粪污方法,能有效将异位发酵床发酵过程中产生的热量和气体通入集气罐中储存,为养殖场提供一定的能源储备,节省了能源支出,降低了养殖场的成本,能有效避免集污池粪便堆积结块,保证喷洒粪污的均匀性,能有效通过多种物料混合而成的垫料对粪污进行充分发酵,有效吸附粪污中的臭气和重金属,解决了传统异位发酵床因重金属含量过高产生的死床现象,有效改善垫料pH值,避免垫料pH值过度碱化,提升发酵效率,能有效通过好氧菌分解粪污,对粪污进行充分分解,抑制粪污中害虫和病菌的繁殖,减少粪污对环境的污染,同时能有效使得发酵后的垫料作为生物有机肥回收利用,达到垫料循环利用的目的。In summary, a method for treating animal and plant manure in an ectopic fermentation bed provided by the present invention can effectively transfer the heat and gas generated in the fermentation process of the ectopic fermentation bed into the gas collection tank for storage, and provide a certain amount of energy for the farm. Energy storage saves energy expenditure, reduces the cost of the farm, can effectively avoid the accumulation and agglomeration of feces in the sewage collection tank, ensures the uniformity of spraying manure, and can effectively treat manure through the litter mixed with various materials. Fully ferment, effectively absorb the odor and heavy metals in the manure, solve the dead bed phenomenon caused by the high content of heavy metals in the traditional ectopic fermentation bed, effectively improve the pH value of the litter, avoid excessive alkalinization of the pH value of the litter, and improve fermentation High efficiency, can effectively decompose manure through aerobic bacteria, fully decompose manure, inhibit the reproduction of pests and bacteria in manure, reduce the pollution of manure to the environment, and effectively make the fermented litter as bio-organic fertilizer Recycling, to achieve the purpose of litter recycling.
具体实施方式Detailed ways
下面结合实施例对本发明作进一步详细的说明。Below in conjunction with embodiment the present invention is described in further detail.
实施例1Example 1
一种异位发酵床处理动植物粪污方法,包括如下步骤:A method for treating animal and plant manure in an ectopic fermentation bed, comprising the steps of:
步骤一,异位发酵床的建设:Step 1, construction of ectopic fermentation bed:
A、在养殖场附近通过水泥建立斜坡式异位发酵床,异位发酵床的中间为喷淋池,喷淋池两侧设有2个发酵池,发酵池底部均设置6个排水沟,有效避免多余水量富集,影响后续发酵处理;A. A slope-type ectopic fermentation bed is established by cement near the farm. The middle of the ectopic fermentation bed is a spray pool. There are 2 fermentation pools on both sides of the spray pool, and 6 drainage ditches are set at the bottom of the fermentation pool, which is effective Avoid the enrichment of excess water, which will affect the subsequent fermentation process;
B、将垫料均匀铺撒在发酵池内部,垫料取树叶、秸秆碎料、蛭石碎料和高岭石粘土的混合物,树叶、秸秆碎料、蛭石碎料和高岭石粘土的总体积比为2:5:1:2,且相邻两种物料之间均撒有一层松针腐殖土,垫料的总高度为1.2m,且每层松针腐殖土的厚度为0.1m,便于通过树叶和秸秆碎料中的纤维素快速吸附粪污中的水分,并提高垫料的透气性,便于垫料中的微生物对粪污进行分解,能有效通过蛭石碎料和高岭石粘土吸附粪污中的水分和重金属,避免了异位发酵床因重金属含量过高产生的死床现象,能有效通过松针腐殖土中和粪污中的碱性物质,减少垫料盐度富集,从而有效改善垫料pH值,避免垫料pH值过度碱化,在垫料表面均匀撒上菌种,菌种铺撒量为1kg/2.5m3,菌种为高温腐熟菌和好氧性微生物菌剂的混合物,有效保证菌种在高温环境下进行生物分解,从而充分对粪污进行处理;B. Spread the bedding evenly inside the fermentation tank. The bedding is a mixture of leaves, straw scraps, vermiculite scraps and kaolinite clay, and leaves, straw scraps, vermiculite scraps and kaolinite clay. The total volume ratio is 2:5:1:2, and a layer of pine needle humus is sprinkled between two adjacent materials. The total height of the litter is 1.2m, and the thickness of each layer of pine needle humus is 0.1m , it is convenient to quickly absorb the moisture in the manure through the cellulose in the leaves and straw debris, and improve the air permeability