CN110550725A - Biological filler for treating livestock and poultry wastewater - Google Patents

Biological filler for treating livestock and poultry wastewater Download PDF

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Publication number
CN110550725A
CN110550725A CN201910833855.5A CN201910833855A CN110550725A CN 110550725 A CN110550725 A CN 110550725A CN 201910833855 A CN201910833855 A CN 201910833855A CN 110550725 A CN110550725 A CN 110550725A
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China
Prior art keywords
sweet potato
biological filler
wormwood
livestock
mixture
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Pending
Application number
CN201910833855.5A
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Chinese (zh)
Inventor
卢洪成
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Hunan Yushan Yyu Agricultural Science And Technology Co Ltd
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Hunan Yushan Yyu Agricultural Science And Technology Co Ltd
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Priority to CN201910833855.5A priority Critical patent/CN110550725A/en
Publication of CN110550725A publication Critical patent/CN110550725A/en
Pending legal-status Critical Current

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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05DINORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
    • C05D5/00Fertilisers containing magnesium
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/20Nature of the water, waste water, sewage or sludge to be treated from animal husbandry
    • 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 filler for treating livestock and poultry wastewater, which is characterized by consisting of sweet potato vines, sweet potato residues, wormwood, a modifier and a base material. And particularly discloses a preparation method of the biological filler and an application method of the biological filler in treating livestock wastewater.

