CN101279861B - A method for processing pig manure to produce organic fertilizer - Google Patents
A method for processing pig manure to produce organic fertilizer Download PDFInfo
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- CN101279861B CN101279861B CN200810069727XA CN200810069727A CN101279861B CN 101279861 B CN101279861 B CN 101279861B CN 200810069727X A CN200810069727X A CN 200810069727XA CN 200810069727 A CN200810069727 A CN 200810069727A CN 101279861 B CN101279861 B CN 101279861B
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- pig manure
- organic fertilizer
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- 210000003608 fece Anatomy 0.000 title claims abstract description 38
- 239000010871 livestock manure Substances 0.000 title claims abstract description 38
- 238000000034 method Methods 0.000 title claims abstract description 17
- 239000003895 organic fertilizer Substances 0.000 title claims abstract description 14
- 238000004519 manufacturing process Methods 0.000 claims abstract description 16
- 238000000855 fermentation Methods 0.000 claims abstract description 15
- 230000004151 fermentation Effects 0.000 claims abstract description 15
- 239000002361 compost Substances 0.000 claims abstract description 13
- 239000002781 deodorant agent Substances 0.000 claims abstract description 13
- 238000002955 isolation Methods 0.000 claims abstract description 13
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 21
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 claims description 12
- 239000003795 chemical substances by application Substances 0.000 claims description 12
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 claims description 10
- 239000000463 material Substances 0.000 claims description 7
- 229910000019 calcium carbonate Inorganic materials 0.000 claims description 5
- 238000002834 transmittance Methods 0.000 claims description 5
- 230000001580 bacterial effect Effects 0.000 claims 3
- 238000009264 composting Methods 0.000 abstract description 18
- 230000000694 effects Effects 0.000 abstract description 4
- 238000005265 energy consumption Methods 0.000 abstract description 4
- 241000894006 Bacteria Species 0.000 abstract description 3
- 238000009792 diffusion process Methods 0.000 abstract description 2
- 235000015097 nutrients Nutrition 0.000 abstract description 2
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 abstract 1
- 239000003337 fertilizer Substances 0.000 description 18
- 239000002068 microbial inoculum Substances 0.000 description 9
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 8
- 239000000203 mixture Substances 0.000 description 8
- 238000009413 insulation Methods 0.000 description 5
- 229910021529 ammonia Inorganic materials 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 230000000249 desinfective effect Effects 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 230000003321 amplification Effects 0.000 description 1
- 238000009305 arable farming Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- 230000003139 buffering effect Effects 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 230000018044 dehydration Effects 0.000 description 1
- 238000006297 dehydration reaction Methods 0.000 description 1
- 230000001877 deodorizing effect Effects 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 230000002045 lasting effect Effects 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 235000013622 meat product Nutrition 0.000 description 1
- 230000002906 microbiologic effect Effects 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 238000003199 nucleic acid amplification method Methods 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 239000010900 piggery waste Substances 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
Classifications
-
- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
- Y02P20/133—Renewable energy sources, e.g. sunlight
-
- 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
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- Fertilizers (AREA)
Abstract
一种处理猪粪生产有机肥的方法，将马粪接种于猪粪中，通过两次高温发酵，纯化、扩增其中的高温纤维菌，制备出发酵菌剂，然后在太阳能隔离温室中接种堆肥，生产出有机肥。该方法堆肥启动快，保氮除臭剂成本低，来源广，效果好；有机肥生产的全部过程均在太阳能隔离温室中进行，有效的防止了猪粪和养分的扩散等二次污染，实现了清洁化处理猪粪并生产有机肥。适合多雨、潮湿、冬季气温偏低的西南和类似地区，投资小，能耗少，成本低，操作简单，实用性强，容易推广。A method for processing pig manure to produce organic fertilizer. Inoculate horse manure into pig manure, purify and amplify the high-temperature cellulosic bacteria in it through two high-temperature fermentations, prepare fermentation bacteria, and then inoculate compost in a solar isolation greenhouse , to produce organic fertilizer. The composting method starts quickly, the cost of nitrogen-containing deodorant is low, the source is wide, and the effect is good; the whole process of organic fertilizer production is carried out in a solar isolation greenhouse, which effectively prevents secondary pollution such as the diffusion of pig manure and nutrients, and realizes In order to cleanly process pig manure and produce organic fertilizer. It is suitable for southwest and similar areas with rainy, humid, and low winter temperatures. It has small investment, low energy consumption, low cost, simple operation, strong practicability, and easy promotion.
