CN110407622A - A kind of production technology using anaerobism biogas residue production solid organic fertilizer - Google Patents
A kind of production technology using anaerobism biogas residue production solid organic fertilizer Download PDFInfo
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- CN110407622A CN110407622A CN201910603653.1A CN201910603653A CN110407622A CN 110407622 A CN110407622 A CN 110407622A CN 201910603653 A CN201910603653 A CN 201910603653A CN 110407622 A CN110407622 A CN 110407622A
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- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D1/00—Fertilisers containing potassium
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- 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
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- 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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Abstract
The invention discloses a kind of production technology using anaerobism biogas residue production solid organic fertilizer, the secondary ageing of material after the cloth and aerobic fermentation, aerobic fermentation of mixture, mixing including raw material, the preparation of powder fertilizer, the preparation of granulated fertilizer.The present invention provides the production technology that one kind is perfect, economic and practical, can rationally utilize biogas residue and stalk, with short production cycle, energy conservation and environmental protection.The organic fertilizer production produced using the technique is high-efficient, and organic fertilizer fertility is good.
Description
Technical field
The present invention relates to organic fertilizer technical fields, and in particular to a kind of production using anaerobism biogas residue production solid organic fertilizer
Technique.
Background technique
By years of researches and it was verified that the organic waste generated in people's life and environment, such as: living
Organic matter, agricultural crop straw, forest fallen leaves, the afforestation vegetation sub-elected in rubbish cuts grass, kitchen garbage, fowl and animal excrement etc., most
Real, most effective processing method is that biogas, three kinds of biogas slurry, biogas residue substances will be generated after fermentation using dry-type anaerobic fermentation.Its
In: biogas can be used for fuel gas generation;Water of the biogas slurry after sewage treatment is up to standard, which returns, can be used for producing;And to containing abundant nutrition
How ingredient biogas residue efficiently uses, and is allowed to turn waste into wealth, and maximumlly creating economic benefit, environmental benefit and social benefit is to work as
Preceding a great problem.
In recent years, with the fast development of Chinese society economy, the quickening and living standards of the people of urbanization process
Rapid raising, domestic waste yield increasingly increases.Averagely everyone generates 0.9~1.2kg house refuse daily in China, and
And increased with annual 3%~5% speed.State Ministry of Environmental Protection's publication in 2016 display: 2015, the big or middle city in 246, China
185,640,000 tons of Output of Domestic Waste, including the annual house refuse total amount that generates in the rural area whole nation is about 496,400,000 tons.Both at home and abroad
To the processing of domestic waste, there are mainly three types of methods: landfill, burn and part compost (kitchen garbage and fowl and animal excrement can heaps
Fertilizer).For vast rural area, discussion agenda is mentioned not yet to house refuse centralized processing work.
China is large agricultural country, and gradually accelerates urbanization process, and current problem is: first is that all kinds of crops straw of agricultural
Stalk yield is very high, at least 70% or more does not efficiently use at present, still based on the burn-up of field the edge of a field, causes largely to provide
Source waste and environmental pollution;Second is that being continuously improved, urban and rural environment greening is horizontal, and afforestation vegetation cuts grass and tree deciduous leaf increases year by year;
Third is that aquaculture continues to develop, birds and livestocks faces gradually increase.
Organic matter in these house refuses, kitchen garbage, fowl and animal excrement, agricultural crop straw, forest fallen leaves, greening at present
Vegetation cuts burning or landfill after grass etc. is substantially collected, and not only wastes vast resources, also brings environmental pollution and increases landfill
Land used.
In short, producing biogas, biogas slurry, natural pond if the organic matter of above-mentioned flood tide is all collected as fermentation raw material
Slag can be efficiently used further, not only renewable mass energy, while can not only have been reduced landfill land used but also can solve serious ring
Border pollution problem.
Chinese patent document CN 101774848B (201010011344.4) discloses a kind of biogas residue organic fertilizer and its preparation side
Method, mixture, granulation and shaping and drying and cooling before pretreatment, granulation including biogas residue.This method pre-processes biogas residue
Time is up to 5~6 months, and using air dry cure, curing efficiency is low, and can not make full use of to stalk etc..It is Chinese special
Sharp file CN101229982A (200810014630.9) discloses a kind of method using biogas residue production mixed organic manure, in biogas residue
Middle addition stalk prepares organic fertilizer, but stalk is caused organic fertilizer that cannot be applied and made full use of, and will increase disease without decomposed
Insect pest.
