CN108191499A - A kind of organic fertilizer and its production method using sludge production - Google Patents
A kind of organic fertilizer and its production method using sludge production Download PDFInfo
- Publication number
- CN108191499A CN108191499A CN201810179909.6A CN201810179909A CN108191499A CN 108191499 A CN108191499 A CN 108191499A CN 201810179909 A CN201810179909 A CN 201810179909A CN 108191499 A CN108191499 A CN 108191499A
- Authority
- CN
- China
- Prior art keywords
- sludge
- parts
- mixture
- organic fertilizer
- fertilizer
- 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
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F7/00—Fertilisers from waste water, sewage sludge, sea slime, ooze or similar masses
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05B—PHOSPHATIC FERTILISERS
- C05B7/00—Fertilisers based essentially on alkali or ammonium orthophosphates
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05G—MIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
- C05G1/00—Mixtures of fertilisers belonging individually to different subclasses of C05
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/10—Process efficiency
- Y02P20/133—Renewable energy sources, e.g. sunlight
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Pest Control & Pesticides (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Fertilizers (AREA)
- Treatment Of Sludge (AREA)
Abstract
The invention discloses a kind of organic fertilizers and its production method using sludge production, according to parts by weight, are made of the following raw material：300 600 parts of sludge drying particles, 60 80 parts of turf mixtures, 12 parts of calcium phosphate, 26 parts of potassium chloride, ammonium chloride and 30 80 parts of 15 25 parts of nitric acid calcium compound, 20 60 parts of fowl and animal excrement mixture, sawdust and stalk comminuted material mixture；It is fermented by sludge, and pass through the combination with organic fertilizer, it adds in micro inorganic fertilizer and so that the nutrient of the fertilizer is more sufficient, chemical breakdown is carried out by the pernicious gas for generating sludge, ingredient useful in sludge with organic fertilizer is adequately combined, does not need to apply chemical fertilizer again, it can directly be absorbed by root system of plant, and soil texture will not be had an impact, its nutritional ingredient structure is reduced, has the ability that can be recycled.
Description
Technical field
The present invention relates to field of organic fertilizer production, specially a kind of organic fertilizer and its producer produced using sludge
Method.
Background technology
For guarantee, we have clean domestic water, basic each city Dou You sewage treatment plants.However, sewage
The domestic sludge that treatment plant generates, always is the problem of allowing environmental protection administration's headache, because these sludge are rich in large amount of organic
Matter and pathogen, worm's ovum, ruderal species are also easy to produce the raw mosquitos and flies of stench, evil, pollution environment.It is main at present to use landfill, fill out sea and burn
Three kinds of processing methods are burnt, the processing method of the prior art easily causes secondary environmental pollution and wastes a large amount of organic manure resource,
Sludge yield is huge and complicated component, how to sludge treatment with using having become the problem of concerned.Sludge is that have
Living resources, as can rationally utilizing can not only then turn waste into wealth, moreover it is possible to increase economic benefit, at present both at home and abroad at each sewage
The method for sludge treatment of reason factory mainly has drying, digestion, compost, burning, utilizes.These methods are continuous in engineering practice
Expose some shortcoming and defect：
1st, sludge digestion, sludge digestion technology mainly have two kinds of aerobic sigestion and anaerobic digestion.Anaerobic digestion methane phase can
To offset the processing cost of partial sludge, aerobic sigestion operating cost is higher, and application is less.Self-heating developed in recent years
Aerobic sigestion technology is a kind of beneficial trial, but the technology only has small-scale engineer application in America and Europe, but need to there are still residue
It handles, the country not yet reports.
2nd, sludge sanitary landfills, it is aqueous for the sludge of landfill with the appearance of new sludge blended landfill shale standard
Rate must be down to less than 60%.It is individually added unlike PAM with traditional chemical conditioning process, in order to ensure dehydration efficiency, this sets
The medicament that standby pre-conditioning adds is inorganic, such as lime, aluminium salt and molysite, this technology take up an area it is big, there are secondary pollution,
It can not later-stage utilization.
3rd, sludge composting is agricultural, there is agricultural difficult point after sludge composting, and compost treatment needs certain technical conditions, cost
It is high；Product difficulty touches the mark requirement and market product sales difficulty after compost treatment.Mainly there are anaerobic composting and aerobic compost two
Kind.Due to using aerobic compost mode, sludge organic matter degradation is more efficient, and foul gas is less, and the period is short, therefore most of heap
Fertile engineering system is all using aerobic compost, and this technology is taken up an area greatly, and still secondary pollution is of high cost.