Description

Biological filler for treating livestock and poultry wastewater
Technical Field
The invention belongs to the field of livestock and poultry wastewater treatment, and particularly relates to a biological filler for treating livestock and poultry wastewater.
Background
with the continuous expansion of the breeding scale and the enhancement of the aspects of environmental protection consciousness, food safety and the like of people, the treatment of livestock wastewater is on the agenda day by day and is rapidly developed into an industry. The waste water of the farm mainly comprises high-concentration organic waste water rich in a large amount of pathogens (escherichia coli, roundworm eggs and the like), and the content of suspended matters and ammonia nitrogen is large, so that the waste water enters an underground water layer through surface runoff and percolation to pollute underground water if the waste water is not properly treated. After the untreated wastewater enters a natural water body, the contents of solid suspended matters, organic matters and microorganisms in the water are increased, the physical, chemical and biological community composition of the water body is changed, and the water quality is deteriorated. The wastewater also contains a large amount of pathogenic microorganisms which can be diffused and spread through the water body and harm the health of people and livestock. The treatment modes of the wastewater mainly comprise: physical treatment, namely firstly carrying out solid-liquid separation, and then carrying out the methods of adopting activated carbon, magnesium oxide modified zeolite and magnetic flocculation precipitation; chemical treatment, namely neutralizing harmful substances by using some chemicals, and oxidizing by using some chemical agents such as hydrogen peroxide and the like; the biological treatment adopts the main methods of aerobic treatment, anaerobic treatment and a treatment mode combining the aerobic treatment and the anaerobic treatment.
Due to the development of intensive and large-scale breeding industry in China, a large number of farms appear in rural areas, the amount of waste water discharged by the farms every day is large and concentrated, a large amount of pollutants are contained in the waste water, and livestock breeders need to comprehensively consider a waste water treatment method according to conditions such as breeding scale, environmental characteristics of the farms and the like. If the waste water can be treated by integrating economic benefits, environmental protection benefits and social benefits, the invention provides the biological filler which changes waste into valuable and is beneficial to the effective treatment of the waste water.
Disclosure of Invention
The invention aims to provide a biological filler for treating livestock and poultry wastewater.
In order to realize the aim of the invention, the biological filler for treating the livestock and poultry wastewater has the specific embodiment that:
The biological filler for treating the livestock and poultry wastewater comprises sweet potato vines, sweet potato residues, wormwood, a modifier and a base material.
the invention relates to a biological filler for treating livestock and poultry wastewater, which comprises the following components in percentage by weight: 1-30% of sweet potato vine, 1-60% of sweet potato residue, 1-30% of wormwood, 1-50% of modified solvent and 1-30% of base material.
The invention relates to a biological filler for treating livestock and poultry wastewater, which comprises the following components in percentage by weight: 10-20% of sweet potato vine, 10-40% of sweet potato residue, 10-20% of wormwood, 20-40% of modified solvent and 10-20% of base material.
The invention relates to a biological filler for treating livestock and poultry wastewater, which comprises the following components in percentage by weight: 16-20% of sweet potato vine, 10-28% of sweet potato residue, 12-20% of wormwood, 20-36% of modified solvent and 10-16% of base material.
The biological filler for treating the livestock and poultry wastewater disclosed by the invention comprises one or more of a modifier, a compound fertilizer, potassium chloride, ammonium phosphate, urea and a silicon-containing fertilizer.
The biological filler for treating the livestock and poultry wastewater comprises one or more of a base material, ceramsite, expanded vermiculite, sepiolite and zeolite.
The invention relates to a biological filler for treating livestock and poultry wastewater, which is prepared by the following steps:
1) Pulverizing sweet potato vine and wormwood in a pulverizer, adding sweet potato residue, mixing, stirring, and mixing uniformly;
2) putting the mixture 1) into a reaction tank, steaming for 4-5 hours at the temperature of 100-200 ℃ under the anoxic or anaerobic condition, then cooling to 50-60 ℃, adding compound fertilizer and water, stirring for 1-2 hours at the temperature of 40-50 ℃, cooling, drying and reserving for later use.
3) Mixing the mixture obtained in the step 2) with ceramsite and expanded vermiculite, and compressing the mixture into blocks by a press machine to obtain biomass blocks;