Description
Technical field
The present invention relates to modern livestock breeding industry, environmental pollution improvement and fertilizer field.Particularly relate to and a kind ofly be primarily aimed at China southwest and characteristics such as similar area is rainy, moist, winter temperature is on the low side, the pig manure of intensive pig production generation, the method for cleaner production fertilizer are handled in innoxious, less energy-consumption.
Background technology
Along with the raising of people's living standard, the continuous increase of population increases day by day to the requirement of meat product, and progress of science and technology makes traditional pig industry develop rapidly to the intensive pig production mode, has also brought a series of environmental problem thereupon.Around many pig farms, concentrate near the ecotopes such as land, water body and air of the dirty severe contamination of excrement of discharging, be badly in need of effectively administering.
At present, the method for administering the intensification piggery waste is a lot, and technical characterstic has nothing in common with each other, and suitable condition and range is also different.Produce in the process of fertilizer at the harmless treatment pig manure, drying and dehydrating, deodoring and disinfecting, quick composting, cut down the consumption of energy, problem such as cleaner production all do not obtain fine solution.In addition, these technology relatively are fit to the area of northern China dry and rainless, and the higher South China of winter temperature.China southwest is rainy, moist, winter temperature is on the low side, and the effect of using relevant technologies processing pig manure is relatively poor, and cost is higher, is difficult to effective application, is badly in need of the pig manure that a kind of effective processing intensification of exploitation pig farm produces, and the novel method of production fertilizer.
Summary of the invention
The objective of the invention is to, provide a kind of suitable China southwest and similar area, innoxious, less energy-consumption processing and utilizing pig manure, the method for cleaner production fertilizer.Under the condition rainy, moist, that winter temperature is on the low side, the pig manure that the intensification pig farm is produced carries out deodoring and disinfecting, quick composting, drying and dehydrating effectively, produces the organic fertilizer that is fit to arable farming.
A kind of method of handling pig manure production fertilizer of the present invention, realize successively through the following steps:
(1) gather fresh horsehit, mix with the pig manure of water content 70～75% in 1: 10 ratio of mass ratio, composting is 10 days in insulation can or fermentation vat or fermenter, gets original microbial inoculum;
(2) original microbial inoculum is mixed with the pig manure of water content 70～75% in 1: 10 ratio of mass ratio, composting is 10 days in insulation can or fermentation vat or fermenter, must produce and use fermenting agent;
(3) build the sun power Isolation warm house, material of main part uses transmittance greater than 80% hollow sunlight board, and the top is an arcuate structure, and its area is pressed: S=0.1X+300 calculates, and X is the fertilizer annual production, 1000＜X＜10000 ton; The common calcium sulfate of mass ratio 75% is mixed with 25% ordinary calcium carbonate, make nitrogen-protecting deodorant; In the sun power Isolation warm house, respectively add in the pig manure of water content 70～75% producing in the ratio of mass ratio 1% with fermenting agent and nitrogen-protecting deodorant, mix, compost thickness is not less than 2 meters, and volume is not less than 100 cubic metres, composting 12～14 days; Every turning in 3～5 days once, reduce to below 20% after temperature is increased to 60 ℃, promptly produce organic fertilizer until water content.
Horsehit is inoculated in the pig manure, and by twice thermophilic fermentation, purifying, amplification high temperature fiber bacterium are wherein prepared fermenting agent.The purpose of using this microbial inoculum is the microbiological degradation process that starts rapidly in the compost, improves the composting temperature, sterilizes effectively and shortens fermentation time.
Sun power Isolation warm house function is to absorb sun power, improves envrionment temperature, both has been of value to the insulation dehydration in the pig manure composting process, is beneficial to again and prevents that foul smell from distributing, and realizes cleaner production.
The nitrogen-protecting deodorant function is:
A. absorb protein and decompose the ammonia that discharges, reduce ammonia volatilization, improve the fertilizer fertilizer efficiency.Its principles of chemistry are:
NH
4 ++CaSO
4→Ca
2 ++(NH
4)
2SO
4；
B. deodorizing.Ammonia is one of main component of pig manure foul smell, so calcium sulfate is absorbing ammonia, reduces volatilization, has the de-odorised function when improving fat effect;
C. the organic acid that produces with organic matter decomposition in, the pH of compost material changes in the buffering organic matter decomposition process, is of value to the lasting vigorous activity of microorganism, reduces moisture, promotes to become thoroughly decomposed.