4th, pyrolyzing sludge is that sludge is sent into pyrolysis oven, and the gas come out from drier is in cooling column through cooling down condensing go
It can in a combustion chamber be used as combustion gas after water.It is pyrolyzed the gas generated recyclable oil or heat after cooling.Gas imports
It burns at 800 DEG C or more combustion chamber.The high-temperature gas that combustion chamber generates generates steam for drying in waste heat boiler, if energy
Can be in combustion chamber auxiliary fuel when insufficient, this technology operation cost is excessively high, and market is beyond affordability.
Invention content
In order to overcome the shortcomings of prior art, the present invention provides a kind of organic fertilizer using sludge production and its production
Method carries out chemical breakdown by the pernicious gas for generating sludge, ingredient useful in sludge is adequately tied with organic fertilizer
It closes, can effectively solve the problem that the problem of background technology proposes.
The technical solution adopted by the present invention to solve the technical problems is：
A kind of organic fertilizer produced using sludge, according to parts by weight, is made of the following raw material：
300-600 parts of sludge drying particles, 60-80 parts of turf mixtures, 1-2 parts of calcium phosphate, potassium chloride and ammonium chloride with
And 15-25 parts of the mixture of calcium nitrate, 20-60 parts of fowl and animal excrement mixture, sawdust and stalk comminuted material mixture 30-80
Part.
Further, 450 parts of particle of sludge drying, 70 parts of turf mixture, 1 part of calcium phosphate, potassium chloride and ammonium chloride with
And 20 parts of nitric acid calcium compound, 50 parts of fowl and animal excrement mixture, sawdust and stalk comminuted material 70 parts of mixture.
Further, the turf mixture includes the mixture of powders after weeds, straw, stalk and branch burning.
Further, the mixture of the potassium chloride and ammonium chloride and calcium nitrate is 1 according to mass ratio：4:20.
In addition, the present invention also provides a kind of production method of the organic fertilizer using sludge production, include the following steps：
S100, sludge is put into sludge container and is fermented, fermentation time is 3-7 days, completes later in fermentation
Then gas in sludge container adds in turf mixture, chlorine by the sodium hydroxide solution that purity is 20% in sludge
The mixture for changing potassium and the mixture of ammonium chloride and calcium nitrate, sawdust and stalk comminuted material is stirred；
S200, sludge is sent into evaporation tank, is toasted by hot-air by the moisture evaporation in sludge to 15%-30%,
And squeeze and form solid soil block shape, soil block is then crushed to a diameter of 3mm-5mm's by block-like soil by pulverizer
Particle, and high-temperature sterilization is carried out to grogs；
S300, fowl and animal excrement mixture are by after being exposed to the sun, forming solid-state, and carry out high-temperature sterilization, later in outdoor
It places 2-3 days and is air-dried；
S400, grogs and the fowl and animal excrement mixture mixing after drying, and stir evenly.
Further, in the step s 100, the gas in sludge container passes through the specific of 20% sodium hydroxide solution
Step is：
S101, sludge container bottom by pressing upwards on the volume-diminished of sludge container, by sludge container
The gas of upper part is discharged to the tank body equipped with 20% sodium hydroxide solution by the discharge line at top；
S102, sodium hydroxide solution is concentrated, and using the sodium hydroxide solution after concentration as PH regulated values to dirt
Mud carries out acid-base value adjusting.
Further, in step s 200, the concrete mode of grogs high-temperature sterilization is heat-flash air, wherein disappearing by high temperature
The time of poison is 5-8 minutes, and the temperature sterilized is 150-180 DEG C.
Compared with prior art, the beneficial effects of the invention are as follows：
(1) present invention, by the combination with organic fertilizer, adds in micro inorganic fertilizer by the way that sludge is carried out storage fermentation
So that the nutrient of the fertilizer is more sufficient, do not need to apply chemical fertilizer again, and the exhaust gas for generation of fermenting is comprehensively utilized, pass through
Sodium hydroxide solution fixes nutritional ingredient therein, comprehensively utilizes again into fertilizer；
(2) present invention is different with common fertilizer, and general fertilizer needs are buried in beneath or need to be exposed to soil
Surface, and the fertilizer can be mixed with soil, property is directly sprinkling upon near the root of plant i.e. closer to the property of soil
Can, it can directly be absorbed by root system of plant, and soil texture will not be had an impact, reduce its nutritional ingredient structure, had
The standby ability that can be recycled.
