CN108029270A - A kind of beach saline land comprehensive processing method - Google Patents
A kind of beach saline land comprehensive processing method Download PDFInfo
- Publication number
- CN108029270A CN108029270A CN201711228598.XA CN201711228598A CN108029270A CN 108029270 A CN108029270 A CN 108029270A CN 201711228598 A CN201711228598 A CN 201711228598A CN 108029270 A CN108029270 A CN 108029270A
- Authority
- CN
- China
- Prior art keywords
- parts
- weight
- soil
- processing method
- hundred million
- 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
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01B—SOIL WORKING IN AGRICULTURE OR FORESTRY; PARTS, DETAILS, OR ACCESSORIES OF AGRICULTURAL MACHINES OR IMPLEMENTS, IN GENERAL
- A01B79/00—Methods for working soil
- A01B79/02—Methods for working soil combined with other agricultural processing, e.g. fertilising, planting
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D1/00—Fertilisers containing potassium
- C05D1/04—Fertilisers containing potassium from minerals or volcanic rocks
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F5/00—Fertilisers from distillery wastes, molasses, vinasses, sugar plant or similar wastes or residues, e.g. from waste originating from industrial processing of raw material of agricultural origin or derived products thereof
- C05F5/002—Solid waste from mechanical processing of material, e.g. seed coats, olive pits, almond shells, fruit residue, rice hulls
-
- 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
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
-
- 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
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
- C05G3/80—Soil conditioners
-
- 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
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
- C05G3/90—Mixtures of one or more fertilisers with additives not having a specially fertilising activity for affecting the nitrification of ammonium compounds or urea in the soil
-
- 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
- Y02A40/22—Improving land use; Improving water use or availability; Controlling erosion
-
- 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
- Y02P60/00—Technologies relating to agriculture, livestock or agroalimentary industries
- Y02P60/20—Reduction of greenhouse gas [GHG] emissions in agriculture, e.g. CO2
- Y02P60/21—Dinitrogen oxide [N2O], e.g. using aquaponics, hydroponics or efficiency measures
-
- 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Soil Sciences (AREA)
- Pest Control & Pesticides (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Mechanical Engineering (AREA)
- Environmental & Geological Engineering (AREA)
- General Chemical & Material Sciences (AREA)
- Geology (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Biochemistry (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geochemistry & Mineralogy (AREA)
- Biotechnology (AREA)
- Inorganic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Environmental Sciences (AREA)
- Botany (AREA)
- Treatment Of Sludge (AREA)
- Fertilizers (AREA)
Abstract
The present invention relates to a kind of alkaline land improving technical field, and in particular to a kind of beach saline land comprehensive processing method, comprises the following steps：Step 1：Plowed soils, obtains scarifying soil, the mixture of sulphur and biomass carbon is added in scarifying soil and is mixed, again plowed soils, kept for 10 30 days；Step 2：Microbial fermentation pond sludge is added to soil, plowed soils, is kept for 10 30 days；Step 3：Apply organic fertilizer, plowed soils.The present invention can improve soil texture, increase topsoil moisture holding capacity and water penetration, promote salinity to migrate downward into, and improve desalination speed；Increase soil with organic matter content, crops is obtained full nutrition in whole growing process；It is obvious to reduce soil ESP and pH value：Heavy salinized native pH value and ESP values can be made to decline rapidly, reach dealkalize desalting effect within a short period of time, promote crop being capable of normal growth；Raw material re-uses for discarded object, and input cost is low, environmentally protective.
Description
Technical field
The present invention relates to a kind of alkaline land improving technical field, and in particular to a kind of beach saline land comprehensive processing method.
Background technology
Large stretch of salt-soda soil is distributed with China, and the degree of salinization of soil is expanding, especially coastal region.Soil is saline and alkaline
Change not only so that agriculture a large amount of underproduction in China, cause very big loss, due also to being on the rise for salinization and alkalization, makes
Obtain tract to be increasingly becoming uselessly, not even a blade of grass grows, and No kernels or seeds are gathered, as in a year of scarcity.