It is very big using biogas residue production its product differentiation of solid organic fertilizer both at home and abroad at present, it is extremely difficult to that " the Chinese people are total
With state agricultural industry criteria " organic fertilizer standard " (NY525-2012) standard " it requires, cause can not to sell or few markets
Demand, main cause are: its technology to using biogas residue be raw material manufacture organic fertilizer the characteristics of specific aim it is not strong, it is not perfect,
Mismatch, automatic control level are low, unstable product quality.
Summary of the invention
It is an object of the present invention to overcome defect existing in the prior art, provide it is a kind of it is perfect, economic and practical,
The production technology that biogas residue and stalk can be rationally utilized, with short production cycle, energy conservation and environmental protection.The organic fertilizer produced using the technique
High production efficiency, organic fertilizer fertility are good.
To achieve the above object, solid organic fertilizer is produced using anaerobism biogas residue the technical scheme is to design a kind of
Production technology, comprising the following steps:
(1) mixture of raw material
For the biogas residue that anaerobic fermentation of organisms generates after being dehydrated, the moisture content of biogas residue is aqueous by being added 70~75%
The crushing straw that rate is 10~20% makes the moisture content of blend feedstock 60~65%;The biogas residue and the volume ratio of stalk are
4~6:1;
Raw material after mixture is deposited in blend feedstock stockyard, and fermenting agent is added and forms mixing, using turning machine to original
Material is mixed well;The fermenting agent is commercially available microbial inoculum.
(2) cloth and aerobic fermentation of mixing
Mixing after choosing ageing from bottom to top is sent into aerobic fermentation pond, and mixing is first mixed well initial fermentation, secondary
The mixing that day will be located at feed end from movable upender is mobile to discharge end, vacates and meets the feed end that one day cloth doses needs
Length carries out the cloth of a new round, moves in circles, and completes entire fermentation period until material reaches discharge end;
The aerobic fermentation period of mixing is 10~15 days, and the moisture content of material is 40~45% after aerobic fermentation;
(3) after aerobic fermentation material ageing
The material fermented is sent to from the taking-up of fermentation vat discharge end by ageing area, the material ageing of production powder fertilizer using forklift
Period is 20~25 days, and the material water ratio after ageing is 30~33%;The material aging period for producing granulated fertilizer is 10~15 days,
Material water ratio is 35~37% after ageing;
(4) preparation of powder fertilizer
By the material after ageing first after pulverizer crushes, it is sent into screening machine and is sieved down, material screening partial size≤2mm;
Material after screening is matched with nitrogen source, phosphorus source and potassium resource according to standard, stirred, is mixed;
(5) preparation of granulated fertilizer
By the material after ageing first after pulverizer crushes, it is sent into screening machine and is sieved down, material screening partial size≤2mm;
Material after screening is stirred with nitrogen source, phosphorus source and potassium resource according to standard, is mixed, is packed;Mixed material water ratio
It is 34~35%;Adding water to adjust material water ratio is 35~36%, material is sent into granulator, by granule materials after granulation
It is sent into the drying of drum-type drying cooling screening integration apparatus.
The mixed mode of raw material is biogas residue and crushing straw tiling heap in pretreatment of raw material as a preferred technical solution,
It puts, biogas residue and stalk are alternately placed;The thickness degree of biogas residue laying is less than 10mm, and the thickness degree of laying straws is according to biogas residue and stalk
Moisture content is determined by calculation.
The mixed mode of raw material is that biogas residue and crushing straw, fermenting agent uniformly mix jointly in pretreatment of raw material, good
It is 1.2m~1.5m that mixed material, which stacks height, in aerobe fermentation pond.
The width in the aerobic fermentation pond is 4~5m as a preferred technical solution, is highly 1.6~2m;It is described aerobic
Fermentation vat is equipped with feed end and discharge end, and the length of feed end and discharge end is respectively the 1/10~1/ of aerobic fermentation pond total length
15, the aerobic fermentation bottom of pond portion is equipped with bottom of pond and is aerated coil pipe, and the circumference of the aeration coil pipe is equipped with intensive orderly ventilation
Hole, stomata arrangement, quantity and supply gas pressure of the aerobic fermentation pond on the aeration coil pipe from feed end to discharge end are according to each stage
Mixing determines the demand of oxygen.
The drying of granule materials and granulation process are the integration of drum-type drying cooling screening as a preferred technical solution,
The leading portion of equipment is hot wind, by granule materials drying dehumidification;Middle section is cold wind, and the cooling further dehumidifying of granule materials guarantees
The moisture content of granule materials is 20~22%;Back segment sieves granule materials after cooling, 8~12 mesh of screen size.
