CN115643993A - Salt-reducing and fertilizing method for coastal saline soil - Google Patents
Salt-reducing and fertilizing method for coastal saline soil Download PDFInfo
- Publication number
- CN115643993A CN115643993A CN202211406481.7A CN202211406481A CN115643993A CN 115643993 A CN115643993 A CN 115643993A CN 202211406481 A CN202211406481 A CN 202211406481A CN 115643993 A CN115643993 A CN 115643993A
- Authority
- CN
- China
- Prior art keywords
- earthworm
- rice
- saline soil
- coastal saline
- fertilization
- 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
- 239000002689 soil Substances 0.000 title claims abstract description 62
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 title claims abstract description 36
- 239000011780 sodium chloride Substances 0.000 title claims abstract description 36
- 238000000034 method Methods 0.000 title claims abstract description 29
- 241000361919 Metaphire sieboldi Species 0.000 claims abstract description 92
- 241000209094 Oryza Species 0.000 claims abstract description 43
- 235000007164 Oryza sativa Nutrition 0.000 claims abstract description 43
- 235000009566 rice Nutrition 0.000 claims abstract description 43
- 241001233061 earthworms Species 0.000 claims abstract description 42
- 239000010871 livestock manure Substances 0.000 claims abstract description 33
- 210000003608 fece Anatomy 0.000 claims abstract description 29
- 239000010902 straw Substances 0.000 claims abstract description 22
- 150000003839 salts Chemical class 0.000 claims abstract description 18
- 230000004720 fertilization Effects 0.000 claims abstract description 16
- 230000009467 reduction Effects 0.000 claims abstract description 16
- 230000006872 improvement Effects 0.000 claims abstract description 15
- 238000003306 harvesting Methods 0.000 claims abstract description 5
- 238000000354 decomposition reaction Methods 0.000 claims description 6
- 238000000855 fermentation Methods 0.000 claims description 3
- 230000004151 fermentation Effects 0.000 claims description 3
- 230000008901 benefit Effects 0.000 abstract description 21
- 238000009395 breeding Methods 0.000 abstract description 5
- 230000001488 breeding effect Effects 0.000 abstract description 5
- 230000035558 fertility Effects 0.000 abstract description 3
- 239000002699 waste material Substances 0.000 description 10
- 235000001674 Agaricus brunnescens Nutrition 0.000 description 6
- 230000001965 increasing effect Effects 0.000 description 6
- 238000011282 treatment Methods 0.000 description 6
- 235000013311 vegetables Nutrition 0.000 description 6
- 238000012258 culturing Methods 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 238000011065 in-situ storage Methods 0.000 description 5
- 244000144972 livestock Species 0.000 description 5
- 244000144977 poultry Species 0.000 description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- 238000011161 development Methods 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 239000011368 organic material Substances 0.000 description 3
- 238000004181 pedogenesis Methods 0.000 description 3
- 240000006677 Vicia faba Species 0.000 description 2
- 235000010749 Vicia faba Nutrition 0.000 description 2
- 235000002098 Vicia faba var. major Nutrition 0.000 description 2
- 239000002154 agricultural waste Substances 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 235000013305 food Nutrition 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 235000015097 nutrients Nutrition 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 230000004584 weight gain Effects 0.000 description 2
- 235000019786 weight gain Nutrition 0.000 description 2
- 208000003643 Callosities Diseases 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 240000005702 Galium aparine Species 0.000 description 1
- 235000014820 Galium aparine Nutrition 0.000 description 1
- 206010020649 Hyperkeratosis Diseases 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 240000008042 Zea mays Species 0.000 description 1
- 235000005824 Zea mays ssp. parviglumis Nutrition 0.000 description 1
- 235000002017 Zea mays subsp mays Nutrition 0.000 description 1
- CKUAXEQHGKSLHN-UHFFFAOYSA-N [C].[N] Chemical compound [C].[N] CKUAXEQHGKSLHN-UHFFFAOYSA-N 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 230000009471 action Effects 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 235000005822 corn Nutrition 0.000 description 1
- 238000003967 crop rotation Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 230000029087 digestion Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000029142 excretion Effects 0.000 description 1
- 238000009313 farming Methods 0.000 description 1
- 239000012634 fragment Substances 0.000 description 1
- 238000009342 intercropping Methods 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 235000016709 nutrition Nutrition 0.000 description 1
- 230000035764 nutrition Effects 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- 239000003895 organic fertilizer Substances 0.000 description 1