The agricultural production amount of Saline is simultaneously improved in transformation salt-soda soil, is one of vital task of China's agricultural development, so
And the method for traditional saline-alkali land soil conditioner is mainly relatively simple using the sodium in gypsum displacement soil, such a method.
As CN1377936A inventions disclosed are entitled：Using waste gypsum plate production saline-alkali soil conditioner method and products thereof and should
It is entitled with, CN1487052A inventions disclosed：Saline soil, it is the exchangeable sodium replaced with calcium sulfate in soil,
Since the use of a large amount of calcium sulfate adds the salinity of soil, thus need to elute, i.e., the use of this kind soil conditioner needs
Coordinate use of pouring water.It is easily hardened the soil in salt-soda soil is not can effectively improve yet with above-mentioned modifying agent, so soil leads to
Permeability is poor, and moisture is difficult to permeate downwards, rainwash is produced, so that salinity is difficult to elute in soil.
The content of the invention
In order to overcome shortcoming and defect existing in the prior art, being provided it is an object of the invention to one kind to be effectively improved
Soil hardening, the beach saline land comprehensive processing method for improving desalination speed.
The purpose of the present invention is achieved through the following technical solutions：
A kind of beach saline land comprehensive processing method, comprises the following steps：
Step 1：Plowed soils, obtains scarifying soil, the mixture of sulphur and biomass carbon is added in scarifying soil and is mixed, again
Plowed soils, is kept for 10-30 days；
Step 2：Microbial fermentation pond sludge will be added after step 2 is handled by soil, plowed soils, is kept for 10-30 days；
Step 3：Apply organic fertilizer, plowed soils.
In step 1 of the present invention, the addition of sulphur can not only reduce saline-alkali soil pH value, adjust soil acidity or alkalinity, can also kill
Bacterium.Biomass carbon can improve soil hardening in this step, be conducive to sulphur and preferably play effect, of the invention other
In step, biomass carbon also helps the lasting performance of fertilizer.Microbial fermentation pond sludge it is penetrating can to improve soil with chesson
Property and retain water and nutrients ability, the potential nutrients in activating soil；Organic fertilizer further enhances soil fertility, improves in soil and supports
The supply situation divided.
Preferably, the biomass carbon is by the rice husk of 50-100 parts by weight, the potassium shale of 1-5 parts by weight, 10-20 weight
The pond sludge of part, 500-700 degrees Celsius of cracking forms the desulfurated plaster of 5-10 parts by weight under anoxic conditions.Potassium-bearing shale
The biomass carbon that adding makes contains abundant potassium element, is conducive to the raising of soil fertility.Desulfurated plaster can provide calcium
Ion, it forms cation exchange with the sodium ion in soil, can be effectively improved the structure of soil, and rice husk and pond sludge become
Waste be changed into values.
Preferably, the microbial fermentation pond sludge is that 5-30 parts by weight are sprinkled into the pond sludge of 100-200 parts by weight
Biomass charcoal powder, obtained after adding microbial bacterial agent fermentation.Microbial fermentation pond sludge can promote difficultly soluble nutrient in soil
Dissolving and release, improve the deliverability of soil nutrient.
Preferably, the dosage of microbial bacterial agent accounts for pond sludge 0.1-1wt%, which includes following component：Glue
Hundred million cfu/g of matter bacillus 0.5-1.5, hundred million cfu/g of bacillus laterosporus 1-3, hundred million cfu/g of saccharomycete 0.2-0.8, Lactococcus lactis
Hundred million cfu/g of bacterium 0.5-1.5, hundred million cfu/g of bacillus stearothermophilus 0.5-1.5, hundred million cfu/g of Streptomyces jingyangensis 0.2-0.8 and double
Hundred million cfu/g of enzyme clostridium 0.2-0.8.The microbial bacterial agent of the present invention can suppress or kill pathogenic bacteria, effectively can decompose pond dirt by bacterium
Organic matter in mud, produces a large amount of humic acid.