A kind of production system using biogas residue production solid organic fertilizer, including blend feedstock stockyard, aerobic fermentation pond, ageing
Feed bin, belt conveyor, pulverizer, screening machine, batch bin, nutrition regulating agent batch bin, is stirred chain-plate type feeder
Machine is granulated trimmer, drum-type drying cooling integration equipment, quantitative package machine;
The discharge port of slag charge storehouse and straw bin is connect with one end of belt conveyer respectively, the belt conveyer other end with
The connection of blend feedstock stockyard;Forklift is equipped between blend feedstock stockyard and the feed end in aerobic fermentation pond;The charging of aerobic fermentation pond
End is equipped with movable upender, and aerobic fermentation bottom of pond portion is equipped with bottom of pond and is aerated coil pipe, and bottom of pond is aerated coil pipe circumference and is equipped with ventilation
Forklift is equipped between the top hopper of hole, aerobic fermentation pond discharge end and chain-plate type feeder;The discharge port of chain-plate type feeder
It is connected to by belt conveyor with feeding hole of pulverizer, the discharge port of pulverizer is connect with the feed end of the first screening machine;On sieve
The feed inlet that object is back to pulverizer through belt conveyor conveying crushes again;Screenings is sent into batch bin by belt conveyor;
The discharge port of batch bin and nutrition regulating agent batch bin is connected to the feed inlet of stirring mixer, and the discharge port of stirring mixer is logical
It crosses belt conveyor and is connect with the feed inlet for being granulated trimmer, the discharge port for being granulated trimmer passes through belt conveyor and drum-type
The feed inlet of Drying and cooling integration apparatus is connected to;The leading portion and hot air duct entrance of drum-type drying cooling integration equipment connect
Logical, the middle section of drum-type drying cooling integration equipment is connected to cold air duct entrance, drum-type drying cooling integration equipment
Equipped with unit of exhausting waste gas, the discharge port of drum-type drying cooling integration equipment is connect with the feed inlet of the second screening machine, the
It is connect respectively by belt conveyor with quantitative package machine on the sieve of two screening machines and under sieve.
The unit of exhausting waste gas includes communicate with each other exhaust pipe and bag filter as a preferred technical solution,.
The advantages and beneficial effects of the present invention are:
(1) the made biological organic fertilizer of the present invention, is the organic waste generated with agricultural production and organic waste rubbish is
The biogas residue that raw material anaerobic fermentation generates carries out being rich in organic matter, amino acid, auxin, list in material obtained by aerobic fermentation again
Sugar, humic acid, unsaturated fatty acid, vitamin and certain phage speciess etc., referred to as " bioactive substance ".By aerobic
Fermentation, further degradation of organic substances so that raw material is thoroughly decomposed, will not due to secondary fermentation calcination root system, with prior art phase
Shorter than fermentation period, fermentation is complete.
(2) by the oxygen demand of control aerobic fermentation different times, the aerobic fermentation time is not only reduced, improves biogas residue
Fermentation rate.
(3) solid organic fertilizer of the invention has soil not hardened compared with traditional fertilizer, and agricultural production reserve strength is big, once
Fertilising at least can apply every year this seed manure in the function and effect of 3 years internal medicine performance fertility, and soil can be more and more fertile, is conducive to agriculture
Crop growth.
(4) the made biological organic fertilizer of the present invention, meets People's Republic of China's agricultural industry criteria " organic fertilizer standard "
(NY525-2012) standard and " biological organic fertilizer " (NY884-2012) standard are met by adding other inorganic fertilizer in right amount
Many-sided demand of plant growth reduces cultivation cost, reduces farmer's burdens.
Detailed description of the invention
Fig. 1 is process flow chart of the invention;
In figure: 1, biogas residue feed bin;2, straw bin;3, blend feedstock stockyard;4, aerobic fermentation pond;5, it is aged feed bin;6,
Pulverizer;7, the first screening machine;8, batch bin;9, nutrition regulating agent batch bin;10, stirring mixer;11, it is granulated trimmer;
12, drum-type drying cooling integration equipment;13, the second screening machine;14, quantitative package machine;15, hot air duct;16, exhaust gas is arranged
Device of air;17, cold air duct.
Specific embodiment
With reference to the accompanying drawings and examples, further description of the specific embodiments of the present invention.Following embodiment is only
For clearly illustrating technical solution of the present invention, and not intended to limit the protection scope of the present invention.
