CN106431555A - Method for preparing methane and organic compound fertilizer from plant straws - Google Patents

Method for preparing methane and organic compound fertilizer from plant straws Download PDF

Info

Publication number
CN106431555A
CN106431555A CN201610662167.3A CN201610662167A CN106431555A CN 106431555 A CN106431555 A CN 106431555A CN 201610662167 A CN201610662167 A CN 201610662167A CN 106431555 A CN106431555 A CN 106431555A
Authority
CN
China
Prior art keywords
fermentation
straw
time
temperature
less
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
Application number
CN201610662167.3A
Other languages
Chinese (zh)
Inventor
徐建玲
王汉席
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Northeastern University China
Northeast Normal University
Original Assignee
Northeast Normal University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Northeast Normal University filed Critical Northeast Normal University
Priority to CN201610662167.3A priority Critical patent/CN106431555A/en
Publication of CN106431555A publication Critical patent/CN106431555A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05BPHOSPHATIC FERTILISERS
    • C05B17/00Other phosphatic fertilisers, e.g. soft rock phosphates, bone meal
    • CCHEMISTRY; METALLURGY
    • C12BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12PFERMENTATION OR ENZYME-USING PROCESSES TO SYNTHESISE A DESIRED CHEMICAL COMPOUND OR COMPOSITION OR TO SEPARATE OPTICAL ISOMERS FROM A RACEMIC MIXTURE
    • C12P5/00Preparation of hydrocarbons or halogenated hydrocarbons
    • C12P5/02Preparation of hydrocarbons or halogenated hydrocarbons acyclic
    • C12P5/023Methane
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Abstract

The invention discloses a method for preparing methane and organic compound fertilizer from plant straws. The method comprises the following steps of: grinding plant straws, then stirring and mixing with domesticated sludge and human and animal excreta for primary fermentation; after the primary fermentation is completed, mixing the fermented biogas residues with plant ash and bone powder, and adding plant straws for secondary decomposing and fermentation; after secondary decomposing and fermentation is completed, screening the leavening, mixing the overtails with plant straws and adding into the biogas residues for secondary decomposing fermentation, performing granulation to the undersize, drying and packaging. The method is used for preparing the methane and an organic compound fertilizer, solid waste resources can be fully utilized, the utilization cost is low, the effect is fast, the entire recycling of solid wastes can be realized, and the economic and environment benefits are obvious.