Similarly regional in China southwest and weather condition, to utilize the inventive method to handle pig manure and produce fertilizer, need 15～20 days summer approximately, 45～50 days winters.
Advantage of the present invention is:
1, compost starts soon, fast 1～2 day than common compost start time; Time is short, and need 15～20 days summer, 45～50 days winters, and common compost needs more than 30 days summer at least, surpasses 3 months winter, even can not effectively handle pig manure under field conditions (factors) and produce fertilizer; The temperature height, top temperature can reach 65 ℃, and deodoring and disinfecting is thorough, and the top temperature of common compost is 55～60 ℃.
2, the nitrogen-protecting deodorant cost is low, and the source is wide, and is effective.Use after the nitrogen-protecting deodorant, the fertilizer nitrogen content can improve more than 25%, and the foul smell in the composting fermentation process obviously reduces, and the pH luffing reduces.
3, all processes of organic fertilizer production all carries out in the sun power Isolation warm house, has effectively stoped the diffusion of pig manure and nutrient, and foul smell secondary pollution such as distributes, and has realized cleaning and has handled pig manure and produce fertilizer.In addition, aspect structure design and material use, fully absorb sun power, improve envrionment temperature, and prevent that heat scatters and disappears, being of value to behind the fermentation reactor system later stage of fertilizer becomes thoroughly decomposed and dehydrates.
4, be fit to rainy, moist, that winter temperature is on the low side southwest and similar area, invest little, less energy consumption, cost is low, and is simple to operate, practical, easy popularization.
Embodiment
Embodiment 1:
Gather fresh horsehit, mix with the pig manure of water content 70～75% in 1: 10 ratio of mass ratio, composting is 10 days in insulation can, gets original microbial inoculum; Original microbial inoculum is mixed with the pig manure of water content 70～75% in 1: 10 ratio of mass ratio, and composting is 10 days in insulation can, must produce and use fermenting agent; Build the sun power Isolation warm house, material of main part uses transmittance greater than 80% hollow sunlight board, and the top is an arcuate structure, and its area is 400m
2, i.e. 1000 tons of fertilizer annual production; The common calcium sulfate of mass ratio 75% is mixed with 25% ordinary calcium carbonate, make nitrogen-protecting deodorant, in the sun power Isolation warm house, respectively add in the pig manure of water content 70～75% producing in the ratio of mass ratio 1% with fermenting agent and nitrogen-protecting deodorant, mix, 2 meters of compost thickness, long 10 meters, wide 5 meters, composting 12 days; Turning in per 5 days was once reduced to below 20% until water content after temperature was increased to 60 ℃, promptly produced organic fertilizer;
Embodiment 2:
Gather fresh horsehit, mix with the pig manure of water content 70～75% in 1: 10 ratio of mass ratio, composting is 10 days in fermentation vat, gets original microbial inoculum; Original microbial inoculum is mixed with the pig manure of water content 70～75% in 1: 10 ratio of mass ratio, and composting is 10 days in fermentation vat, must produce and use fermenting agent; Build the sun power Isolation warm house, material of main part uses transmittance greater than 80% hollow sunlight board, and the top is an arcuate structure, and its area is 800m
2, i.e. 5000 tons of fertilizer annual production; The common calcium sulfate of mass ratio 75% is mixed with 25% ordinary calcium carbonate, make nitrogen-protecting deodorant, in the sun power Isolation warm house, respectively add in the pig manure of water content 70～75% producing in the ratio of mass ratio 1% with fermenting agent and nitrogen-protecting deodorant, mix, 3 meters of compost thickness, long 20 meters, wide 10 meters, composting 14 days; Turning in per 4 days was once reduced to below 20% until water content after temperature was increased to 60 ℃, promptly produced organic fertilizer;
Embodiment 3:
Gather fresh horsehit, mix with the pig manure of water content 70～75% in 1: 10 ratio of mass ratio, composting is 10 days in fermenter, gets original microbial inoculum; Original microbial inoculum is mixed with the pig manure of water content 70～75% in 1: 10 ratio of mass ratio, and composting is 10 days in fermenter, must produce and use fermenting agent; Build the sun power Isolation warm house, material of main part uses transmittance greater than 80% hollow sunlight board, and the top is an arcuate structure, and its area is 1300m
2, i.e. 10000 tons of fertilizer annual production; The common calcium sulfate of mass ratio 75% is mixed with 25% ordinary calcium carbonate, make nitrogen-protecting deodorant, in the sun power Isolation warm house, respectively add in the pig manure of water content 70～75% producing in the ratio of mass ratio 1% with fermenting agent and nitrogen-protecting deodorant, mix, 4 meters of compost thickness, long 20 meters, wide 10 meters, composting 14 days; Turning in per 3 days was once reduced to below 20% until water content after temperature was increased to 60 ℃, promptly produced organic fertilizer.
