CN102515907A - Aerobic composting method for organic perishable garbage - Google Patents

Aerobic composting method for organic perishable garbage Download PDF

Info

Publication number
CN102515907A
CN102515907A CN2011104573507A CN201110457350A CN102515907A CN 102515907 A CN102515907 A CN 102515907A CN 2011104573507 A CN2011104573507 A CN 2011104573507A CN 201110457350 A CN201110457350 A CN 201110457350A CN 102515907 A CN102515907 A CN 102515907A
Authority
CN
China
Prior art keywords
phase
thoroughly decomposed
heap
days
turning
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
CN2011104573507A
Other languages
Chinese (zh)
Inventor
杨章印
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.)
Guangzhou Shicheng Management Technology Research Center
Original Assignee
Guangzhou Shicheng Management Technology Research Center
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 Guangzhou Shicheng Management Technology Research Center filed Critical Guangzhou Shicheng Management Technology Research Center
Priority to CN2011104573507A priority Critical patent/CN102515907A/en
Publication of CN102515907A publication Critical patent/CN102515907A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Fertilizers (AREA)

Abstract

The invention aims to provide an aerobic composting method for organic perishable garbage. The method comprises the following steps: adding effective microorganism (EM) strains; crushing and mixing uniformly; forming a pile; entering a first composting period; turning the pile; entering a second composting period; sieving; and entering a later composting period so as to obtain the initial fertilizer. According to the method, the perishable garbage is utilized completely, and the perishable garbage is decomposed into the initial fertilizer according with the national standard by simple methods of composting, turning the materials and the like. Due to proper ventilation, pile-turning time and two-stage composting period, no odor and flies exist in the composting process, and the popularization and the application are more convenient.

