CN102249763A - Biological organic fertilizer produced by using household garbage buried for years - Google Patents

Biological organic fertilizer produced by using household garbage buried for years Download PDF

Info

Publication number
CN102249763A
CN102249763A CN2011101384236A CN201110138423A CN102249763A CN 102249763 A CN102249763 A CN 102249763A CN 2011101384236 A CN2011101384236 A CN 2011101384236A CN 201110138423 A CN201110138423 A CN 201110138423A CN 102249763 A CN102249763 A CN 102249763A
Authority
CN
China
Prior art keywords
parts
organic fertilizer
biological organic
day
rubbish
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.)
Granted
Application number
CN2011101384236A
Other languages
Chinese (zh)
Other versions
CN102249763B (en
Inventor
杨梭臣
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.)
YUNNAN BAOER LAKE MANAGEMENT CO Ltd
Original Assignee
YUNNAN BAOER LAKE MANAGEMENT CO Ltd
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 YUNNAN BAOER LAKE MANAGEMENT CO Ltd filed Critical YUNNAN BAOER LAKE MANAGEMENT CO Ltd
Priority to CN2011101384236A priority Critical patent/CN102249763B/en
Publication of CN102249763A publication Critical patent/CN102249763A/en
Application granted granted Critical
Publication of CN102249763B publication Critical patent/CN102249763B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

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

Abstract

The invention discloses a biological organic fertilizer produced by using household garbage buried for years. Fertilizers are an important material guarantee for developing high-yield high-quality agriculture. The biological organic fertilizer provided in the invention is prepared by the following raw materials by weight percentage: 1000 parts of garbage nutrition soil, 5 to 10 parts of enlarged Japanese ferment bacteria, 4 to 8 parts of modified zeolite powder, 10 to 18 parts of dried chicken manure or duck manure, 16 to 22 parts of rice bran and 8 to 12 parts of rock phosphate powder. The biological organic fertilizer is obtained by the following steps: uniformly stirring the raw materials at the above-mentioned weight percentage, piling the raw materials for fermentation, keeping the temperature for the fermentation at 60 to 70 DEG C for the first and second day, keeping the temperature at 40 to 50 DEG C for the third and fourth day, and keeping the temperature normal for the fifth and sixth day. The invention enables household garbage buried for years to be used again, thereby effectively improving environment and reducing production cost; the invention also enables the problems of difficult addressing of desired landfills due to rapid increase of household garbage and occupation of considerable land by garbage to be overcome and landfills to be used again.