- 239000010815 organic waste Substances 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 230000001681 protective effect Effects 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000005067 remediation Methods 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 230000029058 respiratory gaseous exchange Effects 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000010998 test method Methods 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 235000013619 trace mineral Nutrition 0.000 description 1
- 239000011573 trace mineral Substances 0.000 description 1
Landscapes
- Fertilizers (AREA)
Abstract
The invention relates to a method for salt reduction and fertility improvement of coastal saline soil, which comprises the steps of planting rice in summer, and stacking rice straws and livestock manure as feeds in a harvested rice field to form an earthworm bed for earthworm cultivation after the rice is harvested; harvesting 1/2-2/3 of earthworms in one month before the rice is planted, and turning the rest earthworms, the earthworm bed and the earthworm feces into coastal saline soil for improvement. According to the technical scheme, a set of efficient ecological soil improvement mode is provided according to the rice field planting and earthworm growth and breeding rules and by combining the demand of salt reduction and fertilization of coastal saline soil, and field experiments show that the method has the advantages of high economic and ecological benefits, simplicity and convenience in management, easiness in mastering of technical operation and the like.
Description
Technical Field
The invention relates to the technical field of soil improvement, in particular to a salt-reducing and fertilizing method for coastal saline soil.
Background
The coastal saline soil has the advantages that the effectiveness and the conversion efficiency of soil nutrients are limited due to too high salinity, so that the crop yield is reduced, and therefore, the development of the comprehensive utilization of the coastal saline-alkali soil has important strategic significance for guaranteeing national food safety. The rice planting is generally considered as one of effective methods for improving coastal saline soil, and the salt content of surface soil can be reduced through the leaching action of a water layer on the soil, so that the pH value and the physicochemical property of the saline soil are improved.
Returning rice straws to the field is used as a practical protective farming technology, and is widely applied and popularized in China at present. The crop straw fragments are considered to be one of the best food sources for earthworms, and livestock and poultry manure is added when the straws of the rice field are returned to the field, so that the conversion of organic materials to soil organic carbon can be accelerated by the aid of earthworm treatment. On one hand, earthworms directly contribute to the decomposition of organic materials such as straws and the like through a series of activities such as crushing, digestion, respiration, excretion and the like; on the other hand, earthworms can also change the soil environment by predation, thereby influencing the population dynamics of other indigenous soil organisms and indirectly contributing to the decomposition of organic materials.
The in-situ treatment of the rice field straw earthworms can not only improve the soil fertility, but also obtain a series of earthworm products, namely earthworm bodies and earthworm feces. The earthworm is rich in nutrition, protein, fat and various trace elements, and is a high-quality raw material of various feeds. In recent years, the demand for earthworms is increasing, and the market prospect is huge. The wormcast is a good decomposed organic fertilizer, is also soil with a granular structure, and has a good promotion effect on restoration and improvement of coastal saline soil and growth and development of crops. Therefore, the development of the rice field for breeding the earthworms can obtain remarkable ecological and economic benefits.
Currently, the practice of ectopically culturing earthworms by using organic wastes at home and abroad is more, such as an earthworm culturing method (CN 201310047641.8), indoor three-dimensional assembled earthworm culturing equipment (CN 201410242718.1) and the like, or in-situ earthworm culturing but in an intercropping mode, such as a method for culturing earthworms by crop straws and interplanting corns (CN 201210158112.0) and the like, researches on soil improvement and the like of earthworms are mainly focused on a theoretical level, but the practice of carrying out combination of in-situ treatment of wastes such as straws and the like of earthworms in farmlands and applying the wastes to coastal saline soil remediation is less.