A kind of production technology using anaerobism biogas residue production solid organic fertilizer, comprising the following steps:
(1) mixture of raw material
For the biogas residue that anaerobic fermentation of organisms generates after being dehydrated, the moisture content of biogas residue is aqueous by being added 70~75%
The crushing straw that rate is 10~20% makes the moisture content of blend feedstock 60~65%;The biogas residue and the volume ratio of stalk are
4~6:1;
Raw material after mixture is deposited in blend feedstock stockyard, and fermenting agent is added and forms mixing, old by 10~15 days
Change forms mixing, is mixed well using turning machine to raw material;
(2) cloth and aerobic fermentation of mixing
Mixing after choosing ageing from bottom to top is sent into aerobic fermentation pond, and mixing is first mixed well initial fermentation, secondary
The mixing that day will be located at feed end from movable upender is mobile to discharge end, vacates and meets the feed end that one day cloth doses needs
Length carries out the cloth of a new round, moves in circles, and completes entire fermentation period until material reaches discharge end;
The aerobic fermentation period of mixing is 10~15 days, and the moisture content of material is 40~45% after aerobic fermentation;
(3) after aerobic fermentation material ageing
The material fermented is sent to from the taking-up of fermentation vat discharge end by ageing area, the material ageing of production powder fertilizer using forklift
Period is 20~25 days, and the material water ratio after ageing is 30~33%;The material aging period for producing granulated fertilizer is 10~15 days,
Material water ratio is 35~37% after ageing;
(4) preparation of powder fertilizer
By the material after ageing first after pulverizer crushes, it is sent into screening machine and is sieved down, material screening partial size≤2mm;
Material after screening is subjected to proportion stirring according to standard with nitrogen source, phosphorus source and potassium resource, is mixed, is packed;Nitrogen source, phosphorus source and potassium resource
Total addition level combination material Central Plains have the content of N P and K, according to the content of produced various criterion organic fertilizer according to calculation amount
Addition;
(5) preparation of granulated fertilizer
By the material after ageing first after pulverizer crushes, it is sent into screening machine and is sieved down, material screening partial size≤2mm;
Material after screening is matched with nitrogen source, phosphorus source and potassium resource according to standard, stirred, is mixed, is packed;Mixed material contains
Water rate is 34~35%;Adding water to adjust material water ratio is 35~36%, material is sent into granulator, by particle after granulation
Material is sent into the drying of drum-type drying cooling screening integration apparatus.
The mixed mode of raw material is that biogas residue and crushing straw tiling are stacked in pretreatment of raw material, and biogas residue and stalk are alternately put
It sets;The thickness degree of biogas residue laying is less than 10mm, and the thickness degree of laying straws is determined by calculation according to biogas residue and moisture content of straws.
The mixed mode of raw material is that biogas residue and crushing straw, fermenting agent uniformly mix jointly in pretreatment of raw material, and mixed material is good
The stacking height in aerobe fermentation pond is 1.2m~1.5m.
The width in the aerobic fermentation pond is 4~5m, is highly 1.6~2m;The aerobic fermentation pond be equipped with feed end and
The length of discharge end, feed end and discharge end is respectively the 1/10~1/15 of aerobic fermentation pond total length, the aerobic fermentation pond
Bottom is equipped with bottom of pond and is aerated coil pipe, and the circumference of the aeration coil pipe is equipped with intensive orderly venthole, aerobic fermentation Chi Congjin
Expect stomata arrangement, quantity and the supply gas pressure on end to the aeration coil pipe of discharge end according to each stage mixing to the demand of oxygen
It determines.
The drying of granule materials and granulation process are that the leading portion of drum-type drying cooling screening integration apparatus is hot wind, will
Granule materials drying dehumidification;Middle section is cold wind, by the cooling further dehumidifying of granule materials, guarantees that the moisture content of granule materials is 20
~22%;Back segment sieves granule materials after cooling, 8~12 mesh of screen size.