Description

The biological organic fertilizer that utilizes landfill domestic refuse for many years to produce
Technical field
The present invention relates to the processing of solid waste, be specifically related to the fertilizer that a kind of refuse or rubbish change.
Background technology
Since the seventies in 20th century, China begins to adopt landfill method treatment and disposal domestic waste gradually.So far landfill has become the main disposal options of China's domestic waste, adopt the domestic waste amount of landfill method treatment and disposal to account for more than 70% of whole treatment capacities, some bulky refuse landfill yards have been built up, the rubbish that each landfill yard is inserted up to ten million tons up to a hundred.Reduced investment, technology are simple because landfill method has, convenient management, applied widely, advantage such as maintenance cost is low, form situation according to China's economic and technique level and domestic waste, in long one period from now on, China's domestic waste is disposed will be based on landfill.But, along with the quickening of Urbanization in China.Adopt landfill method treatment and disposal domestic refuse will face several big outstanding problems: the one, generation every year of domestic refuse, the high speed with 7%~9% increased sharply, and the area of required landfill yard is increasing; The 2nd, constantly to the surrounding area expansion, the suburbs land price escalates the city scope, makes the addressing of landfill yard more and more difficult, even can't find suitable site; The 3rd, China after the seventies in 20th century especially a large amount of refuse landfills of building of the middle and later periods eighties reached or be about to reach working life, the construction again of landfill yard and utilize problem to become more and more sharp-pointed again.
On the other hand, usually need a large amount of soil resource again, can adopt the resourceful stale garbage of landfill to substitute, will on economic benefit and environmental benefit, have unrivaled superiority with certain character.If this part resource can be made the higher biological organic fertilizer of use value, will bring huge contribution to China's Agricultural Development.
Summary of the invention
The object of the present invention is to provide a kind ofly can make that the rubbish of landfill obtains regeneration, and utilize this rubbish production to obtain a kind ofly can improving soil quality, efficient, nuisanceless, free of contamination biological organic fertilizer.
For achieving the above object, the present invention is by the following technical solutions: biological organic fertilizer is formed by the preparation of raw material of following parts by weight: 1000 parts in rubbish nutrition soil, Japan's enzymatic microorganism enlarges 5~10 parts of bacterium, 4~8 parts of modified zeolite powders, 10~18 parts in the chicken manure of oven dry or duck excrement, 16~22 parts in rice bran, 8~12 parts of rock phosphate powders.
The preparation method is as follows: the fermentation of banking up after by proportioning above-mentioned raw materials being stirred, turn over throwing according to leavening temperature every day, first, second day maintains the temperature between 60~70 ℃, three, maintained the temperature between 40~50 ℃ in the 4th day, five, keep normal temperature on the 6th day, promptly get the powdery biological organic fertilizer afterwards.
Preferably, raw materials used to calculate proportioning by weight as follows: 1000 parts in rubbish nutrition soil, Japanese enzymatic microorganism enlarge bacterium 5-8 part, modified zeolite powder 5-6 part, the chicken manure of oven dry or duck excrement 13-15 part, rice bran 18-20 part, rock phosphate powder 10-12 part.
Described rubbish nutrition soil is obtained by following method:
1. on the spot landfill domestic refuse is for many years carried out go-on-go: divide to detect metal, construction waste, plastics;
2. the air-dry or oven dry with remaining domestic refuse after the go-no-go;
3. shake and sift out particle, powdery rubbish nutrition soil, move rubbish nutrition soil to production plant area, standby.
Described modified zeolite powder: zeolite is levigate for granularity is 180~220 purpose powder, obtain modified zeolite powder at 280~320 ℃ temperature condition bottom fermentations after 5~6 hours.
Rubbish nutrition soil described in the above-mentioned component is by obtaining after the landfill refuse treatment for many years, contain abundant organic matter, also containing some nitrogen, Phosphorus nutrition.Below be the test result of this physico-chemical property of rubbish nutrition soil matrix:
Figure 551708DEST_PATH_IMAGE001
Enzymatic microorganism is by bacterium, actinomycetes and fungi three major types, the useful active functional group that tens kinds of bacterium and enzyme are formed.It can not only decompose various organic matters such as agricultural crop straw and can decompose chemical ingredientss such as chemical fertilizer residual in the soil, agricultural chemicals, can also decompose mineral substance such as zeolite, shale, it can generate fermentation resultants such as multivitamin, nucleic acid, tropina in the decomposing and fermenting process, nutritive value is quite abundant.
Zeolite powder is natural levigate the forming of zeolite rock, and zeolite has unique adsorptivity, catalytic, ion exchangeable, and ionic selectivity, acid resistance, thermostability, many compositions property reach very high activity and toxin immunity etc.Positively charged ion in zeolite hole and the passage also has stronger selectivity ion-exchange performance.Killed behind the Zeolite modifying because the objectionable impurities that long-term storage produces shows the function of zeolite more fully.