Preferably, the organic fertilizer is by 10-30 parts by weight soya-bean cake, 10-30 parts by weight peanut cake, 10-30 parts by weight
Rapeseed cake, 10-30 parts by weight cottonseed cake, 20-40 parts by weight dish leaf, 20-40 parts by weight melon and fruit peel, 5-10 parts by weight hops
Slag adds 10-50 parts by weight water by fermentation is decomposed to obtain.The above material combination can obtain the high organic fertilizer of nitrogen content, can with it is above-mentioned micro-
Biofermentation pond sludge is effectively coordinated.Microbial fermentation pond sludge is added after soil, the humic that microbial fermentation pond sludge is formed
Acid forms ammonium humate with the nitrogen in organic fertilizer, can reduce the loss of nitrogenous fertilizer.
Preferably, in the mixture of the sulphur and biomass carbon, sulphur accounts for 40-60wt%, the sulphur and biomass carbon
Mixture addition be 50-400kg/ mus.
Preferably, microbial fermentation pond sludge addition is kg/ mus of 500-2000.
Preferably, organic fertilizer addition is kg/ mus of 200-1000.
Preferably, ploughed depth 20-40cm.
The invention has the advantages that：
The addition of sulphur of the present invention can not only reduce saline-alkali soil pH value, adjust soil acidity or alkalinity, can also sterilize；Biomass carbon can
To improve soil hardening；Microbial fermentation pond sludge can improve soil permeability and retain water and nutrients ability, activated soil with chesson
Potential nutrients in earth；Organic fertilizer further enhances soil fertility, improves the supply situation of nutrient in soil.The present invention provides
Raw material used is substantially the re-using of discarded object, has the characteristics of input cost is low, environmentally protective.
To sum up, the present invention can improve soil texture, increase topsoil moisture holding capacity and water penetration, promote salinity to move downwards
Move, improve desalination speed；Present invention increase soil with organic matter content, makes crops be sought comprehensively in whole growing process
Support；It is obvious to reduce soil ESP and pH value：By using the method for the present invention, heavy salinized native pH value and ESP values can be made rapid
Decline, reach dealkalize desalting effect within a short period of time, promote crop being capable of normal growth.
Embodiment
For the ease of the understanding of those skilled in the art, with reference to embodiment, the present invention is further illustrated, embodiment party
The content that formula refers to not is limitation of the invention.
Embodiment 1
A kind of beach saline land comprehensive processing method, comprises the following steps：
Step 1：Plowed soils, obtains scarifying soil, the mixture of sulphur and biomass carbon is added in scarifying soil and is mixed, again
Plowed soils, is kept for 10 days；
Step 2：Microbial fermentation pond sludge will be added after step 2 is handled by soil, plowed soils, is kept for 10 days；
Step 3：Apply organic fertilizer, plowed soils.
The biomass carbon is by the rice husk of 50 parts by weight, the potassium shale of 1 parts by weight, the pond sludge of 10 parts by weight, 5 weights
500 degrees Celsius of cracking form the desulfurated plaster of amount part under anoxic conditions.
The microbial fermentation pond sludge is the biomass charcoal powder that 5 parts by weight are sprinkled into the pond sludge of 100 parts by weight, is added
Enter what is obtained after microbial bacterial agent ferments.
The dosage of microbial bacterial agent accounts for pond sludge 0.1wt%, which includes following component：Colloid gemma bar
It is 0.5 hundred million cfu/g of bacterium, 100,000,000 cfu/g of bacillus laterosporus, 0.2 hundred million cfu/g of saccharomycete, 0.5 hundred million cfu/g of Lactococcus lactis, thermophilic
0.2 hundred million cfu/g of 0.5 hundred million cfu/g of Bacillus stearothermophilus, 0.2 hundred million cfu/g of Streptomyces jingyangensis and clostridium bifermentans.
The organic fertilizer is by 10 parts by weight soya-bean cakes, 10 parts by weight peanut cakes, 10 parts by weight rapeseed cakes, 10 parts by weight
Cottonseed cake, 20 parts by weight dish leafs, 20 parts by weight melon and fruit peels, 5 parts by weight hop residues add 100 parts by weight water by fermentation are decomposed to obtain
's.
In the mixture of the sulphur and biomass carbon, sulphur accounts for 40wt%, and the mixture of the sulphur and biomass carbon adds
Enter amount for 50kg/ mus.
Microbial fermentation pond sludge addition is 500kg/ mus.