Disclosure of Invention
In view of the above-mentioned shortcomings of the prior art, the present invention aims to provide a method for salt reduction and fertilization of coastal saline soil. The invention establishes a technical mode combining rice planting, earthworm cultivation paddy-upland rotation and in-situ decomposition of livestock manure, straw and other wastes, solves the problems of low soil productivity and poor soil formation structure of coastal saline soil by the investment of decomposed organic matters, earthworms and earthworm manure, can also fully utilize cultivated land resources to cultivate earthworms to increase economic benefits and improve the ecological environment of farmlands, has the advantages of good improvement effect and high economic benefits of coastal saline soil, and is used for solving the problems in the prior art.
The purpose of the invention can be realized by the following technical scheme:
the invention provides a method for salt reduction and fertilization of coastal saline soil, which comprises the steps of planting rice in summer, and after harvesting the rice, stacking rice straws and livestock manure as feed in a harvested rice field to form an earthworm bed for earthworm cultivation; harvesting 1/2-2/3 amount of earthworms one month before the rice is planted, and turning the rest earthworms, the earthworm bed and the earthworm feces into coastal saline soil for improvement.
Preferably, the mass ratio of the livestock manure to the rice straws in the earthworm bed is more than or equal to 1.
More preferably, the livestock manure is cow manure or pig manure after dry-wet separation.
Preferably, the earthworm bed can contain mushroom dregs and vegetable wastes, and the addition amount of the mushroom dregs and the vegetable wastes is not more than 1/2 of the addition amount of the livestock and poultry manure. The length of the added mushroom residue and vegetable waste is below 1 cm.
Preferably, the earthworm seedlings are put on the earthworm bed.
Preferably, when the livestock and poultry manure is pig manure, the earthworm bed is fermented and decomposed before earthworm seedlings are put in. The fermentation and decomposition time of the pig manure is 20-30 days.
Preferably, the earthworm beds are stacked into a ridge shape with a trapezoidal cross section, and the bevel edge is sawtooth-shaped.
Preferably, the height of the earthworm bed is 0.2 m-0.5 m.
Preferably, the upper bottom edge of the trapezoid in the earthworm bed is 1 m-1.2 m.
Preferably, the lower bottom edge of the trapezoid in the earthworm bed is 2 m-2.5 m.
Preferably, the length of the earthworm bed is 60-80 m.
More preferably, drainage ditches are arranged on two sides of the earthworm bed, and the width of each drainage ditch is 20cm-30cm. Preferably, a pedestrian passageway is arranged between the two ridges of earthworm beds. Preferably, the width of the walkway is 1.5m-2m.
More preferably, the earthworm bed is covered with a film. To increase the temperature.
Preferably, a shed frame is built on the earthworm bed and is covered by a sunshade net.
Preferably, 25kg-100kg of earthworm seedlings are put into each earthworm bed.
Preferably, the humidity of the earthworm bed is 55-65%, and the temperature is not lower than 10 ℃.
More preferably, when the height of the earthworm bed is reduced by 1/5, fresh feed of 5cm-10cm is added.
Preferably, earthworms are harvested in the earthworm bed in an amount of about 1/2-2/3 of the amount of the earthworms in one month before the rice is planted, and the remaining earthworms are reserved for nutrient activation and soil physical structure improvement of soil.
Preferably, when the earthworms are harvested, the rest earthworms, the earthworm bed and the earthworm cast are turned into coastal saline soil for fertilization and improvement.
According to the method for salt reduction and fertilization of the coastal saline soil, the problems of low soil productivity and poor soil formation structure of the coastal saline soil are solved through the investment of decomposed organic matters, earthworms and earthworm excrement, the economic benefit can be increased by fully utilizing farmland resources to breed the earthworms, the ecological environment of a farmland is improved, and field tests show that the method has the advantages of good improvement effect and high economic benefit of the coastal saline soil, simplicity and convenience in management, easiness in mastering of technical operation and the like.