Claims (1)
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN200810069727XA CN101279861B (en) | 2008-05-23 | 2008-05-23 | A method for processing pig manure to produce organic fertilizer |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN200810069727XA CN101279861B (en) | 2008-05-23 | 2008-05-23 | A method for processing pig manure to produce organic fertilizer |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN101279861A CN101279861A (en) | 2008-10-08 |
| CN101279861B true CN101279861B (en) | 2010-06-09 |
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN200810069727XA Expired - Fee Related CN101279861B (en) | 2008-05-23 | 2008-05-23 | A method for processing pig manure to produce organic fertilizer |
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| CN (1) | CN101279861B (en) |
Families Citing this family (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101618979B (en) * | 2009-07-31 | 2012-10-24 | 广东希普生物科技股份有限公司 | Method for manufacturing bio-organic fertilizers |
| CN103274782A (en) * | 2013-06-01 | 2013-09-04 | 浙江大学 | Method for producing pig manure organic fertilizer by employing waste bacteria stick |
| CN103274784A (en) * | 2013-06-21 | 2013-09-04 | 西南大学 | Method for producing organic fertilizer by processing waste tobacco leaves in field |
| CN103274800A (en) * | 2013-06-21 | 2013-09-04 | 西南大学 | Method for producing special flue-cured tobacco organic fertilizer by processing apple juicing waste residues |
| CN103274785B (en) * | 2013-06-21 | 2014-09-24 | 西南大学 | A method for processing waste tobacco leaves in a rebaking factory to produce organic fertilizer |
| CN104130039B (en) * | 2014-08-19 | 2016-08-24 | 中山市巴斯德农业科技有限公司 | A kind of method utilizing food factory's waste liquid and fowl and animal excrement preparation to protect nitrogen type active organic fertilizer |
| CN110698231A (en) * | 2019-11-27 | 2020-01-17 | 湖南明镜生物科技有限公司 | Pig manure fermentation field construction and fermentation method |
| CN115594542B (en) * | 2022-08-16 | 2024-03-12 | 南京农业大学 | Bacillus sp.za microbial inoculum protective agent and application thereof |
| CN117700262B (en) * | 2023-12-11 | 2024-09-20 | 四川农业大学 | Method for deodorizing pig manure compost, preserving nitrogen and promoting decomposition |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1091729A (en) * | 1993-03-05 | 1994-09-07 | 北京市东城区环境卫生管理局 | human excrement particle fertilizer production method |
| CN1106774A (en) * | 1994-10-11 | 1995-08-16 | 屈寅利 | Multielement high-efficiency organic mixed fertilizer |
| CN1927772A (en) * | 2006-09-19 | 2007-03-14 | 苏长久 | Preparation process of farm manure |
| JP2008074672A (en) * | 2006-09-21 | 2008-04-03 | Shigeru Nakano | Manufacturing method of deodorized organic fertilizer, deodorized organic fertilizer and cultivating method of vegetable or flower plant using the same |
-
2008
- 2008-05-23 CN CN200810069727XA patent/CN101279861B/en not_active Expired - Fee Related
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1091729A (en) * | 1993-03-05 | 1994-09-07 | 北京市东城区环境卫生管理局 | human excrement particle fertilizer production method |
| CN1106774A (en) * | 1994-10-11 | 1995-08-16 | 屈寅利 | Multielement high-efficiency organic mixed fertilizer |
| CN1927772A (en) * | 2006-09-19 | 2007-03-14 | 苏长久 | Preparation process of farm manure |
| JP2008074672A (en) * | 2006-09-21 | 2008-04-03 | Shigeru Nakano | Manufacturing method of deodorized organic fertilizer, deodorized organic fertilizer and cultivating method of vegetable or flower plant using the same |
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| CN101279861A (en) | 2008-10-08 |
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