Description

A kind of aerobic compost method of organic perishable rubbish
Technical field
The present invention relates to a kind of treatment process of organic waste, specifically the aerobic compost method of organic perishable rubbish.
Background technology
The three big problems that Modern World faces: food problems, environmental problem and energy problem.We can say that the solution of these three big problems is all relevant with mikrobe, with regard to feed; Development along with livestock industry production; Guarantee that the essential protein fodder of domestic animal more and more lacks, need to solve the present situation of China's feed protein wretched insufficiency, actively utilize renewable resource; Utilizing the waste material of various agricultural byproducts processings to produce feedstuff protein, is an important channel.Estimate that according to the parties concerned there are 1,000 hundred million tons of cellulose resource in the whole world every year approximately, China has 5,000,000,000 tons approximately, and wherein agricultural crop straw (table straw, straw, corn stalk etc.) just reaches about 500,000,000 tons.What these agricultural crop straws can be used for silage is minority, and great majority are as fuel and fertilizer, even also adopt traditional direct feeding method as the sub-fraction of feed, digestive utilization ratio is very low more.If stalk is carried out microbiological treatment, or the physics and chemistry processing, or comprehensive treating process, then can improve the digestibility of animal greatly.Wherein, the microbiological treatment technology, noticeable especially, the whole world is all making great efforts to explore further investigation, and has obtained remarkable progress.
Summary of the invention
The present invention provides a kind of aerobic compost method of organic perishable rubbish in order to solve the defective of above-mentioned prior art.
Technical solution of the present invention has following steps:
A, fragmentation are mixed
The perishable rubbish of about 10t one car was crushed to the sieve mesh that can cross 1.2cm * 1.2cm in 3-5 hour; Get into aerobic fermentation chamber then; And in aerobic fermentation chamber, add EM (useful microbe crowd) bacterial classification; Abundant mixing, the C/N ratio of regulating perishable rubbish is at 25 ~ 35:1, and water ratio is 50 ~ 70% weight percents;
B, in heaps
The perishable rubbish that obtains behind per two car mixings with the A step is a pile body unit; 4 ~ 8 forced-ventilation pipes of uniform distribution in the heap body; Said waste height is less than 2 meters, and bottom width is less than 5 meters, and the heap surface is carried out and covered 10 ~ 20cm oversize or semi-mature material; Ventpipe communicates with aeration equipment, is provided with TM in the heap body;
C, first becomes thoroughly decomposed the phase
Perishable rubbish after the B step is in heaps was first to become thoroughly decomposed the phase in 10 ~ 15 days, and every day at upper and lower noon is respectively detected heap temperature once during this; Before the said heap temperature to 60 °, ventilate twice every day, each about 30 minutes, heap temperature extended to 30 ~ 50 minutes at 60 ° ~ 75 ° aeration time, control heap body water ratio 50 ~ 70% weight percents;
D, turning
Carry out the turning first time in the time of 10 ~ 15 days in heaps, heap is stopped the surface after the turning does not need to carry out again and covers the sieve thing, regulates water ratio 50 ~ 70% weight percents;
E, second becomes thoroughly decomposed the phase
For the first time after the turning 15 ~ 20 days be second to become thoroughly decomposed the phase; Every day at upper and lower noon is respectively detected heap temperature once during this, through long-time ventilation or turning in 2 ~ 3 days once, and to make the control heap temperature less than 75 °; Preceding 10 days through the not moisturizing of only ventilating after 50 ~ 60%, 10 days of moisturizing control water ratio;
F, screening
Second becomes thoroughly decomposed the heap body of phase through the screen cloth of 1.2cm * 1.2cm, tells top sieve thing and sieve thing down, and the top sieve thing is used to pile body to be carried out lid or make addition material, becomes thoroughly decomposed the phase after the following sieve thing entering;
G, after become thoroughly decomposed the phase
Under sieve and become thoroughly decomposed the phase after thing gets into, after become thoroughly decomposed the phase less than 30 days, met " townm refuse agricultural standards " composting production (GB8172-87) at last.
Below, enumerate embodiment and comparative example specifies the present invention, but the present invention does not receive any qualification of these embodiment.
The invention has the advantages that and make full use of perishable rubbish; Through simple means such as compost stirrings is the first fertilizer of National standard with perishable garbage decomposition; Because suitable ventilation, turning time and two sections become thoroughly decomposed the phase, composting process is destitute of smell does not have fly, is convenient to promote and use.
Embodiment 1
A, fragmentation are mixed
The perishable rubbish of about 10t one car was crushed to the sieve mesh that can cross 1.2cm * 1.2cm in 3 hours; Get into aerobic fermentation chamber then; And in aerobic fermentation chamber, add the EM-1 type bacterial classification of Guangzhou Bioisystech Co., Ltd of benefit nation; Abundant mixing, the C/N ratio of regulating perishable rubbish is at 25:1, and water ratio is 50% weight percent;
B, in heaps
The perishable rubbish that obtains behind per two car mixings with the A step is a pile body unit, 4 forced-ventilation pipes of uniform distribution in the heap body, and said waste height is less than 2 meters; Bottom width is less than 5 meters; The heap surface is carried out and is covered the 10cm semi-mature material, and ventpipe communicates with aeration equipment, is provided with TM in the heap body;
C, first becomes thoroughly decomposed the phase
Perishable rubbish after the B step is in heaps was first to become thoroughly decomposed the phase in 10 days, and every day at upper and lower noon is respectively detected heap temperature once during this; Before the said heap temperature to 60 °, ventilate twice every day, each about 30 minutes, heap temperature extended to 30 minutes at 60 ° of aeration time, control heap body water ratio 50% weight percent;
D, turning
Carry out the turning first time in the time of 10 days in heaps, heap is stopped the surface after the turning does not need to carry out again and covers the sieve thing, regulates water ratio 50% weight percent;
E, second becomes thoroughly decomposed the phase
For the first time after the turning 15 days be second to become thoroughly decomposed the phase, every day at upper and lower noon is respectively detected heap temperature once during this, and by long-time ventilation, making the control heap temperature less than 75 °, preceding 10 days by the not moisturizing of only ventilating after 50%, 10 day of moisturizing control moisture content;
F, screening
Second becomes thoroughly decomposed the heap body of phase through the screen cloth of 1.2cm * 1.2cm, tells top sieve thing and sieve thing down, and the top sieve thing is used to pile body to be carried out lid or make addition material, becomes thoroughly decomposed the phase after the following sieve thing entering;
G, after become thoroughly decomposed the phase
Under sieve and become thoroughly decomposed the phase after thing gets into, after become thoroughly decomposed the phase less than 30 days, met " townm refuse agricultural standards " composting production (GB8172-87) at last.
Embodiment 2
With embodiment 1, be perishable refuse breaking 5 hours in the described A step, C/N ratio is adjusted to 35:1, and water ratio is 70% weight percent; 8 forced-ventilation pipes of B step heap body uniform distribution, the debugging of heap body is 1.5 meters, and bottom width is 4 meters, and the heap surface is carried out and is covered the 20cm oversize; C step the first phase of becoming thoroughly decomposed is 15 days, extends to 40 minutes when heap temperature to 65 is spent, control heap body water ratio 60% weight percent; The D step is turning for the first time in the time of 14 days in heaps, regulates water ratio 70% weight percent; After the turning for the first time of E step 20 days be second to become thoroughly decomposed the phase, turning in 3 days once, moisturizing in preceding 10 days control water ratio 60%.
Embodiment 3
With embodiment 1, be perishable refuse breaking 4 hours in the described A step, C/N ratio is adjusted to 30:1, and water ratio is 60% weight percent; 6 forced-ventilation pipes of B step heap body uniform distribution, the debugging of heap body is 1 meter, and bottom width is 3 meters, and the heap surface is carried out and is covered the 15cm oversize; C step the first phase of becoming thoroughly decomposed is 13 days, extends to 50 minutes when heap temperature to 75 is spent, control heap body water ratio 70% weight percent; The D step is turning for the first time in the time of 15 days in heaps, regulates water ratio 60% weight percent; After the turning for the first time of E step 17 days be second to become thoroughly decomposed the phase, turning in 2 days once, moisturizing in preceding 10 days control water ratio 55%.