Organic fertilizer addition is 200kg/ mus.
Ploughed depth is 20cm.
Embodiment 2
A kind of beach saline land comprehensive processing method, comprises the following steps：
Step 1：Plowed soils, obtains scarifying soil, the mixture of sulphur and biomass carbon is added in scarifying soil and is mixed, again
Plowed soils, is kept for 15 days；
Step 2：Microbial fermentation pond sludge will be added after step 2 is handled by soil, plowed soils, is kept for 15 days；
Step 3：Apply organic fertilizer, plowed soils.
The biomass carbon is by the rice husk of 70 parts by weight, the potassium shale of 3 parts by weight, the pond sludge of 15 parts by weight, 8 weights
650 degrees Celsius of cracking form the desulfurated plaster of amount part under anoxic conditions.
The microbial fermentation pond sludge is the biomass charcoal powder that 20 parts by weight are sprinkled into the pond sludge of 150 parts by weight,
Add after microbial bacterial agent ferments what is obtained.
The dosage of microbial bacterial agent accounts for pond sludge 0.5wt%, which includes following component：Colloid gemma bar
It is 0.9 hundred million cfu/g of bacterium, 200,000,000 cfu/g of bacillus laterosporus, 0.6 hundred million cfu/g of saccharomycete, 0.9 hundred million cfu/g of Lactococcus lactis, thermophilic
0.8 hundred million cfu/g of 0.9 hundred million cfu/g of Bacillus stearothermophilus, 0.5 hundred million cfu/g of Streptomyces jingyangensis and clostridium bifermentans.
The organic fertilizer is by 15 parts by weight soya-bean cakes, 13 parts by weight peanut cakes, 17 parts by weight rapeseed cakes, 15 parts by weight
Cottonseed cake, 29 parts by weight dish leafs, 29 parts by weight melon and fruit peels, 8 parts by weight hop residues add 30 parts by weight water by fermentation are decomposed to obtain.
In the mixture of the sulphur and biomass carbon, sulphur accounts for 50wt%, and the mixture of the sulphur and biomass carbon adds
Enter amount for 250kg/ mus.
Microbial fermentation pond sludge addition is 1500kg/ mus.
Organic fertilizer addition is 500kg/ mus.
Ploughed depth is 30cm.
Embodiment 3
A kind of beach saline land comprehensive processing method, comprises the following steps：
Step 1：Plowed soils, obtains scarifying soil, the mixture of sulphur and biomass carbon is added in scarifying soil and is mixed, again
Plowed soils, is kept for 19 days；
Step 2：Microbial fermentation pond sludge will be added after step 2 is handled by soil, plowed soils, is kept for 21 days；
Step 3：Apply organic fertilizer, plowed soils.
The biomass carbon is by the rice husk of 80 parts by weight, the potassium shale of 3 parts by weight, the pond sludge of 17 parts by weight, 8 weights
600 degrees Celsius of cracking form the desulfurated plaster of amount part under anoxic conditions.
The microbial fermentation pond sludge is the biomass charcoal powder that 21 parts by weight are sprinkled into the pond sludge of 180 parts by weight,
Add after microbial bacterial agent ferments what is obtained.
The dosage of microbial bacterial agent accounts for pond sludge 0.7wt%, which includes following component：Colloid gemma bar
It is 1.5 hundred million cfu/g of bacterium, 200,000,000 cfu/g of bacillus laterosporus, 0.6 hundred million cfu/g of saccharomycete, 0.8 hundred million cfu/g of Lactococcus lactis, thermophilic
0.7 hundred million cfu/g of 1.5 hundred million cfu/g of Bacillus stearothermophilus, 0.6 hundred million cfu/g of Streptomyces jingyangensis and clostridium bifermentans.
The organic fertilizer is by 15 parts by weight soya-bean cakes, 20 parts by weight peanut cakes, 20 parts by weight rapeseed cakes, 20 parts by weight
Cottonseed cake, 20 parts by weight dish leafs, 30 parts by weight melon and fruit peels, 8 parts by weight hop residues add 45 parts by weight water by fermentation are decomposed to obtain.