A kind of production system using biogas residue production solid organic fertilizer, including the blend feedstock stockyard, aerobic set gradually
Fermentation vat, ageing feed bin, chain-plate type feeder, belt conveyor, pulverizer, screening machine, batch bin, nutrition regulating agent ingredient
Storehouse, is granulated trimmer, drum-type drying cooling integration equipment, quantitative package machine at stirring mixer;
Biogas residue and stalk are deposited in respectively in biogas residue feed bin 1 and straw bin 2, and biogas residue and stalk are respectively by belt conveyer
It is sent to blend feedstock stockyard 3 and mixes ageing, the mixing after ageing is sent to the feed end in aerobic fermentation pond 4, aerobic hair with forklift
Ferment pond feed end is equipped with movable upender, and aerobic fermentation bottom of pond portion is equipped with bottom of pond and is aerated coil pipe, and bottom of pond is aerated on coil pipe circumference
Equipped with venthole, material after the aerobic fermentation of aerobic fermentation pond discharge end is placed in ageing feed bin 5 by forklift;Use forklift
The material being aged in feed bin is sent to the top hopper of chain-plate type feeder, powder is delivered to by belt conveyor through uniform distribution
Broken 6 feed inlet of machine, the discharge port of pulverizer are connect with the feed end of the first screening machine 7;Oversize is returned through belt conveyor conveying
The feed inlet for being back to pulverizer crushes again;Screenings is sent into batch bin 8 by belt conveyor;Batch bin and nutrition regulating agent are matched
The discharge port of feed bin 9 is connected to the feed inlet of stirring mixer 10, and the discharge port of stirring mixer passes through belt conveyor and makes
The feed inlet connection of grain trimmer 11, the discharge port for being granulated trimmer pass through belt conveyor and drum-type drying cooling integration
The feed inlet of equipment 12 is connected to;The leading portion of drum-type drying cooling integration equipment is connected to 15 entrance of hot air duct, drum-type
The middle section of Drying and cooling integration apparatus is connected to 17 entrance of cold air duct, and drum-type drying cooling integration equipment is equipped with exhaust gas
The discharge port of exhaust apparatus 16, drum-type drying cooling integration equipment is connect with the feed inlet of the second screening machine, the second screening
It is connect respectively by belt conveyor with quantitative package machine 14 on the sieve of machine 13 and under sieve.
The unit of exhausting waste gas includes communicate with each other exhaust pipe and bag filter.
Powder fertilizer can have both been produced using above-mentioned technique or produced granulated fertilizer.
The production technology of powder fertilizer:
(1) fertile raw material sources and mixture are made
The biogas residue that anaerobic fermentation of organisms generates is transported to organic fertilizer fertilizer workshop by belt conveyor after dehydration
Blend feedstock stockyard.According to the needs for making fertile technique, it is necessary to be controlled to the moisture content and its aqueous uniformity of making fertile raw material
System, it is therefore desirable to which the suitable straw after crushed of mixture, stalk mix in biogas residue according to the difference of biogas residue water content
It is completed with process in blend feedstock stockyard, the moisture control of blend feedstock is 60%.
Mixed mode be using biogas residue and stalk layering tiling stack, that is, spread one layer of biogas residue, repave above one layer of crushing straw,
One layer of biogas residue is repaved above, and two kinds of materials replace laying, and the thickness degree of respective laying needs logical according to biogas residue and moisture content of straws
It is specific determining to cross calculating;Material heap size and height can specifically be determined according to site condition.
The mixed mode of raw material is that biogas residue and crushing straw, fermenting agent uniformly mix jointly in pretreatment of raw material, is mixed
It is 1.2m~1.5m that material, which stacks height,.
(2) cloth and aerobic fermentation
Daily to one defective material of fermentation vat cloth, start to lower and upper to be taken in the side in blend feedstock stockyard using forklift
Expect, and be fed separately to several and support in fermentation vat well, equably the feed end of cloth to pond, raw material enters aerobic from now on
Fermentation procedure;Next day carries out stirring operation by movable upender, can further mix raw material during stirring, simultaneously will
Raw material is mobile to fermentation vat discharge end, and after vacating the feed end length that can meet one day cloth doses needs, begins to the same day
Cloth material process;It moves in circles by this process, until material reaches fermentation vat discharge end.So far the fertile raw material of system completes entirely good
Aerobe fermentation period, aerobic fermentation period are generally 10~15 days.Thus the length of feed end and discharge end is respectively aerobic fermentation
The 1/10~1/15 of pond total length.The number of days of fermentation period is determined according to the ingredient of fermentation raw material and feature, important
Be by it is all enter pond raw material achieve the purpose that complete fermentation is good within the aerobic fermentation period.The moisture content control of material after aerobic fermentation
System is 40%.
The width of fermentation vat is 4-5m, is highly 1.6-2m under normal circumstances.The item number and length of fermentation vat, mainly root
It is determined according to site condition, production capacity and according to the fermentation period that material condition determines.
During aerobic fermentation: being aerated coil pipe (being equipped with intensive orderly venthole on aeration tube circumference) to object from bottom of pond
The sufficient fresh air of material supply, to meet the needs of material aerobic fermentation is to oxygen.
Bottom of pond is aerated the selection of the arrangement of mounting means and pipe upper vent hole of coil pipe, quantity and supply gas pressure, mainly
It is determined according to fabric thickness in material condition (including gas permeability), pond.Because in each stage material of aerobic fermentation to oxygen
Demand is different, and sectional quantitative air supply method is taken on fermentation vat length direction.