of the bedding material, which is convenient for the microorganisms in the bedding material to decompose the manure, and can effectively pass through the vermiculite debris and kaolin Stone clay absorbs moisture and heavy metals in manure, avoiding the dead bed phenomenon caused by excessive heavy metal content in ectopic fermentation beds, and can effectively neutralize alkaline substances in manure through pine needle humus and reduce litter salinity Enrichment, so as to effectively improve the pH value of the litter, avoid excessive alkalinization of the pH value of the litter, evenly sprinkle the bacteria on the surface of the litter, the amount of the bacteria spread is 1kg/2.5m 3 , the bacteria are high-temperature decomposed bacteria and good The mixture of aerobic microbial agents can effectively ensure the biological decomposition of the bacteria in a high temperature environment, so as to fully treat the manure;
C、在喷淋池内部均匀固定搅拌机,将发酵池两侧顶部均设置有滑轨,在滑轨之间滑动安装位移机,再于位移机上方安装自动喷淋机,自动喷淋机一端安装抽污泵,在移机下方安装槽式翻抛机,槽式翻抛机的宽度与发酵池宽度相等;C. Fix the mixer evenly inside the spray tank, set slide rails on the top of both sides of the fermentation tank, slide and install the displacement machine between the slide rails, and then install the automatic spray machine above the displacement machine, and install the automatic spray machine at one end Sewage pump, install a trough turner under the transfer machine, the width of the trough turner is equal to the width of the fermentation tank;
D、在异位发酵床上方建立密封阳光棚,密封阳光棚的两侧均固定有通风风机,再于异位发酵床附近建立集气罐,将一侧通风风机通过管道与通风风机相连通,另一侧通风风机与外界环境相连通;D. Set up a sealed sun shed above the ectopic fermentation bed. Ventilation fans are fixed on both sides of the sealed sun shed, and then a gas collecting tank is built near the ectopic fermentation bed, and the ventilation fan on one side is connected with the ventilation fan through a pipeline. The ventilation fan on the other side is connected with the external environment;
步骤二,粪污收集处理:Step 2, manure collection and treatment:
A、在养殖场下方建立集污池,并在集污池附近设立蓄水箱,通过蓄水箱为养殖场提供饮用水;A. Set up a sewage collection tank under the farm, and set up a water storage tank near the sewage collection tank, and provide drinking water for the farm through the water storage tank;
B、在集污池内部安装切割泵,通过切割泵将收集的粪尿进行高速破碎搅拌,保持集污池内部粪污的均匀性,再通过蓄水箱为集污池提供额外补水,保持集污池的含水量达到50%;B. Install a cutting pump inside the sewage collection tank, and use the cutting pump to crush and stir the collected feces and urine at a high speed to maintain the uniformity of the feces and sewage inside the sewage collection tank, and then provide additional water for the sewage collection tank through the water storage tank to maintain the collection The water content of the sewage pool reaches 50%;
C、在集污池与异位发酵床之间铺设管道,通过抽液泵将集污池中混合均匀的粪水抽入步骤一中的喷淋池内部;C. Lay a pipeline between the sewage collection tank and the ectopic fermentation bed, and pump the uniformly mixed dung in the sewage collection tank into the inside of the spray tank in step 1 through a liquid suction pump;
步骤三,异位发酵:Step 3, ectopic fermentation:
A、打开步骤一中密封阳光棚两侧的通风风机,保持密封阳光棚内部通风性,保持棚内含氧量达到环境含氧量的85%,在发酵池中均匀喷洒发酵剂对垫料进行初步发酵,发酵时间为5天;A. Turn on the ventilation fans on both sides of the sealed sun shed in step 1, maintain the ventilation inside the sealed sun shed, keep the oxygen content in the shed to 85% of the oxygen content in the environment, and spray the fermentation agent evenly in the fermentation tank to dry the litter. Preliminary fermentation, the fermentation time is 5 days;