In the mixture of the sulphur and biomass carbon, sulphur accounts for 55wt%, and the mixture of the sulphur and biomass carbon adds
Enter amount for 300kg/ mus.
Microbial fermentation pond sludge addition is 1000 kg/ mus.
Organic fertilizer addition is 700kg/ mus.
Ploughed depth is 35cm.
Embodiment 4
A kind of beach saline land comprehensive processing method, comprises the following steps：
Step 1：Plowed soils, obtains scarifying soil, the mixture of sulphur and biomass carbon is added in scarifying soil and is mixed, again
Plowed soils, is kept for 30 days；
Step 2：Microbial fermentation pond sludge will be added after step 2 is handled by soil, plowed soils, is kept for 30 days；
Step 3：Apply organic fertilizer, plowed soils.
The biomass carbon is by the rice husk of 100 parts by weight, the potassium shale of 5 parts by weight, the pond sludge of 20 parts by weight, 10
700 degrees Celsius of cracking form the desulfurated plaster of parts by weight under anoxic conditions.
The microbial fermentation pond sludge is the biomass charcoal powder that 30 parts by weight are sprinkled into the pond sludge of 200 parts by weight,
Add after microbial bacterial agent ferments what is obtained.
The dosage of microbial bacterial agent accounts for pond sludge 1wt%, which includes following component：Colloid bacillus cereus
1.5 hundred million cfu/g, 300,000,000 cfu/g of bacillus laterosporus, 0.8 hundred million cfu/g of saccharomycete, 1.5 hundred million cfu/g of Lactococcus lactis, thermophilic fat
0.8 hundred million cfu/g of 1.5 hundred million cfu/g of fat bacillus, 0.8 hundred million cfu/g of Streptomyces jingyangensis and clostridium bifermentans.
The organic fertilizer is by 30 parts by weight soya-bean cakes, 30 parts by weight peanut cakes, 30 parts by weight rapeseed cakes, 30 parts by weight
Cottonseed cake, 40 parts by weight dish leafs, 40 parts by weight melon and fruit peels, 10 parts by weight hop residues add 50 parts by weight water by fermentation are decomposed to obtain
's.
In the mixture of the sulphur and biomass carbon, sulphur accounts for 60wt%, and the mixture of the sulphur and biomass carbon adds
Enter amount for 400kg/ mus.
Microbial fermentation pond sludge addition is 2000 kg/ mus.
Organic fertilizer addition is 1000 kg/ mus.
Ploughed depth is 40cm.
Embodiment 5
A kind of beach saline land comprehensive processing method, comprises the following steps：
Step 1：Plowed soils, obtains scarifying soil, the mixture of sulphur and biomass carbon is added in scarifying soil and is mixed, again
Plowed soils, is kept for 15 days；
Step 2：Microbial fermentation pond sludge will be added after step 2 is handled by soil, plowed soils, is kept for 15 days；
Step 3：Apply organic fertilizer, plowed soils, oyster shell whiting and bone meal are separately added into according still further to 100kg/ mus of standard.
The biomass carbon is by the rice husk of 70 parts by weight, the potassium shale of 3 parts by weight, the pond sludge of 15 parts by weight, 8 weights
650 degrees Celsius of cracking form the desulfurated plaster of amount part under anoxic conditions.
The microbial fermentation pond sludge is the biomass charcoal powder that 20 parts by weight are sprinkled into the pond sludge of 150 parts by weight,
Add after microbial bacterial agent ferments what is obtained.
The dosage of microbial bacterial agent accounts for pond sludge 0.5wt%, which includes following component：Colloid gemma bar
It is 0.9 hundred million cfu/g of bacterium, 200,000,000 cfu/g of bacillus laterosporus, 0.6 hundred million cfu/g of saccharomycete, 0.9 hundred million cfu/g of Lactococcus lactis, thermophilic
0.8 hundred million cfu/g of 0.9 hundred million cfu/g of Bacillus stearothermophilus, 0.5 hundred million cfu/g of Streptomyces jingyangensis and clostridium bifermentans.