(3) it discharges and is aged
The material fermented taking-up is sent to from fermentation vat discharge end by ageing area using forklift, is piled respectively by discharging time
It is aged material heap and carries out material ageing.Under normal circumstances, the material for producing powder fertilizer needs to be aged 20 days, material water ratio control after ageing
System is 33%.
(4) it is crushed and sieves
It will be sent in the hopper of chain-plate type feeder top by the material of ageing using forklift, it is defeated by belt through uniform distribution
It send machine to be transported to pulverizer, then crushing rear material is transported to screening machine by belt conveyor and is sieved.Large particle on sieve
Material, which is then sent through pulverizer back to belt conveyor through belt conveyor conveying, to be continued to crush;Under sieve≤2mm material has for qualification
Machine fertilizer raw material, is transported to batch bin through belt conveyor.
(5) ingredient and mixing
Feed proportioning system is equipped with 4 batch bins, in which: 1 is organic fertilizer batch bin by above-mentioned operation output, remaining 3
A is N, P, K auxiliary material storehouse respectively.According to the existing organic fertilizer production standard of country: 1. " organic fertilizer " (NY525-2012), 2. " life
Organic fertilizer " (NY884-2012) 3. " the agricultural control standard of townm refuse " (GB 8172-87), in proportion carry out each component match
Material is transported to stirring mixer by the material that storehouse lower belt conveyer prepares and is stirred mixing, then will be mixed by belt conveyor
Material is transported on two-way sub-material belt conveyor.
(6) powder fertilizer packs
When producing powder fertilizer, the overall process of powder fertilizer production in bulk is completed after above-mentioned ingredient.For convenient for storing, sell
Sell, transport and peasant fertilising, this technique be equipped with powder fertilizer automatic gauge fill packet function, i.e., by two-way sub-material belt conveyor by powder fertilizer
It is transported to dress chartered plane pack, and realizes automatic weighing, automatic dress packet.
The production technology of granulated fertilizer:
The step of making fertile raw material sources and mixture and cloth and aerobic fermentation is identical as powder fertilizer is prepared, and produces the material of granulated fertilizer
It needs to be aged 10 days, material water ratio control is 37% after ageing.
The step of broken and screening and ingredient and mixing, is also identical as preparing for powder fertilizer.
Granulation Drying and cooling:
After N P and K ingredient, powder fertilizer is transported to granulator by two-way sub-material belt conveyor and is pelletized.Again
Granulated fertilizer drum-type drying cooling screening integration apparatus is transported to by belt conveyor to be dried, cool down, sieve.Drying is used
Hot wind is fed by hot-wind inlet pipeline, during the continuous of drum-type drying cooling screening integration apparatus, uniform rotation,
Leading portion by hot wind by granulated fertilizer constantly drying dehumidification, to improve the intensity of granulated fertilizer particle;Middle section by roller tail portion cold wind into
Port introduces cold wind and dehumidifies by granulated fertilizer constantly cooling and further, and the moisture content for making granulated fertilizer reach organic fertilizer production standard is wanted
It asks;Drying and exhaust gas after cooling are discharged by exhaust apparatus, the qualified discharge after exhaust pipe is sent to bag filter dedusting.
Screening and granulated fertilizer dress packet:
Granulated fertilizer after cooling is sieved in the back segment of drum-type drying cooling screening integration apparatus, it is thin that sieve is lower
Granulated fertilizer is granulated fertilizer on sieve, and fills chartered plane and granulated fertilizer dress chartered plane automatic weighing, automatic dress packet by particulate fertilizer respectively.
The above is only a preferred embodiment of the present invention, it is noted that for the ordinary skill people of the art
For member, without departing from the technical principles of the invention, several improvements and modifications can also be made, these improvements and modifications
Also it should be regarded as protection scope of the present invention.