Specifically, compared with the prior art, the beneficial effects of the invention are embodied in the following aspects:
(1) The management is convenient: the earthworm bed is simple and convenient to set, only rice straws, livestock and poultry manure, mushroom residues, vegetable wastes and the like are needed to be built into a ridge, earthworm seedlings are placed on the ridge, the remaining earthworms, the earthworm bed and the earthworm manure are turned into farmland soil one month before rice planting, and the technical operation is easy to master.
(2) The earthworm bed has reasonable design: the earthworm bed is characterized by ridge shape and drainage ditches arranged at two sides. The water accumulation on the ridge surface can be prevented during rainfall, and the earthworms are prevented from being flooded by water; the earthworm bed is covered with a film to increase the temperature, a shed frame is built and covered by a sunshade net, so that the temperature of the earthworm growth environment is prevented from being too high or too low, and the production efficiency is improved.
(3) The economic benefit is good: the net profit of earthworm cultivation in each mu of rice field can reach 3000-4000 yuan.
(4) The ecological benefit is good: because the earthworms are cultivated in the rice field, the residual agricultural wastes and the earthworm casts are turned into the rice field, and the salt reduction and fertilization are added through the organic decomposed substances and the earthworm casts, so that the salt content of the soil can be reduced, the soil is loosened, the soil fertility is increased, and the ecological benefit of soil improvement is better.
Detailed Description
Before the present embodiments are further described, it is to be understood that the scope of the invention is not to be limited to the specific embodiments described below; it is also to be understood that the terminology used in the examples herein is for the purpose of describing particular embodiments only, and is not intended to limit the scope of the present invention. Test methods in which specific conditions are not specified in the following examples are generally carried out under conventional conditions or under conditions recommended by the respective manufacturers.
When numerical ranges are given in the examples, it is understood that both endpoints of each of the numerical ranges and any value therebetween can be selected unless the invention otherwise indicated. Unless defined otherwise, all technical and scientific terms used herein have the same meaning as commonly understood by one of ordinary skill in the art to which this invention belongs. In addition to the specific methods, devices, and materials used in the examples, any methods, devices, and materials similar or equivalent to those described in the examples may be used in the practice of the invention in addition to the specific methods, devices, and materials used in the examples, in keeping with the knowledge of one skilled in the art and with the description of the invention.
The present invention will be described in detail with reference to specific examples.
Example 1
After the rice is harvested, an earthworm bed consisting of rice straws and livestock and poultry manure (mushroom dregs and vegetable wastes) is stacked in the rice field for fermentation to breed earthworms, the earthworm bed comprises the components of the rice straws and the pig manure, and a proper amount of mushroom dregs and vegetable wastes can be selectively stacked on the earthworm bed. The earthworms are stacked in a trapezoidal shape, the stacking height is 0.4m, the width of the upper opening of the wide edge is 1.2m, the width of the lower opening of the wide edge is 2.5m, and the length of the long edge of the wide edge is 80m. Drainage ditches are arranged on two sides of the water tank, and the width of each drainage ditch is 30cm. The width of the pedestrian passageway between two ridges is 1.5m. And (3) building an earthworm bed after harvesting the rice, fermenting and decomposing for 25d, and then breeding the earthworms. The earthworm beds are all covered by a film to increase the temperature, and a shed frame is built on the earthworm beds and covered by a sunshade net to increase the temperature in winter and keep out of the sun in summer. When seedlings are thrown, 75kg of earthworm seedlings are thrown in each earthworm bed. In the breeding process, the humidity of the earthworm bed is kept between 55 percent and 65 percent, and the temperature is not lower than 10 ℃. In the breeding process, after the earthworm bed is obviously reduced, fresh feed with the thickness of 5cm-10cm is added. The earthworms with the amount of 1/2 are harvested by adopting an optical drive method before the rice is planted, and the rest earthworms, the earthworm bed and the earthworm feces are turned into a rice field.