The organic fertilizer is by 15 parts by weight soya-bean cakes, 13 parts by weight peanut cakes, 17 parts by weight rapeseed cakes, 15 parts by weight
Cottonseed cake, 29 parts by weight dish leafs, 29 parts by weight melon and fruit peels, 8 parts by weight hop residues add 30 parts by weight water by fermentation are decomposed to obtain.
In the mixture of the sulphur and biomass carbon, sulphur accounts for 50wt%, and the mixture of the sulphur and biomass carbon adds
Enter amount for 250kg/ mus.
Microbial fermentation pond sludge addition is 1500kg/ mus.
Organic fertilizer addition is 500kg/ mus.
Ploughed depth is 30cm.
Result of the test：Certain salt-soda soil uses the modification method of 1-5 of the embodiment of the present invention, and the content of organic matter is by from 9.899g/
Kg increases to 16.852-18.936g/kg, and pH value is reduced to 7.71-7.42 by 8.36, and basicity is reduced to 18.43- by 44.48%
17.54%.
Above-described embodiment is the preferable implementation of the present invention, and in addition, the present invention can be realized with other manner,
Do not depart from and any on the premise of present inventive concept obviously replace within protection scope of the present invention.
Claims (9)
- A kind of 1. beach saline land comprehensive processing method, it is characterised in that：Comprise the following steps：Step 1：Plowed soils, obtains scarifying soil, the mixture of sulphur and biomass carbon is added in scarifying soil and is mixed, again Plowed soils, is kept for 10-30 days；Step 2：Microbial fermentation pond sludge will be added after step 2 is handled by soil, plowed soils, is kept for 10-30 days；Step 3：Apply organic fertilizer, plowed soils.
- A kind of 2. beach saline land comprehensive processing method according to claim 1, it is characterised in that：The biomass carbon is dirty by the pond of the rice husk of 50-100 parts by weight, the potassium shale of 1-5 parts by weight, 10-20 parts by weight Mud, 500-700 degrees Celsius of cracking forms the desulfurated plaster of 5-10 parts by weight under anoxic conditions.
- A kind of 3. beach saline land comprehensive processing method stated according to claim 1, it is characterised in that：The microbial fermentation pool Mud is the biomass charcoal powder that 5-30 parts by weight are sprinkled into the pond sludge of 100-200 parts by weight, adds microbial bacterial agent fermentation Obtain afterwards.
- A kind of 4. beach saline land comprehensive processing method according to claim 3, it is characterised in that：The use of microbial bacterial agent Amount accounts for pond sludge 0.1-1wt%, which includes following component：Hundred million cfu/g of colloid bacillus cereus 0.5-1.5, side spore Hundred million cfu/g of bacillus 1-3, hundred million cfu/g of saccharomycete 0.2-0.8, hundred million cfu/g of Lactococcus lactis 0.5-1.5, stearothermophilus gemma Hundred million cfu/g of bacillus 0.5-1.5, hundred million cfu/g of Streptomyces jingyangensis 0.2-0.8 hundred million cfu/g and clostridium bifermentans 0.2-0.8.
- A kind of 5. beach saline land comprehensive processing method according to claim 1, it is characterised in that：The organic fertilizer is By 10-30 parts by weight soya-bean cake, 10-30 parts by weight peanut cake, 10-30 parts by weight rapeseed cake, 10-30 parts by weight cottonseed cake, 20- 40 parts by weight dish leafs, 20-40 parts by weight melon and fruit peel, 5-10 parts by weight hop residues add 10-50 parts by weight water by fermentation is decomposed to obtain 's.
- A kind of 6. beach saline land comprehensive processing method according to claim 1, it is characterised in that：The sulphur and biology In the mixture of matter charcoal, sulphur accounts for 40-60wt%, and the mixture addition of the sulphur and biomass carbon is 50-400kg/ mus.
- A kind of 7. beach saline land comprehensive processing method according to claim 1, it is characterised in that：Microbial fermentation pond sludge Addition is kg/ mus of 500-2000.
- A kind of 8. beach saline land comprehensive processing method according to claim 1, it is characterised in that：Organic fertilizer addition For kg/ mus of 200-1000.