Phosphorus is important chemical material, also is the bioelement of crop growth, adds rock phosphate powder and can effectively replenish phosphorus in raw material.
The present invention has following beneficial effect:
1. turn waste into wealth, reduced production cost: the present invention has realized successfully adding with landfill rubbish for many years that other effective constituents are mixed, fermentation makes biological organic fertilizer, make landfill rubbish for many years obtain utilizing once more, effectively improved environment, reduced production cost.Solved the domestic refuse problem that required landfill yard is difficult to addressing that increases sharply, also solved the problem that waste takies a large amount of soils simultaneously, the landfill place utilized once more.
2. improve output and security of products, improve soil: contain great number of organic matters and nitrogen, Phosphorus nutrition in the rubbish nutrition soil.Utilize the bio-organic fertilizer of the autochthonal product of rubbish nutrition can improve soil organic matter content, can significantly improve Soil structure, vegetable soil, thus increase soil fertility, help the Sustainable development and the utilization in soil.
3. solve the problem of dumping produced pollution environment and land occupation, the protection environment.
4. use its probiotics of this biological organic fertilizer and can kill pathogenic bacteria in the soil, can improve the soil comprehensively reach that soil property is soft, ventilative, water conservation, guarantor's fertilizer, drought resisting, waterlogging, improve the gentle soil fertility in ground, overcome farm crop continuous cropping disease, effectively control disease and pest, stable increase output, and can greatly improve the quality of agricultural-food and the purpose of mouthfeel.
Specific embodiment
Embodiment 1: the fermentation of banking up after chicken manure, 16kg rice bran, 8kg rock phosphate powder, the 1000kg rubbish nutrition soil that 5kg Japan enzymatic microorganism is enlarged bacterium, 4kg modified zeolite powder, 10kg oven dry stirs, turn over throwing according to leavening temperature every day, first, second day maintains the temperature between 60~70 ℃, three, maintained the temperature between 40~50 ℃ in the 4th day, five, keep normal temperature on the 6th day, promptly get the powdery biological organic fertilizer afterwards.
Embodiment 2:Preparation rubbish nutrition soil: 1. on the spot landfill domestic refuse is for many years carried out go-on-go: divide to detect metal, construction waste, plastics; 2. the air-dry or oven dry with remaining domestic refuse after the go-no-go; 3. shake and sift out particle, powdery rubbish nutrition soil, move rubbish nutrition soil to production plant area, standby.Rubbish nutrition soil 1000kg that makes above and 10kg Japan enzymatic microorganism enlarge chicken manure, 12kg rock phosphate powder, the 22kg rice bran of bacterium, 6kg modified zeolite powder, 18kg oven dry, the fermentation of banking up after stirring, turn over throwing according to leavening temperature every day, first, second day maintains the temperature between 60~70 ℃, three, maintained the temperature between 40~50 ℃ in the 4th day, five, keep normal temperature on the 6th day, promptly get the powdery biological organic fertilizer afterwards.
Embodiment 3: preparation rubbish nutrition soil: 1. on the spot landfill domestic refuse is for many years carried out go-on-go: divide to detect metal, construction waste, plastics; 2. the air-dry or oven dry with remaining domestic refuse after the go-no-go; 3. shake and sift out particle, powdery rubbish nutrition soil, move rubbish nutrition soil to production plant area, standby.The preparation modified zeolite powder: zeolite is levigate for granularity is 180 purpose powder, obtain modified zeolite powder at 280 ℃ temperature condition bottom fermentations after 6 hours.With the above rubbish nutrition soil 1000kg that makes, modified zeolite powder 5kg and 7kg Japan enzymatic microorganism enlarge duck excrement, 9kg rock phosphate powder, the 19kg rice bran of bacterium, 14kg oven dry, the fermentation of banking up after stirring, turn over throwing according to leavening temperature every day, first, second day maintains the temperature between 60~70 ℃, three, maintained the temperature between 40~50 ℃ in the 4th day, kept normal temperature, and promptly got the powdery biological organic fertilizer afterwards in the 5th, the 6th day.
Embodiment 4:Preparation rubbish nutrition soil: 1. on the spot landfill domestic refuse is for many years carried out go-on-go: divide to detect metal, construction waste, plastics; 2. the air-dry or oven dry with remaining domestic refuse after the go-no-go; 3. shake and sift out particle, powdery rubbish nutrition soil, move rubbish nutrition soil to production plant area, standby.The preparation modified zeolite powder: zeolite is levigate for granularity is 220 purpose powder, obtain modified zeolite powder at 320 ℃ temperature condition bottom fermentations after 5 hours.The fermentation of banking up after the rubbish nutrition soil 1000kg that 8kg Japan enzymatic microorganism is enlarged duck excrement, 12kg rock phosphate powder, 20kg rice bran, the preparation of above method of the chicken manure of bacterium, 6kg modified zeolite powder, 5kg oven dry and 10kg oven dry stirs, turn over throwing according to leavening temperature every day, first, second day maintains the temperature between 60~70 ℃, three, maintained the temperature between 40~50 ℃ in the 4th day, five, keep normal temperature on the 6th day, promptly get the powdery biological organic fertilizer afterwards.