Claims (1)

1. the aerobic compost method of organic perishable rubbish is characterized in that following steps are arranged:
A, fragmentation are mixed
The perishable rubbish of about 10t one car was crushed to the sieve mesh that can cross 1.2cm * 1.2cm in 3-5 hour; Get into aerobic fermentation chamber then, and in aerobic fermentation chamber, add the EM bacterial classification, fully mixing; The C/N ratio of regulating perishable rubbish is at 25 ~ 35:1, and water ratio is 50 ~ 70% weight percents;
B, in heaps
The perishable rubbish that obtains behind per two car mixings with the A step is a pile body unit; 4 ~ 8 forced-ventilation pipes of uniform distribution in the heap body; Said waste height is less than 2 meters, and bottom width is less than 5 meters, and the heap surface is carried out and covered 10 ~ 20cm oversize or semi-mature material; Ventpipe communicates with aeration equipment, is provided with TM in the heap body;
C, first becomes thoroughly decomposed the phase
Perishable rubbish after the B step is in heaps was first to become thoroughly decomposed the phase in 10 ~ 15 days, and every day at upper and lower noon is respectively detected heap temperature once during this; Before the said heap temperature to 60 °, ventilate twice every day, each about 30 minutes, heap temperature extended to 30 ~ 50 minutes at 60 ° ~ 75 ° aeration time, control heap body water ratio 50 ~ 70% weight percents;
D, turning
Carry out the turning first time in the time of 10 ~ 15 days in heaps, heap is stopped the surface after the turning does not need to carry out again and covers the sieve thing, regulates water ratio 50 ~ 70% weight percents;
E, second becomes thoroughly decomposed the phase
For the first time after the turning 15 ~ 20 days be second to become thoroughly decomposed the phase; Every day at upper and lower noon is respectively detected heap temperature once during this, through long-time ventilation or turning in 2 ~ 3 days once, and to make the control heap temperature less than 75 °; Preceding 10 days through the not moisturizing of only ventilating after 50 ~ 60%, 10 days of moisturizing control water ratio;
F, screening
Second becomes thoroughly decomposed the heap body of phase through the screen cloth of 1.2cm * 1.2cm, tells top sieve thing and sieve thing down, and the top sieve thing is used to pile body to be carried out lid or make addition material, becomes thoroughly decomposed the phase after the following sieve thing entering;
G, after become thoroughly decomposed the phase
Under sieve and become thoroughly decomposed the phase after thing gets into, after become thoroughly decomposed the phase less than 30 days, met " townm refuse agricultural standards " composting production (GB8172-87) at last.
CN2011104573507A 2011-12-31 2011-12-31 Aerobic composting method for organic perishable garbage Pending CN102515907A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2011104573507A CN102515907A (en) 2011-12-31 2011-12-31 Aerobic composting method for organic perishable garbage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2011104573507A CN102515907A (en) 2011-12-31 2011-12-31 Aerobic composting method for organic perishable garbage

Publications (1)

Publication Number Publication Date
CN102515907A true CN102515907A (en) 2012-06-27

Family

ID=46287051

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2011104573507A Pending CN102515907A (en) 2011-12-31 2011-12-31 Aerobic composting method for organic perishable garbage

Country Status (1)