Description

A kind of method that straw prepares biogas and compoiste fertilizer
Technical field
The present invention relates to a kind of method that straw prepares biogas and compoiste fertilizer, belong to solid recycling skill Art field.
Background technology
In the last few years, severe contamination air after straw burns, if recycling, not only solves air pollution and asks Topic, and energy shortage problem can be alleviated as resource.The purposes of current straw mainly has three aspects, and one is to make For biomass power generation, two is as fuel utilization heat energy, and three is to prepare biogas and fertilizer as fermentation raw material.Compare it Under, preparing biogas and fertilizer as fermentation raw material is that the horizontal highest of current recycling is a kind of, not only realizes waste Complete resource, and do not produce secondary pollution, economic benefit and obvious environment benefit.
It is to first pass through the mud one time fermentation preparation after adding domestication that straw prepares biogas and the principle of fertilizer Biogas, the biogas residue after preparation adds straw, plant ash and bone meal to carry out secondary compost fermentation and prepare fertilizer, secondary compost The straw that fermentation adds does not need to pulverize, and the completely straw that do not ferment on a small quantity returns the fertile fermentation of system by screening Pond.The method low cost, biogas output is big, and the fertilizer fertilizer efficiency of preparation is high.
Prepare biogas at present and the patent of fertilizer includes:Produce fertilizer using fermentation tunnel Rapid Fermentation feces of livestock and poultry Method (201511030820.6), a kind of preparation method (201510959405.2) of rabbit dejection organic fertilizer, a kind of vinegar groove earthworm The preparation method (201510951429.3) of earthworm excrement anti-soil-borne disease slow-releasing granules fertilizer, utilize potato residues and animal dung Just the method (201510785700.0) of organic compound fertilizer, produce the apparatus and method of biological organic fertilizer using excrement in septic tank (201510766980.0) a kind of, technique of utilization animal fill and excrement production fertilizer (201510746406.9), a kind of use excrement, stalk produce soluble fertilizer method (201510707613.3), a kind of with High-moisture feces of livestock and poultry produces the fermentation system of fertilizer and fermentation process (201510667261.3), utilizes livestock manure fermented Produce multi-element biological fertilizer (201510462478.0), a kind of method of feces of livestock and poultry hamlessizing technology fertilizer (201510344607.6), the method preparing water conservation biological organic fertilizer using high-moisture fowl and animal excrement (201510260833.6) a kind of fertilizer that, utilization animal wastes make and its preparation technology (201510137802.1), one Kind pig manure, chicken manure mixing stool detection fertilizer (201410255921.2), a kind of utilization stalk directly make fertilizer The Straw manures (201610131358.7) of method and preparation, stalk harmless conversion fertilizer producing equipment (201520040808.2), A kind of utilization straw preparation water-soluble ecology organic carbon fertile method (201510965747.5), a kind of compoiste fertilizer Preparation method (201510298512.5), using stalk fast composting system (201420044634.2) etc..But above-mentioned patent because There is complex process, high cost, technical merit is low and is also easy to produce one or more shortcoming such as secondary pollution, range is subject to very Big limitation, application effect is inconspicuous, Difficulty.
Therefore, exploitation one is simple and practical, workable, particularly effectively utilizes straw waste, realizes useless The complete resource of thing, will be significant.
Content of the invention
It is an object of the invention to provide a kind of method that straw prepares biogas and compoiste fertilizer, improve straw Recycling level, reduction prepares the cost of biogas and fertilizer.
The technical scheme is that and be achieved in that, a kind of method that straw prepares biogas and compoiste fertilizer, The method includes procedure below:Straw stirs to mix and carries out one time fermentation with the mud of domestication and human and animal excreta after pulverizing; After the completion of one time fermentation, the biogas residue of fermentation is mixed with plant ash and bone meal, be simultaneously introduced straw and carry out secondary compost and send out Ferment;After the completion of secondary compost fermentation, fermentate is sieved, carry out secondary in oversize and straw mixing addition biogas residue Compost fermentation, screenings is granulated, and packs after drying.
Described straw pulverizes the of length no more than 8cm after processing;Described mud adopts the dirt of sewage treatment plant It is desirable to sludge heavy-metal content is less than existing national standards requirement, the domestication time is 7~14 to the bed mud of mud or rivers and lakes My god.