Claims (5)

1. the biological organic fertilizer that utilizes landfill domestic refuse for many years to produce, it is characterized in that, raw materials used proportioning by weight is as follows: 1000 parts in rubbish nutrition soil, Japan's enzymatic microorganism enlarges 5~10 parts of bacterium, 4~8 parts of modified zeolite powders, 10~18 parts in the chicken manure of oven dry or duck excrement, 16~22 parts in rice bran, 8~12 parts of rock phosphate powders;
The preparation method is as follows: the fermentation of banking up after by proportioning above-mentioned raw materials being stirred, turn over throwing according to leavening temperature every day, first, second day maintains the temperature between 60~70 ℃, three, maintained the temperature between 40~50 ℃ in the 4th day, five, keep normal temperature on the 6th day, promptly get the powdery biological organic fertilizer afterwards.
2. the biological organic fertilizer that utilizes landfill domestic refuse for many years to produce according to claim 1, it is characterized in that, raw materials used proportioning by weight is as follows: 1000 parts in rubbish nutrition soil, Japan's enzymatic microorganism enlarges bacterium 5-8 part, modified zeolite powder 5-6 part, chicken manure or duck excrement 13-15 part of oven dry, rice bran 18-20 part, rock phosphate powder 10-12 part.
3. the biological organic fertilizer that utilizes landfill domestic refuse for many years to produce according to claim 1 and 2 is characterized in that described rubbish nutrition soil is obtained by following method:
1. on the spot landfill domestic refuse is for many years carried out go-on-go: divide to detect metal, construction waste, plastics;
2. the air-dry or oven dry with remaining domestic refuse after the go-no-go;
3. shake and sift out particle, powdery rubbish nutrition soil, move rubbish nutrition soil to production plant area, standby.
4. the biological organic fertilizer that utilizes landfill domestic refuse for many years to produce according to claim 1 and 2, it is characterized in that, described modified zeolite powder is that zeolite is levigate for granularity is 180~220 purpose powder, obtains modified zeolite powder at 280~320 ℃ temperature condition bottom fermentations after 5~6 hours.
5. the biological organic fertilizer that utilizes landfill domestic refuse for many years to produce according to claim 3, it is characterized in that, described modified zeolite powder is that zeolite is levigate for granularity is 180~220 purpose powder, obtains modified zeolite powder at 280~320 ℃ temperature condition bottom fermentations after 5~6 hours.
CN2011101384236A 2011-05-26 2011-05-26 Biological organic fertilizer produced by using household garbage buried for years Expired - Fee Related CN102249763B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2011101384236A CN102249763B (en) 2011-05-26 2011-05-26 Biological organic fertilizer produced by using household garbage buried for years

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2011101384236A CN102249763B (en) 2011-05-26 2011-05-26 Biological organic fertilizer produced by using household garbage buried for years

Publications (2)

Publication Number Publication Date
CN102249763A true CN102249763A (en) 2011-11-23
CN102249763B CN102249763B (en) 2013-11-06

Family

ID=44977383

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2011101384236A Expired - Fee Related CN102249763B (en) 2011-05-26 2011-05-26 Biological organic fertilizer produced by using household garbage buried for years

Country Status (1)

Country Link
CN (1) CN102249763B (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102674913A (en) * 2012-05-23 2012-09-19 湖北益丰生物肥业有限公司 Organic fluid fertilizer and preparation method
CN105198677A (en) * 2015-11-12 2015-12-30 四川亨润农业科技股份有限公司 Selenium-rich biological organic fertilizer and preparation method thereof
CN105850458A (en) * 2016-04-22 2016-08-17 中国科学院武汉植物园 Method for planting thalia dealbata on side slope
CN105850457A (en) * 2016-04-22 2016-08-17 中国科学院武汉植物园 Method for planting miscanthus sinensis on side slope

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105541431A (en) * 2015-12-16 2016-05-04 黄平县小秋农民专业合作社 Organic fertilizer for blueberry tree