Description of the drawings
Fig. 1 is the overall flow schematic diagram of the present invention.
Specific embodiment
Below in conjunction with the attached drawing in the embodiment of the present invention, the technical solution in the embodiment of the present invention is carried out clear, complete
Site preparation describes, it is clear that described embodiment is only part of the embodiment of the present invention, instead of all the embodiments.It is based on
Embodiment in the present invention, those of ordinary skill in the art are obtained every other without making creative work
Embodiment shall fall within the protection scope of the present invention.
As shown in Figure 1, a kind of organic fertilizer produced using sludge, according to parts by weight, is made of the following raw material：
300-600 parts of sludge drying particles, 60-80 parts of turf mixtures, 1-2 parts of calcium phosphate, potassium chloride and ammonium chloride with
And 15-25 parts of the mixture of calcium nitrate, 20-60 parts of fowl and animal excrement mixture, sawdust and stalk comminuted material mixture 30-80
Part.
Further, 450 parts of particle of sludge drying, 70 parts of turf mixture, 1 part of calcium phosphate, potassium chloride and ammonium chloride with
And 20 parts of nitric acid calcium compound, 50 parts of fowl and animal excrement mixture, sawdust and stalk comminuted material 70 parts of mixture.
Further, the turf mixture includes the mixture of powders after weeds, straw, stalk and branch burning.
Further, the mixture of the potassium chloride and ammonium chloride and calcium nitrate is 1 according to mass ratio：4:20.
In addition, the present invention also provides a kind of production method of the organic fertilizer using sludge production, include the following steps：
Step S100, sludge is put into sludge container and fermented, fermentation time is 3-7 days, is completed in fermentation
Afterwards then the gas in sludge container is added in into turf mixing by the sodium hydroxide solution that purity is 20% in sludge
The mixture of the mixture of object, potassium chloride and ammonium chloride and calcium nitrate, sawdust and stalk comminuted material is stirred.
In above-mentioned steps, the adjusting of sludge acid-base value is further included, the wherein gas in sludge container passes through 20%
Sodium hydroxide solution the specific steps are：
Step S101, the bottom of sludge container is by pressing upwards on the volume-diminished of sludge container, by sludge collection
The gas of part is discharged to the tank body equipped with 20% sodium hydroxide solution by the discharge line at top in vanning.
The gas that sludge generally generates mainly has methane, carbon dioxide and hydrogen sulfide, and hydrogen sulfide is main polluted gas,
And this 3 kinds of gases can then be neutralized to hydrogen sulfide by sodium hydroxide solution, and sodium hydroxide solution and carbon dioxide can be anti-
Sodium carbonate or sodium bicarbonate should be obtained, sodium carbonate and sodium bicarbonate can also recycle.
Step S102, sodium hydroxide solution is concentrated, and using the sodium hydroxide solution after concentration as PH regulated values
Acid-base value adjusting is carried out to sludge.
It is in addition, after the turf mixture fully burns including weeds, part straw, stalk and branch and inabundant
Ash behind part after burning, fully burning is then mixed with sludge, and the opportunity of mixing is is preferred when sludge can also stir dynamic.
It may further be preferable that potassium chloride, ammonium chloride and nitric acid calcium compound are added to make the nutrient of fertilizer more to fill
Foot more comprehensively, does not need to carry out again to add chemical fertilizer, can need progress dosage, Ke Yifen according to plant when adding these types of substance
Class, some can add, some can be not added with.
S200, sludge is sent into evaporation tank, is toasted by hot-air by the moisture evaporation in sludge to 15%-30%,
And squeeze and form solid soil block shape, soil block is then crushed to a diameter of 3mm-5mm's by block-like soil by pulverizer
Particle, and high-temperature sterilization is carried out to grogs；
S300, fowl and animal excrement mixture are by after being exposed to the sun, forming solid-state, and carry out high-temperature sterilization, later in outdoor
It places 2-3 days and is air-dried.
Wherein, fowl and animal excrement mixture carries out drying of being exposed to the sun first, and the degree of drying is also required to grasp, be pinched with hand,
Firmly can pinching then just, should not be too dry, also unsuitable overly wet, fowl and animal excrement mixture has further included part great soil group impurity.