Different proportions of the straws and the pig manure of the earthworm bed are set, and the influence of the proportions on the growth of the earthworms is analyzed. The growth of earthworms is greatly influenced by the carbon-nitrogen ratio of the feed. As can be seen from table 1, the straw/pig manure ratios are 40, 30, 20, 80 and 50, and the maximum weight gain of earthworms can reach 9.2, 8.8, 8.6 and 8.3. When the ratio of the straws is less than 20% or more than 50%, the weight of the earthworms is obviously reduced. Especially, the weight gain is reduced to be below 4 after the straw ratio exceeds 50 percent. Therefore, when the straw proportion is 20-50% and the pig manure proportion is 50-80%, the weight increasing effect of the earthworms is optimal.
TABLE 1 influence of different earthworm bed straw/pig manure ratios on earthworm growth
Note: different letters after the same column of data indicate significant differences between treatments (P < 0.05)
Compared with the rice-earthworm mode and the rice green manure (broad bean) rotation mode, the rice-earthworm mode disclosed by the invention has the advantages that the influence on the physicochemical properties of the coastal saline soil is compared (table 2), the rice-earthworm mode obviously improves soil organic matters, quick-acting phosphorus and quick-acting potassium, is respectively 16.7%, 10.9% and 13.0% higher than the rice green manure mode, the pH value and the soil EC are also obviously reduced, the pH value and the soil EC are respectively reduced by 0.34 unit and 13.3%, and the ecological benefit is obvious.
TABLE 2 influence of different technical modes on the physicochemical properties of the soil
Note: different letters after the same column of data indicate significant differences between treatments (P < 0.05)
Comparing the economic benefits of the rice-earthworm mode and the rice green manure mode (table 3), although the total expenditure of the rice-earthworm mode is respectively 423.36% higher, the total expenditure of the rice-earthworm mode is also 315.93% higher in net income. On the one hand, the net gain is mainly due to the production of earthworms, which greatly increases the economic benefit. On the other hand, in the rice earthworm mode, earthworms, earthworm cast and completely fermented agricultural wastes are returned to the field, so that the soil is fertilized, the coastal saline soil is improved, the yield of rice is increased to a certain extent, and the income is increased.
TABLE 3 economic benefits for different models
Crop rotation mode | Total expenditure (Yuan/mu) | Net income (Yuan/mu) |
Rice-green manure (broad bean) | 1070b | 1130b |
Rice-earthworm | 5600a | 4700a |
Note: the patch comprises 330 yuan/mu of green manure planting; different letters after the same column of data indicate significant differences between treatments (P < 0.05)
In conclusion, the method for salt reduction and fertilization of the coastal saline soil provided by the invention establishes a technical mode combining rice planting, earthworm cultivation, paddy-upland rotation and in-situ decomposition of wastes such as livestock manure, straw and the like, not only solves the problems of low coastal saline soil productivity and poor soil formation structure through the investment of decomposed organic matters, earthworms and earthworm manure, but also can fully utilize cultivated land resources to cultivate earthworms to increase economic benefits and improve ecological environment of farmlands, has the advantages of good coastal saline soil improvement effect and high economic benefits, and is used for solving the problems in the prior art. Therefore, the invention effectively overcomes various defects in the prior art and has high industrial utilization value.
The embodiments described above are described to facilitate an understanding and use of the invention by those skilled in the art. It will be readily apparent to those skilled in the art that various modifications to these embodiments may be made, and the generic principles described herein may be applied to other embodiments without the use of the inventive faculty. Therefore, the present invention is not limited to the above embodiments, and those skilled in the art should make improvements and modifications within the scope of the present invention based on the disclosure of the present invention.
Claims (10)
1. A method for salt reduction and fertilization of coastal saline soil is characterized in that rice is planted in summer, and after the rice is harvested, rice straws and livestock manure are used as feed and stacked in a harvested rice field to form an earthworm bed for earthworm cultivation; harvesting 1/2-2/3 amount of earthworms one month before the rice is planted, and turning the rest earthworms, the earthworm bed and the earthworm feces into coastal saline soil for improvement.