Country Link
CN (1) CN102515907A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104261920A (en) * 2014-10-20 2015-01-07 云南省农业科学院农业环境资源研究所 Method for accelerating aerobic composting rate of agricultural solid wastes
CN104785491A (en) * 2014-06-11 2015-07-22 湖南紫博星生物科技发展有限公司 Kitchen waste automatic treatment system
WO2018014754A1 (en) * 2016-07-19 2018-01-25 金发科技股份有限公司 Efficient aerobic composting technology for kitchen garbage
WO2018014756A1 (en) * 2016-07-19 2018-01-25 金发科技股份有限公司 Rapid fermentation method for kitchen waste
CN110092680A (en) * 2019-04-19 2019-08-06 浙江旺能生态科技有限公司 Organic fertilizer production method based on the perishable rubbish in the market of farm produce

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE10133777A1 (en) * 2001-07-16 2003-02-06 Variotec Josef Biller Growth-promoting micro-organism culture concentrated in a secondary container with feed-back to separate primary culture seed tank
CN1712386A (en) * 2004-06-14 2005-12-28 宁波杉杉环保发展有限公司 High-temperature aerobic fermentation of organic refuse material
CN101973794A (en) * 2010-10-29 2011-02-16 中国农业大学 Composting method

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE10133777A1 (en) * 2001-07-16 2003-02-06 Variotec Josef Biller Growth-promoting micro-organism culture concentrated in a secondary container with feed-back to separate primary culture seed tank
CN1712386A (en) * 2004-06-14 2005-12-28 宁波杉杉环保发展有限公司 High-temperature aerobic fermentation of organic refuse material
CN101973794A (en) * 2010-10-29 2011-02-16 中国农业大学 Composting method

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104785491A (en) * 2014-06-11 2015-07-22 湖南紫博星生物科技发展有限公司 Kitchen waste automatic treatment system
CN104785491B (en) * 2014-06-11 2017-12-08 湖南紫博星生物科技发展有限公司 Food waste automated processing system
CN104261920A (en) * 2014-10-20 2015-01-07 云南省农业科学院农业环境资源研究所 Method for accelerating aerobic composting rate of agricultural solid wastes
WO2018014754A1 (en) * 2016-07-19 2018-01-25 金发科技股份有限公司 Efficient aerobic composting technology for kitchen garbage
WO2018014756A1 (en) * 2016-07-19 2018-01-25 金发科技股份有限公司 Rapid fermentation method for kitchen waste
CN110092680A (en) * 2019-04-19 2019-08-06 浙江旺能生态科技有限公司 Organic fertilizer production method based on the perishable rubbish in the market of farm produce

Similar Documents

Publication Publication Date Title
CN104926541B (en) A kind of production technology of joint wheat bran stalk vinasse seaweed mixed fungus fermentation efficient biologic-organic fertilizer
CN103613447B (en) A kind of Polyelement slow release granular fertilizer with high fertilizer efficiency and preparation method thereof
CN101851127B (en) Preparation process of multifunctional bamboo-shell organic-inorganic composite fertilizer
CN103274779A (en) Production method of environment-friendly bio-organic fertilizer
CN101863687A (en) Method for refining microbial organic fertilizer with branch lops
CN104387134A (en) Method for processing bio-organic fertilizer
CN101874567A (en) Method for resource utilization of plant wastes
CN102515907A (en) Aerobic composting method for organic perishable garbage
CN101885626B (en) Mushroom waste and livestock manure compound fertilizer and production method thereof
CN106083258B (en) A kind of functionality pig manure modifying agent and the method for preparing mushroom-cultivating material using modified pig manure
CN104230401A (en) Treatment method of kitchen garbage
CN103319269B (en) Chicken manure, pig manure and pleurotus eryngii mushroom bran-containing organic fertilizer and preparation method thereof
CN101712568A (en) Bio-organic fertilizer and preparation method thereof
CN102807400A (en) Method for preparing organic fertilizer through barrel fermentation
CN104509691A (en) Fungus chaff bird feed and preparation method thereof
CN102180716A (en) Method for producing organic compound fertilizer by fermenting animal manure
CN110981626A (en) Straw compound fertilizer and preparation method thereof
CN104737989A (en) Method for treating fermentation filter residue and livestock and poultry manure mixture on large scale through fly maggots
CN104803722A (en) Organic fertilizer prepared from straw and preparation technology of organic fertilizer
CN103146391B (en) Straw decomposing inoculant and production technique thereof
CN102503615B (en) Method for preparing microbe-fermented organic fertilizer
CN107011091A (en) A kind of preparation method of efficient organic fertilizer
CN104193430A (en) Straw rotting agent and preparation method thereof
CN107032854A (en) The method that stalk fermentation biogas residue prepares organic fertilizer
CN103755407A (en) Method for preparing biological carbon organic matrix in high-altitude regions

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C12 Rejection of a patent application after its publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20120627