S400, grogs and the fowl and animal excrement mixture mixing after drying, and stir evenly.
Further, in step s 200, the concrete mode of grogs high-temperature sterilization is heat-flash air, wherein disappearing by high temperature
The time of poison is 5-8 minutes, and the temperature sterilized is 150-180 DEG C.
Due to containing many machine substance and pathogen, worm's ovum, ruderal species etc. in sludge, these substances are for fertilizer
It does not act on then, grass and crops contention nutrient will be grown after germinateing as ruderal species, it is therefore desirable to by 150-180 DEG C
High-temperature process, eliminate a part of unwanted substance to reach.
It should be further noted that during entire stirring and heating, it is straight that a part of energy can be first filtered in sludge
The sewage under filter is taken over, is directly discharged to the processing that cesspool carries out sewage, remaining soil block includes after reducing sludge evaporation
Some objectionable impurities are excessive, so as to influence the actual effect of fertilizer.
For the technical program, by the way that sludge carried out storage fermentation, and with the combination of organic fertilizer, add in micro
Inorganic fertilizer so that the nutrient of the fertilizer is more sufficient, does not need to apply chemical fertilizer again, and the exhaust gas for generation of fermenting is carried out comprehensive profit
With, nutritional ingredient therein is fixed by sodium hydroxide solution, is comprehensively utilized again into fertilizer, the fertilizer can and soil
Mixing, closer to the property of soil, the root for being directly sprinkling upon plant nearby, can directly be inhaled property by root system of plant
It receives, and soil texture will not be had an impact, reduce its nutritional ingredient structure, have the ability that can be recycled.
It is obvious to a person skilled in the art that the present invention is not limited to the details of above-mentioned exemplary embodiment, Er Qie
In the case of without departing substantially from spirit or essential attributes of the invention, the present invention can be realized in other specific forms.Therefore, no matter
From the point of view of which point, the present embodiments are to be considered as illustrative and not restrictive, and the scope of the present invention is by appended power
Profit requirement rather than above description limit, it is intended that all by what is fallen within the meaning and scope of the equivalent requirements of the claims
Variation is included within the present invention.Any reference numeral in claim should not be considered as to the involved claim of limitation.
Claims (7)
1. a kind of organic fertilizer produced using sludge, which is characterized in that according to parts by weight, be made of the following raw material：
300-600 parts of sludge drying particles, 60-80 parts of turf mixtures, 1-2 parts of calcium phosphate, potassium chloride and ammonium chloride and nitre
30-80 parts of the mixture of 20-60 parts of 15-25 parts of mixture, the fowl and animal excrement mixture of sour calcium, sawdust and stalk comminuted material.
2. a kind of organic fertilizer produced using sludge according to claim 1, it is characterised in that：Sludge dries particle 450
Part, 70 parts of turf mixture, 1 part of calcium phosphate, potassium chloride and ammonium chloride and 20 parts of nitric acid calcium compound, fowl and animal excrement mixture
50 parts, 70 parts of the mixture of sawdust and stalk comminuted material.
3. a kind of organic fertilizer produced using sludge according to claim 1, it is characterised in that：The turf mixture packet
Include the mixture of powders after weeds, straw, stalk and branch burning.
4. a kind of organic fertilizer produced using sludge according to claim 1, it is characterised in that：The potassium chloride and chlorination
The mixture of ammonium and calcium nitrate is 1 according to mass ratio：4:20.
5. the production method of a kind of organic fertilizer using sludge production, which is characterized in that include the following steps：
S100, sludge is put into sludge container and is fermented, fermentation time is 3-7 days, by sludge after completion of fermenting
Then gas in container adds in turf mixture, potassium chloride by the sodium hydroxide solution that purity is 20% in sludge
It is stirred with the mixture of the mixture of ammonium chloride and calcium nitrate, sawdust and stalk comminuted material；
S200, sludge is sent into evaporation tank, is toasted by hot-air by the moisture evaporation in sludge to 15%-30%, and squeeze
Soil block is then crushed to the particle of a diameter of 3mm-5mm into solid soil block shape by swaging by block-like soil by pulverizer,
And high-temperature sterilization is carried out to grogs；
S300, fowl and animal excrement mixture are by after being exposed to the sun, forming solid-state, and carry out high-temperature sterilization, later in outdoor placement
It is air-dried within 2-3 days；
S400, grogs and the fowl and animal excrement mixture mixing after drying, and stir evenly.