4) Soaking the mixture 3) in 0.2-2mol/L potassium chloride solution for 3-5 hours, taking out the soaked mixture, and drying the soaked mixture; and compressing the mixture into blocks by a press machine again to obtain the biomass blocks.
the invention relates to a biological filler for treating livestock and poultry wastewater, which comprises sweet potato vine: sweet potato residue: the mass ratio of the wormwood is 1-5:1-7: 1-7; the mass ratio of the compound fertilizer to the water is 0.8:10-8: 10; the mass ratio of the ceramsite to the expanded vermiculite is 0.25:1-2.5: 1.
The invention relates to a biological filler for treating livestock and poultry wastewater, which comprises sweet potato vine: sweet potato residue: the mass ratio of the wormwood is 4:7: 3; the mass ratio of the compound fertilizer to the water is 1.2: 10.
The invention relates to a biological filler for treating livestock and poultry wastewater, which is applied by the following method: and (3) putting the obtained biomass blocks into a livestock and poultry wastewater pool, soaking for 10-24 hours, taking out, scattering, covering a layer of rice straw on the surface, and composting.
the invention relates to a biological filler for treating livestock and poultry wastewater, and an application of the biological filler in treating the livestock and poultry wastewater.
The composting quality of the biological filler for treating the livestock and poultry wastewater after being soaked in the biological filler is identified by the following steps: according to the checking standard of the rotten degree. The quality of the compost after decomposition is a comprehensive index for identifying the quality of the compost. Can be judged according to the color, smell, straw hardness, compost leaching liquid, compost volume, carbon-nitrogen ratio and corruption coefficient, and specifically comprises the following steps: (1) from the viewpoint of color and smell, the straw of the decomposed compost becomes brown or black brown, has black juice and night, has ammonia odor, and the content of ammonium nitrogen is obviously increased by using an ammonium reagent for quick measurement. And (2) the hardness of the straws is that the compost is held by hands, is soft and elastic when being warm, is crisp when being dry, is easy to break, and organic matters lose elasticity. And (3) taking decomposed compost, adding clean water, stirring (the ratio of fertilizer to water is 1:5-10), and standing for 3-5 minutes to obtain light yellow leachate. And (4) the compost volume is reduced 2/3-1/2 compared with that of the compost when just piled. (5) carbonitriding, generally 20-30:1 (25: 1 is the most preferable) (6), and a humification coefficient of about 30%. The compost which reaches the indexes is high-quality compost with good fertilizer efficiency and can be applied to various soils and crops. The fertilizer can be applied for a long time, and has remarkable effects of high yield, soil improvement and soil fertility improvement. Detailed Description
The following examples are intended to further illustrate the invention and are not intended to limit the scope of the invention in any way.
example 1 composition: the preparation method of the sweet potato vine comprises the following steps of (1) 4kg of sweet potato vine, 7kg of sweet potato residue, 3kg of wormwood, 9kg of compound fertilizer, 2.5kg of ceramsite and 1.5kg of expanded vermiculite: 1) Pulverizing sweet potato vine and wormwood in a pulverizer, adding sweet potato residue, mixing, stirring, and mixing uniformly; 2) Putting 1) into a reaction tank, steaming at 180 ℃ for 5 hours under the condition of oxygen deficiency or oxygen-free, then cooling to 50-60 ℃, adding compound fertilizer and water (mass ratio is 1.2: 10), stirring for 2 hours at 50 ℃, cooling, drying and reserving for later use. 3) Mixing the mixture obtained in the step 2) with ceramsite and expanded vermiculite, and compressing the mixture into blocks by a press machine; 4) Soaking the mixture 3) in 0.5mol/L potassium chloride solution for 4 hours, taking out the soaked mixture, and drying the soaked mixture; compressing the mixture into blocks by a press machine again to obtain biomass blocks; the application comprises the following steps: and (3) putting the obtained biomass blocks into a livestock and poultry wastewater pool, soaking for 20 hours, taking out, scattering, covering a layer of rice straw on the surface, and composting. Example 2 composition: the preparation method of the sweet potato vine comprises the following steps of (1) 4kg of sweet potato vine, 7kg of sweet potato residue, 3kg of wormwood, 7kg of compound fertilizer, 2.5kg of ceramsite and 1kg of expanded vermiculite: 1) Pulverizing sweet potato vine and wormwood in a pulverizer, adding sweet potato residue, mixing, stirring, and mixing uniformly; 2) Putting 1) into a reaction tank, steaming at 180 ℃ for 5 hours under the condition of oxygen deficiency or oxygen-free, then cooling to 50-60 ℃, adding compound fertilizer and water (mass ratio is 1.2: 10), stirring for 2 hours at 50 ℃, cooling, drying and reserving for later use. 3) Mixing the mixture obtained in the step 2) with ceramsite and expanded vermiculite, and compressing the mixture into blocks by a press machine to obtain biomass blocks; 4) Soaking the mixture 3) in 