B、打开步骤一中喷淋池内部的搅拌机,通过搅拌机对喷淋池内部粪水进行持续搅拌,保持粪水的均匀性,再通过抽污泵将粪水抽入自动喷淋机中并均匀喷洒在垫料上,自动喷淋机的喷洒量为1T/50m3,避免粪污过度喷洒造成垫料含水量过多的现象,控制位移机在滑轨上移动,通过槽式翻抛机不断地对喷洒过粪水的垫料进行翻动,翻动频率为3次/天;B. Turn on the mixer inside the spray tank in step 1, and continuously stir the dung water inside the spray tank through the mixer to maintain the uniformity of the dung water, and then use the sewage pump to pump the dung water into the automatic spray machine and make it evenly Spray on the litter, the spraying amount of the automatic sprayer is 1T/50m 3 , to avoid the excessive water content of the litter caused by excessive spraying of feces, control the displacement machine to move on the slide rail, through the trough type throwing machine to continuously Turn the litter that has been sprayed with dung water regularly, and the turning frequency is 3 times/day;
C、对密封阳光棚内部进行升温,通过高温异位发酵床对粪污进行发酵,发酵过程中保持发酵池的中心温度在60℃,保持异位发酵床发酵池在发酵时垫料的含水量在40%,发酵过程中密封阳光棚内部含氧量不足时,保持每平米垫料每天获得15m3的空气补充,有效保证菌种中的好氧微生物的生存环境,便于对粪污进行发酵处理;C. Heat up the inside of the sealed sun shed, and ferment the manure through the high-temperature ectopic fermentation bed. During the fermentation process, keep the central temperature of the fermentation tank at 60°C, and maintain the water content of the litter during fermentation in the ectopic fermentation bed fermentation tank. At 40%, when the oxygen content inside the sealed sun shed is insufficient during the fermentation process, 15m3 of air is maintained per square meter of litter every day, which effectively ensures the living environment of aerobic microorganisms in the strains and facilitates the fermentation of manure. ;
D、将发酵产生的热量和气体通过一侧通风风机导入集气罐中储存,为养殖场提供一定的能源储备,供养殖场发电使用。D. The heat and gas generated by fermentation are introduced into the gas collecting tank through the ventilation fan on one side for storage, so as to provide a certain energy reserve for the farm to generate electricity for the farm.
步骤四,定期处理和维护:Step four, regular processing and maintenance:
A、每个月补充1次菌种,补充的菌种含量为初次铺撒菌种量的3%;A. Supplement the bacteria once a month, and the supplemented bacteria content is 3% of the initial spread of bacteria;
B、每隔6个月清理出垫料总量的一半作为蔬菜、果树以及其它农作物的有机肥料循环使用,再补充一定含量的垫料,保持垫料总高度为原垫料高度的95%。B. Clean up half of the total amount of litter every 6 months as organic fertilizer for vegetables, fruit trees and other crops, and then add a certain amount of litter to keep the total height of the litter at 95% of the original height.
实施例2Example 2
一种异位发酵床处理动植物粪污方法,本实施例与实施例1的不同之处在于,步骤一B中,垫料取木屑、橘皮碎料和谷壳的混合物,木屑、橘皮碎料和谷壳的总体积比为6:1:3,且相邻两种物料之间均撒有一层松针腐殖土,垫料的总高度为1.5m,且每层松针腐殖土的厚度为0.15m。A method for treating animal and plant manure in an ectopic fermentation bed. The difference between this embodiment and Example 1 is that in Step 1B, the litter is a mixture of wood chips, orange peel scraps and chaff, and wood chips, orange peel The total volume ratio of crushed material and chaff is 6:1:3, and a layer of pine needle humus is sprinkled between the two adjacent materials. The total height of the litter is 1.5m, and each layer of pine needle humus The thickness is 0.15m.
其他同实施例1。Others are the same as embodiment 1.