6. the production method of a kind of organic fertilizer using sludge production according to claim 5, which is characterized in that in step
In S100, gas in sludge container by 20% sodium hydroxide solution the specific steps are：
S101, sludge container bottom by pressing upwards on the volume-diminished of sludge container, by sludge packaging upper box part
The gas divided is discharged to the tank body equipped with 20% sodium hydroxide solution by the discharge line at top；
S102, sodium hydroxide solution is concentrated, and using the sodium hydroxide solution after concentration as PH regulated values to sludge into
Row acid-base value is adjusted.
7. the production method of a kind of organic fertilizer using sludge production according to claim 5, which is characterized in that in step
In S200, the concrete mode of grogs high-temperature sterilization is heat-flash air, wherein the time by high-temperature sterilization is 5-8 minutes, and disappear
The temperature of poison is 150-180 DEG C.
Priority Applications (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810179909.6A CN108191499A (en) | 2018-03-05 | 2018-03-05 | A kind of organic fertilizer and its production method using sludge production |
| PCT/CN2018/092063 WO2019169786A1 (en) | 2018-03-05 | 2018-06-20 | Organic fertilizer produced with sludge and production method therefor |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810179909.6A CN108191499A (en) | 2018-03-05 | 2018-03-05 | A kind of organic fertilizer and its production method using sludge production |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN108191499A true CN108191499A (en) | 2018-06-22 |
Family
ID=62595071
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201810179909.6A Pending CN108191499A (en) | 2018-03-05 | 2018-03-05 | A kind of organic fertilizer and its production method using sludge production |
Country Status (2)
| Country | Link |
|---|---|
| CN (1) | CN108191499A (en) |
| WO (1) | WO2019169786A1 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN116553974A (en) * | 2023-05-19 | 2023-08-08 | 内蒙古蒙土生态环保科技有限公司 | Special base fertilizer for eucalyptus and preparation method thereof |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101830756A (en) * | 2010-05-12 | 2010-09-15 | 英联国际化学品（北京）有限公司 | Green process for producing organic fertilizer by aerobic fermentation of multi-microorganism |
| CN102351589A (en) * | 2011-07-14 | 2012-02-15 | 李桓宇 | Bio-organic fertilizer produced by use of municipal sludge and production method thereof |
| CN104529596A (en) * | 2015-01-16 | 2015-04-22 | 南开大学 | Method for producing organic fertilizer by use of pretreated sludge |
| CN106495834A (en) * | 2016-10-09 | 2017-03-15 | 洛阳茂生生物技术有限公司 | A kind of method that utilization sludge prepares fertilizer |
Family Cites Families (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101823911A (en) * | 2009-03-08 | 2010-09-08 | 林炳营 | Bio-organic fertilizer special for dry saline-alkali plowland |
| KR20130065891A (en) * | 2011-12-12 | 2013-06-20 | 서희동 | Method for treating organic wastes |
| CN102603375A (en) * | 2012-04-01 | 2012-07-25 | 江苏田娘农业科技有限公司 | Sewage sludge compost and preparation method of sewage sludge compost |
| CN103086769B (en) * | 2013-01-25 | 2015-04-08 | 福建省星源农牧科技股份有限公司 | Dragon fruit-purposed high-potassium organic fertilizer prepared from domestic sludge and fowl manure and production method thereof |
| CN104671842A (en) * | 2013-11-28 | 2015-06-03 | 山东农棵源生物科技有限公司 | Preparation method for sludge biological organic fertilizer |
| CN103920378B (en) * | 2014-05-08 | 2016-03-09 | 山东天力干燥股份有限公司 | A kind of municipal sludge drying tail gas treating apparatus and method |
| CN104163553A (en) * | 2014-08-01 | 2014-11-26 | 刘欢欢 | Sludge treatment method |
| CN107384420A (en) * | 2017-07-25 | 2017-11-24 | 中国冶集团有限公司 | Sludge soil conditioner, preparation method and applications |
-
2018
- 2018-03-05 CN CN201810179909.6A patent/CN108191499A/en active Pending
- 2018-06-20 WO PCT/CN2018/092063 patent/WO2019169786A1/en active Application Filing
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101830756A (en) * | 2010-05-12 | 2010-09-15 | 英联国际化学品（北京）有限公司 | Green process for producing organic fertilizer by aerobic fermentation of multi-microorganism |