The biogas that described one time fermentation produces is conveyed to user after carrying out purified treatment, and marsh gas purifying processing method is to adopt Sodium carbonate liquor or activated carbon with saturation;The mixture ratio of described one time fermentation raw material is straw:Mud:People and animals Excrement=0.45~0.65:0.15~0.25:0.15~0.45, this ratio is the ratio of dry material;Described one time fermentation mistake Cheng Zhong, takes biogas slurry using pumping, is recirculated back to flow to fermentation vat and carries out stirring of surging, daily start pump circulation once, open every time Open 5~10 minutes.
In described secondary compost fermentation, material ratio is biogas residue:Bone meal:Plant ash:Straw=1:0.07~ 0.15:0.05~0.12:0.45~0.55, this ratio is the ratio of dry material;Straw add first for fresh plant Thing stalk, later for the mixture of oversize and the new fresh plant stalk adding;Add in secondary compost fermentation mixture and send out Ferment agent, the addition of leavening is 100~200 g ton, by adding in bone meal, adds secondary compost to send out when fermentation starts In ferment mixture;Described secondary compost fermentation mixture starts water content control when fermenting 55%~65%;Compost height Summer controls in 0.6~1.0m, and winter controls in 0.8~1.6m;Adopt film or straw screen or mat to cover during fermentation, treat internal temperature liter During to 25 DEG C, covering is opened, summer starts a turning when temperature is raised to more than 45 DEG C, winter temperature be raised to 55 DEG C with Started a turning when upper, turning need to be carried out later when temperature reaches more than 60 DEG C;Described leavening living bacteria count >=200 hundred million/gram.
Described screening, the aperture using screen cloth is 10~20mm;After described granulation drying, its water content is less than 15%;Packaging is using plastic bag sealing packaging.
The described one time fermentation termination time is less than the 40% of maximum gas production, and one time fermentation temperature is not less than 15 DEG C; The time of secondary compost fermentation is 10~20 days, and fermentation terminates the previous day control temperature and is more than 70 DEG C, and the time is little no less than 3 When.
The sodium carbonate liquor of described purified treatment or activated carbon, when total absorptivity is less than 70%, need to be processed;Right Sodium carbonate liquor processing method is to heat under the conditions of temperature is 50~80 DEG C, and the heat time is 20~30 minutes;To activated carbon Processing method be under 80~100 DEG C of temperature conditionss heating, the heat time be 10~20 minutes.
The fresh plant stalk that described secondary compost fermentation adds, is rolled, rolling contact is before addition 100~200kPa, stalk laying depth is 100~200mm, rolls 3~5 times;After fermentation ends, fermentation mixture temperature is low In 40 DEG C, add bacillus subtilis can prepare bio-bacterial manure.
The positive effect of the present invention is to make full use of solid waste, realizes the complete resource of solid waste, the party Method is simple, low cost, instant effect, economic benefit and obvious environment benefit.
Brief description
Fig. 1 is the process flow diagram of the present invention.
Specific embodiment
The present invention is further illustrated below in conjunction with the accompanying drawings
Embodiment 1:Prepare biogas and compoiste fertilizer with maize straw
As shown in figure 1, this technical process includes:Mixed with the mud of domestication and human and animal excreta stirring after corn straw smashing Conjunction carries out one time fermentation;After the completion of one time fermentation, the biogas residue of fermentation is mixed with plant ash and bone meal, is simultaneously introduced maize straw Carry out secondary compost fermentation;After the completion of secondary compost fermentation, fermentate is sieved, oversize and maize straw mixing add Carry out secondary compost fermentation in biogas residue, screenings is granulated, pack after drying.
Straw pulverizes the of length no more than 8cm after processing, and mud adopts the mud of sewage treatment plant it is desirable to mud weight Tenor is less than existing national standards and requires, and the domestication time is 7 days.
The biogas that one time fermentation produces is conveyed to user after carrying out purified treatment, and marsh gas purifying processing method is to adopt saturation Sodium carbonate liquor;The mixture ratio of one time fermentation raw material is straw:Mud:Human and animal excreta=0.45:0.15: 0.40, this ratio is the ratio of dry material;During one time fermentation, biogas slurry is taken by pumping, be recirculated back to flow to fermentation vat, real Existing agitating function, daily startup pump circulation once, is opened 5 minutes every time.