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1256258A (en) * 1999-12-15 2000-06-14 华中理工大学 Environment protecting method during producing compound fertilizer with excrments and domestic garbage
CN1757616A (en) * 2005-08-18 2006-04-12 武汉合缘绿色生物工程有限公司 Ferment fungi biological organic fish guano, and its prodn. method
CN1785924A (en) * 2005-11-04 2006-06-14 袁登辉 Amino acid organic fertilizer, its preparation method and use
CN1872803A (en) * 2005-06-04 2006-12-06 成官文 A biologic organic fertilizer, and preparation method

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1256258A (en) * 1999-12-15 2000-06-14 华中理工大学 Environment protecting method during producing compound fertilizer with excrments and domestic garbage
CN1872803A (en) * 2005-06-04 2006-12-06 成官文 A biologic organic fertilizer, and preparation method
CN1757616A (en) * 2005-08-18 2006-04-12 武汉合缘绿色生物工程有限公司 Ferment fungi biological organic fish guano, and its prodn. method
CN1785924A (en) * 2005-11-04 2006-06-14 袁登辉 Amino acid organic fertilizer, its preparation method and use

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102674913A (en) * 2012-05-23 2012-09-19 湖北益丰生物肥业有限公司 Organic fluid fertilizer and preparation method
CN102674913B (en) * 2012-05-23 2014-03-05 湖北益丰生物肥业有限公司 Organic fluid fertilizer and preparation method
CN105198677A (en) * 2015-11-12 2015-12-30 四川亨润农业科技股份有限公司 Selenium-rich biological organic fertilizer and preparation method thereof
CN105850458A (en) * 2016-04-22 2016-08-17 中国科学院武汉植物园 Method for planting thalia dealbata on side slope
CN105850457A (en) * 2016-04-22 2016-08-17 中国科学院武汉植物园 Method for planting miscanthus sinensis on side slope

Also Published As

Publication number Publication date
CN102249763B (en) 2013-11-06

Similar Documents

Publication Publication Date Title
CN101429066B (en) Method for producing fertilizer with papermaking sewage sludge
CN101439997B (en) Preparation of seaweed organic fertilizer
CN103980051B (en) A kind of ureaformaldehyde humic acid organic fertilizer
CN100361938C (en) Process for preparing organic fertilizer by biological mud and grass refuse of papermaking plant
CN102180743B (en) Method for producing insect resistance organic compound fertilizer by fermentation of agricultural organic wastes
CN105439775A (en) Specific fertilizer for saline-alkali soil and preparation method thereof
CN102180737B (en) Method for producing organic compound fertilizer by fermenting agricultural organic waste
CN107916108A (en) A kind of soil conditioner, its preparation method and application
CN104761412A (en) A fertilizer for sweet potato planting in saline-alkali land and a preparing method thereof
CN102249763B (en) Biological organic fertilizer produced by using household garbage buried for years
CN101899395A (en) Screening and construction method for composite microbial system for rapidly degrading rice straw and composite microbial system
CN105001007B (en) A kind of method and organic fertilizer that organic fertilizer is manufactured using citrus peel residue and municipal sludge as primary raw material
CN103288502A (en) Method for preparing biological organic fertilizer from sugarcane leaves as main raw material
CN104909867A (en) Bioorganic fertilizer and preparation method thereof
CN102180716B (en) Method for producing organic compound fertilizer by fermenting animal manure
CN102173899B (en) Amino acid-containing liquid fertilizer and preparation method thereof
CN101486608A (en) Biological green fertilizer
CN105566002A (en) Preparation method of ferment mineral substance drought-resisting and water-retaining selenium-rich fertilizer
CN103664251A (en) Bio-fertilizer produced by using agricultural wastes
CN102173887A (en) Production method of biological organic fertilizer containing Avermectins
CN107200645A (en) A kind of bioactivation enzymolysis phosphorus agent containing bacillus licheniformis and preparation method thereof
CN104230579A (en) Preparation method for chitin-rich compound fertilizer
CN102040430B (en) Method for producing compound microbial fertilizer with insecticidal effect
CN102241549B (en) Amino-acid-containing biological compound fertilizer
CN102077710A (en) Method for improving saline-alkali soil by utilizing biological waste compost

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20131106

Termination date: 20200526

CF01 Termination of patent right due to non-payment of annual fee