0.2mol/L potassium chloride solution for 4 hours, taking out the soaked mixture, and drying the soaked mixture; compressing the mixture into blocks by a press machine again to obtain biomass blocks; the application comprises the following steps: and (3) putting the obtained biomass blocks into a livestock and poultry wastewater pool, soaking for 20 hours, taking out, scattering, covering a layer of rice straw on the surface, and composting. Example 3 composition: the preparation method of the sweet potato vine comprises the following steps of (1) 4kg of sweet potato vine, 7kg of sweet potato residue, 3kg of wormwood, 5kg of compound fertilizer, 2.5kg of ceramsite and 1.2kg of expanded vermiculite: 1) Pulverizing sweet potato vine and wormwood in a pulverizer, adding sweet potato residue, mixing, stirring, and mixing uniformly; 2) Putting 1) into a reaction tank, steaming at 180 ℃ for 4-5 hours under the condition of oxygen deficiency or oxygen-free, then cooling to 50-60 ℃, adding compound fertilizer and water (mass ratio is 1.2: 10), stirring for 2 hours at 50 ℃, cooling, drying and reserving for later use. 3) Mixing the mixture obtained in the step 2) with ceramsite and expanded vermiculite, and compressing the mixture into blocks by a press machine to obtain biomass blocks; 4) Soaking the mixture 3) in 1.0mol/L potassium chloride solution for 4 hours, taking out the soaked mixture, and drying the soaked mixture; compressing the mixture into blocks by a press machine again to obtain biomass blocks; the application comprises the following steps: and (3) putting the obtained biomass blocks into a livestock and poultry wastewater pool, soaking for 20 hours, taking out, scattering, covering a layer of rice straw on the surface, and composting.
Test example 1
And (3) screening the pyrolysis temperature: fixing biological filler components (0.5 kg sweet potato vine, 0.5g sweet potato residue, 0.5kg wormwood, 0.5kg compound fertilizer, 0.5kg ceramsite and 0.2kg expanded vermiculite), and screening the pyrolysis temperature. The pig manure sewage is evenly mixed and evenly divided into 5 groups, and screening is carried out according to indexes of biochemical oxygen demand (BOD 5), chemical oxygen demand (CODcr) (mg/L), suspended matters (SS) (mg/L) and ammonia nitrogen (NH 3-N) (mg/L). The results are as follows:
From the results, as the pyrolysis temperature increased, each index value before the comparative treatment was decreased, but at the pyrolysis temperature of 180 ℃, each index value was relatively the lowest, so that the process pyrolysis temperature of 180 ℃ was determined.
Test example 2
screening the sweet potato vine, the sweet potato residue and the wormwood in proportion: fixing compound fertilizer, ceramsite and expanded vermiculite, and screening sweet potato vine, sweet potato residue and wormwood in proportion. The pig manure sewage is uniformly mixed and averagely divided into 9 groups:
1 group of sweet potato vine, sweet potato residue and wormwood in a ratio of 0:1
2 groups of sweet potato vine, sweet potato residue and wormwood in a ratio of 1:0:1
3 groups of sweet potato vine, sweet potato residue and wormwood are proportioned at the ratio of 1:1:0
4 groups of sweet potato vine, sweet potato residue and wormwood are mixed according to the proportion of 4:5:3
5 groups of sweet potato vine, sweet potato residue and wormwood are mixed according to the proportion of 4:7:3
6 groups of sweet potato vine, sweet potato residue and wormwood are proportioned at a ratio of 5:5:3
7 groups of sweet potato vine, sweet potato residue and wormwood are proportioned at a ratio of 5:7:3
8 groups of sweet potato vine, sweet potato residue and wormwood are mixed according to the proportion of 4:3:7
9 groups of sweet potato vine, sweet potato residue and wormwood are proportioned at a ratio of 5:3:7
screening is carried out by indexes of biochemical oxygen demand (BOD 5), chemical oxygen demand (CODcr) (mg/L), suspended matter (SS) (mg/L) and ammonia nitrogen (NH 3-N) (mg/L) of the pig manure sewage. The results are as follows:
The results show that the index values of each group are reduced before the comparison treatment, and the index values of each group are reduced to a large extent compared with the index values of 1-3 groups and 4-9 groups, which indicates that the sweet potato vine, the sweet potato residue and the wormwood have a synergistic effect and are all absent. Meanwhile, when the ratio of the sweet potato vine to the sweet potato residue to the wormwood is 4:7:3, the index value is the lowest, so that the ratio of the sweet potato vine to the sweet potato residue to the wormwood is 4:7: 3.
Test example 3
The biological fillers prepared in examples 1, 2 and 3 are subjected to sewage treatment, and wastewater treatment is performed by taking pig manure sewage (average water quality is shown in the following table) as an example according to the discharge standard of pollutants for livestock and poultry breeding (GB 18596-2001). The results are shown in the following table:
According to the results, before comparison treatment, the index values of all groups are reduced and reach the discharge standard GB18596-2001 of pollutants for livestock and poultry breeding, and the effect of example 1 is optimal.