Secondary compost fermentation compound dry material ratio is biogas residue:Bone meal:Plant ash:Straw=1:0.07:0.05: 0.45;Straw add first for fresh straw, later for oversize and the new fresh plant stalk adding Mixture;Leavening is added, the addition of leavening is 200 g ton, by adding bone meal in secondary compost fermentation mixture In, add in secondary compost fermentation mixture when fermentation starts;Described secondary compost fermentation mixture starts containing when fermenting Water rate control is 55%~65%;Compost summer height is 1.0m, and winter height is 1.6m;Adopt film to cover during fermentation, treat When internal temperature is raised to 25 DEG C, covering is opened, summer starts a turning, winter temperature when temperature is raised to more than 45 DEG C Start a turning when being raised to more than 55 DEG C, turning need to be carried out later when temperature reaches more than 60 DEG C;Described leavening Living bacteria count >=20,000,000,000/gram, leavening adopts the potent type organic fertilizer fermentation that Shandong Gao Long bio tech ltd produces Agent.
The aperture of the sieve aperture that screening adopts is 10~20mm, and after granulation drying, water content is less than 15%, and packaging adopts plastics Bag hermetic package.
The one time fermentation termination time is less than the 40% of maximum gas production, and one time fermentation temperature is not less than 15 DEG C;Secondary heap The time of fertile fermentation is 20 days, and fermentation termination the previous day controls temperature to be more than 70 DEG C, and the time is no less than 3 hours.
The sodium carbonate liquor of purified treatment, when total absorptivity is less than 70%, is processed;To sodium carbonate liquor process side Method is to heat under the conditions of temperature is 50~80 DEG C, and the heat time is 20 minutes.
The fresh plant stalk that secondary compost fermentation adds, is rolled before addition, and rolling contact is 100kPa, Stalk laying depth is 100mm, rolls 3 times;After fermentation ends, fermentation mixture temperature is less than 40 DEG C, adds withered grass gemma Bacillus can prepare bio-bacterial manure.
Embodiment 2:Prepare biogas and compoiste fertilizer with straw
As shown in figure 1, preparing biogas and fertilizer according to technological process, straw is pulverized of length no more than after processing 8cm, mud adopts the bed mud in river, and the domestication time is 14 days.
Biogas adopts active carbon purifying, and the mixture dry material ratio of one time fermentation raw material is straw:Mud:People and animals Excrement=0.65:0.15:0.20, daily startup pump circulation once, is opened 10 minutes every time.
In secondary compost fermentation, mixture dry material ratio is biogas residue:Bone meal:Plant ash:Straw=1:0.15: 0.12:0.55;In secondary compost fermentation mixture, the addition of leavening is 100 g ton, by adding in bone meal, in fermentation Add during beginning in secondary compost fermentation mixture;Secondary compost fermentation mixture starts water content control when fermenting 55% ~65%;Compost height summer controls in 0.6m, and winter controls in 0.8m;Adopt straw screen or mat to cover during fermentation, treat internal temperature liter During to 25 DEG C, covering is opened, summer starts a turning when temperature is raised to more than 45 DEG C, winter temperature be raised to 55 DEG C with Started a turning when upper, turning need to be carried out later when temperature reaches more than 60 DEG C;Leavening living bacteria count >=200 Hundred million/gram, leavening adopts the potent type organic fertilizer fermentation agent that Shandong Gao Long bio tech ltd produces.
The aperture of screening sieve used is 10~20mm, and after granulation drying, its water content is less than 15%, and packaging adopts polybag Pack.
The one time fermentation termination time is less than the 40% of maximum gas production, and one time fermentation temperature is not less than 15 DEG C;Secondary heap The time of fertile fermentation is 10 days, and fermentation termination the previous day controls temperature to be more than 70 DEG C, and the time is no less than 3 hours.
The fresh plant stalk that secondary compost fermentation adds, is rolled before addition, and rolling contact is 200kPa, Stalk laying depth is 200mm, rolls 5 times.
The activated carbon of purified treatment, when total absorptivity is less than 70%, is processed;To the processing method of activated carbon be Temperature heats under the conditions of being 80~100 DEG C, and the heat time is 10 minutes.
Specific embodiment disclosed above is disclosed to the present invention, but the present invention is not limited to this, any this area The thinkable change of technical staff, in design philosophy and scope without departing from the present invention, what the present invention was carried out various changes Dynamic, all should be within protection scope of the present invention.