| CN102351589A (en) * | 2011-07-14 | 2012-02-15 | 李桓宇 | Bio-organic fertilizer produced by use of municipal sludge and production method thereof |
| CN104529596A (en) * | 2015-01-16 | 2015-04-22 | 南开大学 | Method for producing organic fertilizer by use of pretreated sludge |
| CN106495834A (en) * | 2016-10-09 | 2017-03-15 | 洛阳茂生生物技术有限公司 | A kind of method that utilization sludge prepares fertilizer |
Non-Patent Citations (2)
| Title |
|---|
| 李章海等: "《有机肥条垛型堆积发酵技术与应用》", 30 June 2015, 中国科学技术大学出版社 * |
| 韩宝平等: "《固体废物处理与应用》", 30 June 2010, 华中科技大学出版社 * |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN116553974A (en) * | 2023-05-19 | 2023-08-08 | 内蒙古蒙土生态环保科技有限公司 | Special base fertilizer for eucalyptus and preparation method thereof |
Also Published As
| Publication number | Publication date |
|---|---|
| WO2019169786A1 (en) | 2019-09-12 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN101333123B (en) | Process for reclaiming city domestic sludge | |
| CN103396857B (en) | Rank vegetation plantation and comprehensive utilization substitute the apparatus and method of fossil energy | |
| CN104387136B (en) | Method for producing organic fertilizer from municipal dry branch/fallen leaf waste and application thereof | |
| CN104150987B (en) | A kind of method of animal waste recycling | |
| CN101708938B (en) | Sludge or organic garbage high-low temperature coupling themolysis method | |
| CN104830397B (en) | A kind of compound high-temperature environmental-protection biomass fuel and preparation method thereof | |
| CN105175044B (en) | A kind of composting system and its compost method containing biomass carbon | |
| CN103588515B (en) | Urban and rural waste treatment method | |
| CN103766035B (en) | Root stubble, the high-efficient treatment method of straw-returning | |
| CN204509147U (en) | A kind of device of agricultural wastes high temperature quick fermentation production fertilizer | |
| CN101659582B (en) | Method for rapidly converting animal-poultry faeces into high-efficiency fertilizer | |
| CN101838090B (en) | Method for treating sludge of urban sewage treatment plants in controllable composting mode | |
| CN102603383B (en) | Production equipment and preparation method of slow-release bio-organic fertilizer | |
| CN103787750A (en) | Charcoal livestock and poultry excrement composting conditioner and preparation and use method thereof | |
| CN103242069A (en) | Sludge resource utilization method | |
| CN104829378A (en) | Watermelon fertilizer and preparation method thereof | |
| CN104804794A (en) | Environment-friendly high-energy composite biomass fuel and preparation method thereof | |
| CN102093137B (en) | Method and system for treating residual sludge by solar energy thermal radiation oxygen-enriched fermentation | |
| CN104140820A (en) | Desertification and degeneration soil modifier made of organic waste and active coke | |
| CN104193130B (en) | A kind for the treatment of process of sewage plant sludge | |
| CN110639931A (en) | Process for coupling kitchen waste and biomass to coproduce oil, electricity, steam and carbon | |
| CN105037019A (en) | Coal cinder organic fertilizer special for walnuts and preparation method thereof | |
| CN108276034A (en) | A kind of method that four useless disposal of resources derives organic fertilizer | |
| CN103553845A (en) | Technology for preparing soil loosening and adjusting fertilizer through treatment of grass carbon ash strong alkali wastewater in straw burning power plant | |
| CN104250171A (en) | Preparation method for charcoal base fertilizer |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| TA01 | Transfer of patent application right |
Effective date of registration: 20200520 Address after: 610000 room 2107, 21 / F, unit 1, building 4, no.1700, north section of Tianfu Avenue, Chengdu high tech Zone, China (Sichuan) pilot Free Trade Zone, Chengdu Applicant after: Sichuan Yihe Shengda Environmental Protection Technology Co., Ltd Address before: 610000 Chengdu, Sichuan, China (Sichuan) free trade pilot area, Chengdu City hi tech Zone, 3 north 3 of the 3 section of Tianfu Avenue 14 units. Applicant before: SICHUAN DEMINGSI TECHNOLOGY Co.,Ltd. |
|
| TA01 | Transfer of patent application right | ||
| WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20180622 |
|
| WD01 | Invention patent application deemed withdrawn after publication |