Claims (10)

1. the biological filler for treating the livestock and poultry wastewater is characterized by consisting of sweet potato vines, sweet potato residues, wormwood, a modifier and a base material.
2. The biological filler for treating livestock and poultry wastewater according to claim 1, which is characterized by comprising the following components in percentage by weight: 1-30% of sweet potato vine, 1-60% of sweet potato residue, 1-30% of wormwood, 1-50% of modified solvent and 1-30% of base material.
3. The biological filler for treating livestock and poultry wastewater according to claim 1, which is characterized by comprising the following components in percentage by weight: 10-20% of sweet potato vine, 10-40% of sweet potato residue, 10-20% of wormwood, 20-40% of modified solvent and 10-20% of base material.
4. The biological filler for treating livestock and poultry wastewater according to claim 1, which is characterized by comprising the following components in percentage by weight: 16-20% of sweet potato vine, 10-28% of sweet potato residue, 12-20% of wormwood, 20-36% of modified solvent and 10-16% of base material.
5. The biological filler for treating livestock and poultry wastewater according to claim 1, wherein the modifier is composed of one or more of compound fertilizer, potassium chloride, ammonium phosphate, urea and silicon-containing fertilizer.
6. The biological filler for treating livestock and poultry wastewater as claimed in claim 1, wherein the substrate is composed of one or more of ceramsite, expanded vermiculite, sepiolite and zeolite.
7. The biological filler for treating livestock wastewater according to claim 1, which is prepared by the following steps:
1) Pulverizing sweet potato vine and wormwood in a pulverizer, adding sweet potato residue, mixing, stirring, and mixing uniformly;
2) Putting the mixture 1) into a reaction tank, steaming for 4-5 hours at 100-200 ℃ under the anoxic or anaerobic condition, then cooling to 50-60 ℃, adding compound fertilizer and water, stirring for 1-2 hours at 40-50 ℃, cooling, drying and reserving for later use;
3) Mixing the mixture obtained in the step 2) with ceramsite and expanded vermiculite, and compressing the mixture into blocks by a press machine to obtain biomass blocks;
4) Soaking the mixture 3) in 0.2-2mol/L potassium chloride solution for 3-5 hours, taking out the soaked mixture, and drying the soaked mixture; and compressing the mixture into blocks by a press machine again to obtain the biomass blocks.
8. The biological filler for treating livestock and poultry wastewater according to claim 7, wherein the weight ratio of sweet potato vine: sweet potato residue: the mass ratio of the wormwood is 1-5:1-7: 1-7; the mass ratio of the compound fertilizer to the water is 0.8:10-8: 10; the mass ratio of the ceramsite to the expanded vermiculite is 0.25:1-2.5: 1.
9. The biological filler for treating livestock wastewater according to any one of claims 1-8, wherein the application method of the filler is as follows: and (3) putting the obtained biomass blocks into a livestock and poultry wastewater pool, soaking for 10-24 hours, taking out, scattering, covering a layer of rice straw on the surface, and composting.
10. A biological filler for treating livestock and poultry wastewater is characterized by being applied to treating livestock and poultry wastewater.
CN201910833855.5A 2019-09-04 2019-09-04 Biological filler for treating livestock and poultry wastewater Pending CN110550725A (en)

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Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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CN104261550A (en) * 2014-10-10 2015-01-07 徐震霖 Biological composite filler for treating livestock wastewater, preparation method and application of biological composite filler
CN105341317A (en) * 2014-08-21 2016-02-24 青岛诚一知识产权服务有限公司 Ecological pig-raising fermentation bed packing
CN105923905A (en) * 2016-05-20 2016-09-07 和县伊迈炭业有限责任公司 Biological stuffing for industrial sewage treatment and preparation method thereof

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003205298A (en) * 2002-01-15 2003-07-22 Uno Juko Kk Treatment apparatus for sewage containing domestic animal urine
CN105341317A (en) * 2014-08-21 2016-02-24 青岛诚一知识产权服务有限公司 Ecological pig-raising fermentation bed packing
CN104229976A (en) * 2014-10-10 2014-12-24 徐震霖 Method for processing livestock waste water through bio-compound fillers
CN104261550A (en) * 2014-10-10 2015-01-07 徐震霖 Biological composite filler for treating livestock wastewater, preparation method and application of biological composite filler
CN105923905A (en) * 2016-05-20 2016-09-07 和县伊迈炭业有限责任公司 Biological stuffing for industrial sewage treatment and preparation method thereof

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Application publication date: 20191210