Claims (8)

1. the method that a kind of straw proposed by the invention prepares biogas and compoiste fertilizer, the method includes following mistake Journey:Straw stirs to mix and carries out one time fermentation with the mud of domestication and human and animal excreta after pulverizing;After the completion of one time fermentation, will The biogas residue of fermentation is mixed with plant ash and bone meal, is simultaneously introduced straw and carries out secondary compost fermentation;Secondary compost fermentation is complete After one-tenth, fermentate is sieved, carry out secondary compost fermentation in oversize and straw mixing addition biogas residue, screenings enters Row granulation, packs after drying.
2. straw according to claim 1 pulverizes the of length no more than 8cm after processing;Described mud adopts sewage The bed mud of the mud for the treatment of plant or rivers and lakes is it is desirable to sludge heavy-metal content is less than existing national standards requirement, during domestication Between be 7~14 days.
3. the biogas that one time fermentation according to claim 1 produces is conveyed to user, marsh gas purifying after carrying out purified treatment Processing method is the sodium carbonate liquor or activated carbon using saturation;The mixture ratio of described one time fermentation raw material is plant straw Stalk:Mud:Human and animal excreta=0.45~0.65:0.15~0.25:0.15~0.45, this ratio is the ratio of dry material;Described One time fermentation during, biogas slurry is taken using pumping, is recirculated back to flow to fermentation vat and carries out stirring of surging, start pump circulation daily Once, open 5~10 minutes every time.
4. in secondary compost fermentation according to claim 1, material ratio is biogas residue:Bone meal:Plant ash:Straw= 1:0.07~0.15:0.05~0.12:0.45~0.55, this ratio is the ratio of dry material;What straw added first is Fresh straw, later for the mixture of oversize and the new fresh plant stalk adding;Secondary compost fermentation mixture Middle addition leavening, the addition of leavening is 100~200 g ton, by adding in bone meal, adds two when fermentation starts In secondary compost fermentation mixture;Described secondary compost fermentation mixture starts water content control when fermenting 55%~65%; Compost height summer controls in 0.6~1.0m, and winter controls in 0.8~1.6m;Adopt film or straw screen or mat to cover during fermentation, treat interior When portion's temperature is raised to 25 DEG C, covering is opened, summer starts a turning, winter temperature liter when temperature is raised to more than 45 DEG C Start a turning during to more than 55 DEG C, turning need to be carried out later when temperature reaches more than 60 DEG C;Described leavening has Effect viable count >=20,000,000,000/gram.
5. screening according to claim 1, the aperture using screen cloth is 10~20mm;After described granulation drying, it contains The water yield is less than 15%;Packaging is using plastic bag sealing packaging.
6. the one time fermentation termination time according to claim 1 is less than the 40% of maximum gas production, one time fermentation temperature It is not less than 15 DEG C;The time of secondary compost fermentation is 10~20 days, and fermentation terminates the previous day control temperature and is more than 70 DEG C, and when Between be no less than 3 hours.
7. the sodium carbonate liquor of purified treatment according to claim 3 or activated carbon, when total absorptivity is less than 70%, needs Processed;It is to heat under the conditions of temperature is 50~80 DEG C to sodium carbonate liquor processing method, the heat time is 20~30 points Clock;Processing method to activated carbon is heating under 80~100 DEG C of temperature conditionss, and the heat time is 10~20 minutes.
8. the fresh plant stalk that the secondary compost fermentation according to claim 1 and 4 adds, is rolled before addition, Rolling contact is 100~200kPa, and stalk laying depth is 100~200mm, rolls 3~5 times;After fermentation ends, send out Ferment mixture temperature is less than 40 DEG C, adds bacillus subtilis can prepare bio-bacterial manure.
CN201610662167.3A 2016-08-12 2016-08-12 Method for preparing methane and organic compound fertilizer from plant straws Pending CN106431555A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610662167.3A CN106431555A (en) 2016-08-12 2016-08-12 Method for preparing methane and organic compound fertilizer from plant straws

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610662167.3A CN106431555A (en) 2016-08-12 2016-08-12 Method for preparing methane and organic compound fertilizer from plant straws

Publications (1)

Publication Number Publication Date
CN106431555A true CN106431555A (en) 2017-02-22

Family

ID=58184832

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610662167.3A Pending CN106431555A (en) 2016-08-12 2016-08-12 Method for preparing methane and organic compound fertilizer from plant straws

Country Status (1)

Country Link
CN (1) CN106431555A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106905078A (en) * 2017-04-01 2017-06-30 南开大学 A kind of preparation method of low-cost high-efficiency organic fertilizer
CN107117786A (en) * 2017-06-29 2017-09-01 重庆市万源禽蛋食品有限公司 Plant's dejecta treatment method and system
CN108569768A (en) * 2017-08-04 2018-09-25 东北师范大学 A kind of method that maize straw prepares artificial swamp matrix
CN108794230A (en) * 2018-09-26 2018-11-13 汪添法 A kind of safe and efficient microbial organic fertilizer and preparation method thereof
CN110407622A (en) * 2019-07-05 2019-11-05 江苏亿金环保科技有限公司 A kind of production technology using anaerobism biogas residue production solid organic fertilizer
CN113277897A (en) * 2021-06-04 2021-08-20 海南瑞民农业科技有限公司 Special fertilizer for high yield of coconuts
CN114456015A (en) * 2022-02-15 2022-05-10 江苏麦客生物科技有限公司 Efficient production method for preparing organic mixed fertilizer by organic biological fermentation