- A kind of 9. beach saline land comprehensive processing method according to claim 1, it is characterised in that：Ploughed depth is 20- 40cm。
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711228598.XA CN108029270A (en) | 2017-11-29 | 2017-11-29 | A kind of beach saline land comprehensive processing method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711228598.XA CN108029270A (en) | 2017-11-29 | 2017-11-29 | A kind of beach saline land comprehensive processing method |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN108029270A true CN108029270A (en) | 2018-05-15 |
Family
ID=62094332
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201711228598.XA Pending CN108029270A (en) | 2017-11-29 | 2017-11-29 | A kind of beach saline land comprehensive processing method |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN108029270A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109156110A (en) * | 2018-10-10 | 2019-01-08 | 南开大学滨海学院 | A method of saline-alkali soil is improved using cordyceps sinensis fermentation liquor |
| CN109169048A (en) * | 2018-11-12 | 2019-01-11 | 石河子大学 | A kind of salt-soda soil grazing Brassica napus cultural method |
| CN110028358A (en) * | 2019-05-07 | 2019-07-19 | 山东农业大学 | Improved the soil mode based on Controlled Release Fertilizer-plant immune inducer-organic fertilizer advantage compatibility beach saline land control salt drop alkali |
Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104355813A (en) * | 2014-10-29 | 2015-02-18 | 贵州省化工研究院 | Method for producing organic-inorganic compound fertilizer through potassium-bearing shale |
| CN104788209A (en) * | 2015-04-22 | 2015-07-22 | 樊连雪 | Carbon-based bioactive ecological fertilizer and production method thereof |
| CN105367335A (en) * | 2015-11-19 | 2016-03-02 | 中国科学院南京土壤研究所 | Biochar-based coast saline-alkali land improvement conditioner and preparation method and application thereof |
| CN105418316A (en) * | 2015-12-14 | 2016-03-23 | 王桂君 | Biochar fertilizer modifying agent suitable for saline-alkali soil and preparing method and application method thereof |
| CN105837378A (en) * | 2016-04-29 | 2016-08-10 | 惠州市四季绿农产品有限公司 | Rapid conditioning agent for soil pH value |
| CN106171111A (en) * | 2016-07-15 | 2016-12-07 | 山东胜伟园林科技有限公司 | A kind of desulfurated plaster compounding application bacterial manure modification method to salt-soda soil |
| CN106278691A (en) * | 2016-07-15 | 2017-01-04 | 山东胜伟园林科技有限公司 | A kind of formula simultaneously using biomass and desulfurated plaster improvement salt-soda soil and application process |
| CN106635026A (en) * | 2016-12-16 | 2017-05-10 | 中国农业大学 | Biomass charcoal-desulfurization gypsum soil conditioner and preparation method and application thereof |
| CN107347291A (en) * | 2017-07-21 | 2017-11-17 | 浙江德润市政园林有限公司 | A kind of salt affected soil modification method |
-
2017
- 2017-11-29 CN CN201711228598.XA patent/CN108029270A/en active Pending
Patent Citations (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN104355813A (en) * | 2014-10-29 | 2015-02-18 | 贵州省化工研究院 | Method for producing organic-inorganic compound fertilizer through potassium-bearing shale |
| CN104788209A (en) * | 2015-04-22 | 2015-07-22 | 樊连雪 | Carbon-based bioactive ecological fertilizer and production method thereof |
| CN105367335A (en) * | 2015-11-19 | 2016-03-02 | 中国科学院南京土壤研究所 | Biochar-based coast saline-alkali land improvement conditioner and preparation method and application thereof |
| CN105418316A (en) * | 2015-12-14 | 2016-03-23 | 王桂君 | Biochar fertilizer modifying agent suitable for saline-alkali soil and preparing method and application method thereof |
| CN105837378A (en) * | 2016-04-29 | 2016-08-10 | 惠州市四季绿农产品有限公司 | Rapid conditioning agent for soil pH value |
| CN106171111A (en) * | 2016-07-15 | 2016-12-07 | 山东胜伟园林科技有限公司 | A kind of desulfurated plaster compounding application bacterial manure modification method to salt-soda soil |
| CN106278691A (en) * | 2016-07-15 | 2017-01-04 | 山东胜伟园林科技有限公司 | A kind of formula simultaneously using biomass and desulfurated plaster improvement salt-soda soil and application process |