Claims (7)
1. a kind of production technology using anaerobism biogas residue production solid organic fertilizer, which comprises the following steps:
(1) mixture of raw material
After being dehydrated, the moisture content of biogas residue is the biogas residue that anaerobic fermentation of organisms generates by the way that moisture content is added 70~75%
10~20% crushing straw makes the moisture content of blend feedstock 60~65%;The biogas residue and the volume ratio of stalk be 4~
6:1;
Raw material after mixture is deposited in blend feedstock stockyard, be added fermenting agent formed mixing, using turning machine to raw material into
Row mixes well;
(2) cloth and aerobic fermentation of mixing
Mixing after choosing ageing from bottom to top is sent into aerobic fermentation pond, and mixing is first mixed well initial fermentation, next day by
Movable upender is mobile to discharge end by the mixing for being located at feed end, and it is long to vacate the feed end that one day cloth doses of satisfaction needs
Degree, carries out the cloth of a new round, moves in circles, and completes entire fermentation period until material reaches discharge end;
The aerobic fermentation period of mixing is 10~15 days, and the moisture content of material is 40~45% after aerobic fermentation;
(3) after aerobic fermentation material ageing
The material fermented is sent to from the taking-up of fermentation vat discharge end by ageing area using forklift, produces the material aging period of powder fertilizer
It is 20~25 days, the material water ratio after ageing is 30~33%;The material aging period for producing granulated fertilizer is 10~15 days, ageing
Material water ratio is 35~37% afterwards;
(4) preparation of powder fertilizer
By the material after ageing first after pulverizer crushes, it is sent into screening machine and is sieved down, material screening partial size≤2mm;It will sieve
Material after choosing is matched according to standard with nitrogen source, phosphorus source and potassium resource, is stirred, is mixed, pack;Nitrogen source, phosphorus source and potassium resource
There is the content of N P and K in total addition level combination material Central Plains, adds according to the content of produced various criterion organic fertilizer according to calculation amount
Add;
(5) preparation of granulated fertilizer
By the material after ageing first after pulverizer crushes, it is sent into screening machine and is sieved down, material screening partial size≤2mm;It will sieve
Material after choosing is matched according to standard with nitrogen source, phosphorus source and potassium resource, is stirred, is mixed, pack;Mixed material water ratio
It is 34~35%;Adding water to adjust material water ratio is 35~36%, material is sent into granulator, by granule materials after granulation
It is sent into the drying of drum-type drying cooling screening integration apparatus.
2. a kind of production technology using anaerobism biogas residue production solid organic fertilizer according to claim 1, which is characterized in that
The mixed mode of raw material is that biogas residue and crushing straw, fermenting agent uniformly mix jointly in pretreatment of raw material, and mixed material is stacked
Height is 1.2m~1.5m.
3. a kind of production technology using anaerobism biogas residue production solid organic fertilizer according to claim 2, which is characterized in that
The width in the aerobic fermentation pond is 4~5m, is highly 1.6~2m;The aerobic fermentation pond is equipped with feed end and discharge end, into
The length for expecting end and discharge end is respectively the 1/10~1/15 of aerobic fermentation pond total length, and the aerobic fermentation bottom of pond portion is equipped with pond
Bottom is aerated coil pipe, and the circumference of the aeration coil pipe is equipped with intensive orderly venthole, and aerobic fermentation pond is from feed end to discharging
Stomata arrangement, quantity and supply gas pressure on the aeration coil pipe at end are determined according to demand of each stage mixing to oxygen.
4. a kind of production technology using anaerobism biogas residue production solid organic fertilizer according to claim 3, which is characterized in that
The drying of granule materials and granulation process are that the leading portion of drum-type drying cooling screening integration apparatus is hot wind, by granule materials
Drying dehumidification;Middle section is cold wind, by the cooling further dehumidifying of granule materials, guarantees that the moisture content of granule materials is 20~22%;
Back segment sieves granule materials after cooling, 8~12 mesh of screen size.
5. a kind of production system according to claim 1 using biogas residue production solid organic fertilizer, which is characterized in that including
Blend feedstock stockyard, aerobic fermentation pond, ageing feed bin, chain-plate type feeder, belt conveyor, pulverizer, screening machine, ingredient
Storehouse, stirring mixer, is granulated trimmer, drum-type drying cooling integration equipment, quantitative package at nutrition regulating agent batch bin
Machine;
The discharge port of biogas residue feed bin and straw bin is connect with one end of belt conveyer respectively, the belt conveyer other end and mixed
Even material storage yard connection;Forklift is equipped between blend feedstock stockyard and the feed end in aerobic fermentation pond;Aerobic fermentation pond feed end
Equipped with movable upender, aerobic fermentation bottom of pond portion is equipped with bottom of pond and is aerated coil pipe, and bottom of pond is aerated coil pipe circumference and is equipped with venthole,
Forklift is equipped between aerobic fermentation pond discharge end and the top hopper of chain-plate type feeder;The discharge port of chain-plate type feeder passes through
Belt conveyor is connected to feeding hole of pulverizer, and the discharge port of pulverizer is connect with the feed end of the first screening machine;Oversize warp
The feed inlet that belt conveyor conveying is back to pulverizer crushes again;Screenings is sent into batch bin by belt conveyor;Ingredient
The discharge port of storehouse and nutrition regulating agent batch bin is connected to the feed inlet of stirring mixer, and the discharge port of stirring mixer passes through skin
It is connect with conveyer with the feed inlet for being granulated trimmer, the discharge port for being granulated trimmer passes through belt conveyor and drum-type drying
The feed inlet of cooling integration equipment is connected to;The leading portion of drum-type drying cooling integration equipment is connected to hot air duct entrance,
The middle section of drum-type drying cooling integration equipment is connected to cold air duct entrance, among drum-type drying cooling integration equipment
Equipped with unit of exhausting waste gas, the discharge port of drum-type drying cooling integration equipment is connect with the feed inlet of the second screening machine, the
It is connect respectively by belt conveyor with quantitative package machine on the sieve of two screening machines and under sieve.