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103204718A (en) * 2013-04-28 2013-07-17 么向和 Comprehensive utilization method of livestock and poultry manures and crop straw resources
CN104561121A (en) * 2015-02-04 2015-04-29 河南省高新技术实业总公司 Method for preparing marsh gas by anaerobic fermentation of agricultural straws

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103204718A (en) * 2013-04-28 2013-07-17 么向和 Comprehensive utilization method of livestock and poultry manures and crop straw resources
CN104561121A (en) * 2015-02-04 2015-04-29 河南省高新技术实业总公司 Method for preparing marsh gas by anaerobic fermentation of agricultural straws

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106905078A (en) * 2017-04-01 2017-06-30 南开大学 A kind of preparation method of low-cost high-efficiency organic fertilizer
CN107117786A (en) * 2017-06-29 2017-09-01 重庆市万源禽蛋食品有限公司 Plant's dejecta treatment method and system
CN108569768A (en) * 2017-08-04 2018-09-25 东北师范大学 A kind of method that maize straw prepares artificial swamp matrix
CN108569768B (en) * 2017-08-04 2021-06-18 东北师范大学 Method for preparing constructed wetland substrate from corn straws
CN108794230A (en) * 2018-09-26 2018-11-13 汪添法 A kind of safe and efficient microbial organic fertilizer and preparation method thereof
CN110407622A (en) * 2019-07-05 2019-11-05 江苏亿金环保科技有限公司 A kind of production technology using anaerobism biogas residue production solid organic fertilizer
CN113277897A (en) * 2021-06-04 2021-08-20 海南瑞民农业科技有限公司 Special fertilizer for high yield of coconuts
CN114456015A (en) * 2022-02-15 2022-05-10 江苏麦客生物科技有限公司 Efficient production method for preparing organic mixed fertilizer by organic biological fermentation

Similar Documents

Publication Publication Date Title
CN106431555A (en) Method for preparing methane and organic compound fertilizer from plant straws
CN102173507B (en) Method for comprehensively recycling fecal sewage of large-scale livestock and poultry farms and farmland crop straws
CN104355707B (en) Dry and wet simultaneous digestion processes the method for fowl and animal excrement and straw
CN102584364B (en) Biologic organic fertilizer and preparation method thereof
CN102336508B (en) Method and system for quickly dehydrating and recycling municipal sewage sludge
CN103265154B (en) Resource utilization and comprehensive treatment process for sewage and manure generated during cultivation
CN106190927B (en) A kind of bacterial strain and its application for sludge high temperature compost
CN102268462A (en) Integrated utilization method of agricultural and pastoral waste
CN105755052A (en) Town multi-element organic waste for preparing biogas and method for preparing biogas from same
CN102925494A (en) Method for producing methane by dry fermentation of beast and bird wastes and crop straws
CN102603383B (en) Production equipment and preparation method of slow-release bio-organic fertilizer
CN101338273A (en) Home device and method for producing methane by dry-type fermentation of stalks
CN108002954A (en) A kind of agricultural wastes anaerobic-aerobic balances fermentation process
CN103435154A (en) Method for recycling contaminants of large-scale livestock and poultry farm
CN106187341A (en) Cultivation Excreta three grade fermemtation method
CN104193426A (en) Method and equipment for fermenting and drying excrement in one step
CN102674651A (en) Feces treatment system and feces treatment method with methane project as link
CN109055189A (en) The high-effect biogas production device of one pot type of stalk soiled litter continuous dry fermentation and technique
CN205576158U (en) Two stage of solid -liquid anaerobic fermentation device
CN104163501B (en) A kind of method of utilizing complex microorganism nest to process liquid dung
CN103461281B (en) Based on the method for the ecological treatment market of farm produce rubbish of earthworm digestion
CN203613189U (en) Multiple material anaerobic dry fermentation system using straw as main raw material
CN108004132A (en) A kind of anaerobic ferment devices of recyclable microorganism ageing hydro-thermal charcoal and the recovery method of microorganism ageing hydro-thermal charcoal
CN111218481A (en) Method for combined fermentation of organic garbage and sludge
CN109328537A (en) A kind of ecological farm village that waste material recycles

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20170222

RJ01 Rejection of invention patent application after publication