| CN106635026A (en) * | 2016-12-16 | 2017-05-10 | 中国农业大学 | Biomass charcoal-desulfurization gypsum soil conditioner and preparation method and application thereof |
| CN107347291A (en) * | 2017-07-21 | 2017-11-17 | 浙江德润市政园林有限公司 | A kind of salt affected soil modification method |
Non-Patent Citations (1)
| Title |
|---|
| 方海兰等: "《城市土壤生态功能与有机废弃物循环利用》", 31 January 2014, 上海科学技术出版社 * |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109156110A (en) * | 2018-10-10 | 2019-01-08 | 南开大学滨海学院 | A method of saline-alkali soil is improved using cordyceps sinensis fermentation liquor |
| CN109169048A (en) * | 2018-11-12 | 2019-01-11 | 石河子大学 | A kind of salt-soda soil grazing Brassica napus cultural method |
| CN109169048B (en) * | 2018-11-12 | 2021-01-19 | 石河子大学 | Method for cultivating oilseed rape for feeding in saline-alkali soil |
| CN110028358A (en) * | 2019-05-07 | 2019-07-19 | 山东农业大学 | Improved the soil mode based on Controlled Release Fertilizer-plant immune inducer-organic fertilizer advantage compatibility beach saline land control salt drop alkali |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN105237228A (en) | Liquid biological organic fertilizer with high content of organic substances and preparation method | |
| CN105859489A (en) | Special compound fertilizer for saline-alkali soil and production method thereof | |
| CN103143556B (en) | Passivating agent for reducing cadmium activity of acidic vegetable soil and use method thereof | |
| CN107201234A (en) | A kind of inland soda alkaline land modifying agent and application | |
| CN108002907A (en) | A kind of method for improveing continuous cropping soil | |
| CN113861991B (en) | Building residue soil modifier prepared from kitchen waste, preparation method and application of building residue soil modifier | |
| CN108029270A (en) | A kind of beach saline land comprehensive processing method | |
| CN103952355A (en) | Compound microbial phosphate-solubilizing bacterial agent and preparation method thereof | |
| CN107580818A (en) | A kind of soil conditioning and the integrated approach repaired | |
| CN109089709A (en) | A kind of method that apple is efficiently planted in salt-soda soil | |
| CN105964680A (en) | Coastal saline continuous cropping cotton soil ecological restoration agent and preparing method and application thereof | |
| CN111253193B (en) | High-concentration fulvic acid efficient liquid fertilizer and application thereof | |
| CN107955622A (en) | A kind of alkaline land improving organic conditioner and its method for improveing salt-soda soil | |
| CN107087451B (en) | method for improving severe soda saline-alkali soil | |
| CN103435383A (en) | Special microbial fertilizer for seaside solonchak, and preparation method and application of microbial fertilizer | |
| CN107432131B (en) | Saline-alkali soil improvement method | |
| CN109020755A (en) | Active small molecular organic carbon bio-feritlizer and preparation method thereof applied to facility ginseng planting | |
| El-Akhdar et al. | Intergradation of different fertilizers for sustainable agriculture enhanced growth and yield of wheat (Triticum aestivum L.) | |
| CN111777461A (en) | Water-soluble organic fertilizer and preparation method thereof | |
| CN114014721A (en) | Preparation method and application of alkaline soil conditioner based on kitchen waste | |
| Mohaseb et al. | Role of mineral and bio-fertilizers on some soil properties and rice productivity under reclaimed saline soils | |
| Mirza et al. | Rehabilitation of soils through environmental friendly technologies: Role of Sesbania and farmyard manure | |
| Ghanem et al. | Improvement of mung bean growth and productivity in salinity-affected soil after seed inoculation with phosphate-dissolving bacteria. | |
| CN106753418A (en) | Alkaline land modifying agent and saline and alkali land improvement method based on spent bleaching clay | |
| CN102249755A (en) | Farmland ginseng planting soil conditioner |
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 | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20180515 |
|
| RJ01 | Rejection of invention patent application after publication |