6. the production system according to claim 5 using biogas residue production solid organic fertilizer, which is characterized in that the exhaust gas
Exhaust apparatus includes communicate with each other exhaust pipe and bag filter.
7. the solid organic fertilizer of production technology preparation according to any one of claims 1 to 4.
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Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110903110A (en) * | 2019-11-25 | 2020-03-24 | 浙江万泰环境工程有限公司 | Quick good oxygen system of becoming fertile of natural pond sediment |
CN111978110A (en) * | 2020-09-03 | 2020-11-24 | 肥城中持十方生物能源有限公司 | Method for preparing granular organic fertilizer |
CN113004102A (en) * | 2021-03-08 | 2021-06-22 | 广州市土根旺生物科技有限公司 | Full water-soluble agate type granular bacterial manure production equipment |
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CN115043678A (en) * | 2022-07-15 | 2022-09-13 | 山东鼎创生物科技有限公司 | Biogas residue solid-state fermentation bio-organic fertilizer and preparation method and application thereof |
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Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104326773A (en) * | 2013-07-22 | 2015-02-04 | 保康沃土生态农业开发有限公司 | Technology for producing biological organic fertilizer |
CN204265657U (en) * | 2014-11-11 | 2015-04-15 | 巫溪县明申肥业有限公司 | Organic fertilizer production line |
CN106431555A (en) * | 2016-08-12 | 2017-02-22 | 东北师范大学 | Method for preparing methane and organic compound fertilizer from plant straws |
CN109438066A (en) * | 2018-12-11 | 2019-03-08 | 广东巴斯德环境科技有限公司 | A kind of processing method and technique of biogas residue |
-
2019
- 2019-07-05 CN CN201910603653.1A patent/CN110407622A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104326773A (en) * | 2013-07-22 | 2015-02-04 | 保康沃土生态农业开发有限公司 | Technology for producing biological organic fertilizer |
CN204265657U (en) * | 2014-11-11 | 2015-04-15 | 巫溪县明申肥业有限公司 | Organic fertilizer production line |
CN106431555A (en) * | 2016-08-12 | 2017-02-22 | 东北师范大学 | Method for preparing methane and organic compound fertilizer from plant straws |
CN109438066A (en) * | 2018-12-11 | 2019-03-08 | 广东巴斯德环境科技有限公司 | A kind of processing method and technique of biogas residue |
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110903110A (en) * | 2019-11-25 | 2020-03-24 | 浙江万泰环境工程有限公司 | Quick good oxygen system of becoming fertile of natural pond sediment |
CN111978110A (en) * | 2020-09-03 | 2020-11-24 | 肥城中持十方生物能源有限公司 | Method for preparing granular organic fertilizer |
CN113004102A (en) * | 2021-03-08 | 2021-06-22 | 广州市土根旺生物科技有限公司 | Full water-soluble agate type granular bacterial manure production equipment |
CN113004102B (en) * | 2021-03-08 | 2022-07-29 | 广州天适立农生态农业发展有限公司 | Full water-soluble agate type granular bacterial manure production equipment |
CN114057514A (en) * | 2021-12-01 | 2022-02-18 | 中国市政工程华北设计研究总院有限公司 | Dry anaerobic biogas residue three-stage dehydration-based powder fertilizer production system and powder fertilizer production method thereof |
CN115043678A (en) * | 2022-07-15 | 2022-09-13 | 山东鼎创生物科技有限公司 | Biogas residue solid-state fermentation bio-organic fertilizer and preparation method and application thereof |
CN115197000A (en) * | 2022-07-25 | 2022-10-18 | 湖北延创环保科技有限责任公司 | Energy-saving organic fertilizer production process |
CN115197000B (en) * | 2022-07-25 | 2024-05-17 | 湖北延创环保科技有限责任公司 | Energy-saving organic fertilizer production process |
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