本技术领域中的普通技术人员应当认识到,以上的实施例仅是用来说明本发明,而并非用作为对本发明的限定,只要在本发明的实质精神范围内,对以上所述实施例的变化、变型都将落在本发明的权利要求范围内。Those of ordinary skill in the art should recognize that the above embodiments are only used to illustrate the present invention, rather than as a limitation to the present invention, as long as within the scope of the spirit of the present invention, the above-described embodiments Changes and modifications will fall within the scope of the claims of the present invention.
Claims (8)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910787977.5A CN110407424A (en) | 2019-08-26 | 2019-08-26 | A method for treating animal and plant manure in an ectopic fermentation bed |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910787977.5A CN110407424A (en) | 2019-08-26 | 2019-08-26 | A method for treating animal and plant manure in an ectopic fermentation bed |
Publications (1)
Publication Number | Publication Date |
---|---|
CN110407424A true CN110407424A (en) | 2019-11-05 |
Family
ID=68368926
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201910787977.5A Pending CN110407424A (en) | 2019-08-26 | 2019-08-26 | A method for treating animal and plant manure in an ectopic fermentation bed |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN110407424A (en) |
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110746244A (en) * | 2019-11-26 | 2020-02-04 | 湖南明镜生物科技有限公司 | Method for preparing soil conditioner by fermenting bed stockpile |
CN111003912A (en) * | 2019-12-16 | 2020-04-14 | 温氏食品集团股份有限公司 | Dirty membrane of excrement covers fermentation degradation system |
CN111704335A (en) * | 2020-06-30 | 2020-09-25 | 福建省农业科学院畜牧兽医研究所 | A zero-emission mode treatment system and working method for aquaculture waste |
CN111848311A (en) * | 2020-08-14 | 2020-10-30 | 湖南省蓝鹰科技有限公司 | Method for preparing biological fertilizer from pig manure in pig farm |
CN112094040A (en) * | 2020-08-19 | 2020-12-18 | 裴毅敏 | Treatment method for realizing zero pollution discharge of pig farm excrement resource utilization |
CN112279696A (en) * | 2020-10-27 | 2021-01-29 | 江苏省农业科学院 | A kind of solid matrix raw material prepared by using rabbit farm sewage and preparation method thereof |
CN112913698A (en) * | 2021-02-05 | 2021-06-08 | 江西正合生态农业有限公司 | Method for fully quantitatively collecting, storing and transporting pig breeding excrement |
CN113121274A (en) * | 2021-04-20 | 2021-07-16 | 漳州市强生环保设备有限公司 | Fermentation treatment system containing organic waste aerobic fermentation pile turning machine |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP3771570B1 (en) * | 2004-11-22 | 2006-04-26 | セブンフーズ株式会社 | Livestock barn and excrement disposal method in barn |
CN105859078A (en) * | 2016-04-05 | 2016-08-17 | 福建省农业科学院农业生物资源研究所 | Ectopic fermentation bed livestock breeding excrement treatment system and application thereof |
CN108046559A (en) * | 2017-12-26 | 2018-05-18 | 广东广垦畜牧工程研究院有限公司 | A kind of scale pig-breeding field waste zero-emission utilization system |
CN110143738A (en) * | 2019-05-28 | 2019-08-20 | 山东众客食品有限公司 | A kind of meat duck cultivation waste heterotopic biological fermentation bed processing method |
-
2019
- 2019-08-26 CN CN201910787977.5A patent/CN110407424A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP3771570B1 (en) * | 2004-11-22 | 2006-04-26 | セブンフーズ株式会社 | Livestock barn and excrement disposal method in barn |
CN105859078A (en) * | 2016-04-05 | 2016-08-17 | 福建省农业科学院农业生物资源研究所 | Ectopic fermentation bed livestock breeding excrement treatment system and application thereof |
CN108046559A (en) * | 2017-12-26 | 2018-05-18 | 广东广垦畜牧工程研究院有限公司 | A kind of scale pig-breeding field waste zero-emission utilization system |
CN110143738A (en) * | 2019-05-28 | 2019-08-20 | 山东众客食品有限公司 | A kind of meat duck cultivation waste heterotopic biological fermentation bed processing method |
Non-Patent Citations (1)
Title |
---|
李齐贤: "《高效养猪关键技术》", 31 January 2010, 安徽科学技术出版社 * |
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110746244A (en) * | 2019-11-26 | 2020-02-04 | 湖南明镜生物科技有限公司 | Method for preparing soil conditioner by fermenting bed stockpile |
CN111003912A (en) * | 2019-12-16 | 2020-04-14 | 温氏食品集团股份有限公司 | Dirty membrane of excrement covers fermentation degradation system |
CN111704335A (en) * | 2020-06-30 | 2020-09-25 | 福建省农业科学院畜牧兽医研究所 | A zero-emission mode treatment system and working method for aquaculture waste |
CN111848311A (en) * | 2020-08-14 | 2020-10-30 | 湖南省蓝鹰科技有限公司 | Method for preparing biological fertilizer from pig manure in pig farm |
CN112094040A (en) * | 2020-08-19 | 2020-12-18 | 裴毅敏 | Treatment method for realizing zero pollution discharge of pig farm excrement resource utilization |
CN112279696A (en) * | 2020-10-27 | 2021-01-29 | 江苏省农业科学院 | A kind of solid matrix raw material prepared by using rabbit farm sewage and preparation method thereof |
CN112913698A (en) * | 2021-02-05 | 2021-06-08 | 江西正合生态农业有限公司 | Method for fully quantitatively collecting, storing and transporting pig breeding excrement |
CN113121274A (en) * | 2021-04-20 | 2021-07-16 | 漳州市强生环保设备有限公司 | Fermentation treatment system containing organic waste aerobic fermentation pile turning machine |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN110407424A (en) | A method for treating animal and plant manure in an ectopic fermentation bed | |
CN106824972B (en) | Comprehensive treatment system and method for breeding pollution of large-scale pig farm | |
CN101416610B (en) | Pigpen fermentation bed and use thereof | |
CN103265154B (en) | Resource utilization and comprehensive treatment process for sewage and manure generated during cultivation | |
CN205420113U (en) | Livestock farm dung disposal system | |
CN102557772A (en) | Fermentation device for sludge compost treatment and treatment method using same | |
CN104016557A (en) | Governance method for realizing resource utilization and zero pollution emission of piggery wastes | |
CN107360982A (en) | A kind of method of the outer fermentation bed processing piggery waste of house | |
CN101279861B (en) | A method for processing pig manure to produce organic fertilizer | |
CN104430187A (en) | Method for treating sludge in vermiculture | |
CN107698119A (en) | A kind of administering method for realizing the discharge of piggery waste recycling no pollution | |
CN111454086A (en) | Guide rail vehicle type anaerobic-aerobic combined fermentation composting device | |
CN109526762A (en) | The cattle farm fermenting bed padding and preparation method thereof that after separating dry space from moist space prepared by cattle manure residue | |
CN104108840B (en) | A kind of water rushes the dirty integrated conduct method of excrement formula large-scale milch cow farms excrement | |
CN111718091A (en) | A kind of urban sludge treatment method | |
CN102173548B (en) | Method for improving degradation and aerobic composting of cow dung with earthworm | |
CN206188669U (en) | Quick compost reactor | |
CN107466876A (en) | A kind of preparation method of dystopy microbial fermentation bed | |
CN101696075A (en) | Method for biologically digesting and recycling pig large intestine excrement and hair and intestine wastes | |
CN201362974Y (en) | Simple environment-friendly hoggery | |
CN1931798A (en) | In-situ farm animal excrement degrading process | |
CN106431580A (en) | Method and apparatus for treating fecal contamination and producing organic fertilizer at same time through simulation forest surface ecological system | |
CN212035037U (en) | Wisdom ecological agriculture industry building circulation system | |
JP3706097B2 (en) | Organic waste fermentation treatment system | |
CN108207648A (en) | The integration ecological colony house of breeding waste utilization of resources |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20191105 |
|
RJ01 | Rejection of invention patent application after publication |