2. The method for salt reduction and fertilization of the coastal saline soil as claimed in claim 1, wherein the mass ratio of the livestock manure to the rice straw in the earthworm bed is greater than or equal to 1.
3. The method for salt reduction and fertilization by utilizing coastal saline soil as claimed in claim 1, wherein when the livestock manure is pig manure, the earthworm bed is fermented and decomposed before earthworm seedlings are put in, and the fermentation and decomposition time of the pig manure is 20-30 days.
4. The method for salt reduction and fertilization of the coastal saline soil as claimed in claim 1, wherein the earthworm beds are stacked in a ridge shape with a trapezoidal cross section and a sawtooth-shaped bevel edge.
5. The method for salt reduction and fertilization of the coastal saline soil as claimed in claim 4, wherein the height of the earthworm bed is 0.2-0.5 m, the upper bottom edge of the trapezoid in the earthworm bed is 1-1.2 m, the lower bottom edge of the trapezoid in the earthworm bed is 2-2.5 m, and the ridge length of the earthworm bed is 60-80 m.
6. The method for salt reduction and fertilization of the coastal saline soil as claimed in claim 5, wherein 25kg-100kg of earthworm seedlings are put in each earthworm bed.
7. The method for salt reduction and fertilization of the coastal saline soil as claimed in claim 1, wherein drainage ditches are arranged on two sides of the earthworm bed, and the width of each drainage ditch is 20cm-30cm;
a pedestrian passage is arranged between the two earthworm beds, and the width of the pedestrian passage is 1.5m-2m.
8. The method for salt-reducing and fertilizing the coastal saline soil as claimed in claim 1, wherein the earthworm bed is covered with a film;
a shed frame is built on the earthworm bed and is covered by a sunshade net.
9. The method for salt reduction and fertilization of coastal saline soil as claimed in claim 1, wherein the moisture of the earthworm bed is 55% -65%, and the temperature is not lower than 10 ℃.
10. The method for salt reduction and fertilization of the coastal saline soil as claimed in claim 1, wherein fresh feed of 5-10 cm is added when the height of the earthworm bed is reduced by 1/5.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211406481.7A CN115643993A (en) | 2022-11-10 | 2022-11-10 | Salt-reducing and fertilizing method for coastal saline soil |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202211406481.7A CN115643993A (en) | 2022-11-10 | 2022-11-10 | Salt-reducing and fertilizing method for coastal saline soil |
Publications (1)
Publication Number | Publication Date |
---|---|
CN115643993A true CN115643993A (en) | 2023-01-31 |
Family
ID=85021546
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202211406481.7A Pending CN115643993A (en) | 2022-11-10 | 2022-11-10 | Salt-reducing and fertilizing method for coastal saline soil |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN115643993A (en) |
Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20120234244A1 (en) * | 2010-12-23 | 2012-09-20 | Miguel Jardine | System and method for continuous vermiculture cycle |
CN104335731A (en) * | 2013-08-06 | 2015-02-11 | 天津贾立明蚯蚓养殖有限公司 | Method for improving saline-alkali land by earthworms |
KR20160086595A (en) * | 2015-01-12 | 2016-07-20 | 김재인 | Rice cultivation complex soil implovent methods using of earth worm as faundmental resources |
EP3105198A1 (en) * | 2014-02-10 | 2016-12-21 | Biofil Mikrobiológiai, Géntechnológiai És Biokémiai KFT. | Soil bacteria for inoculating stress soils |
CN106900197A (en) * | 2017-03-01 | 2017-06-30 | 天津海林生态建设股份公司 | A kind of sustainable synthesis improvement method of marine solonchak ecological circulation |
CN107912097A (en) * | 2017-10-20 | 2018-04-17 | 宁夏三度生态农业科技有限公司 | A kind of saline-alkali soil improvement method |
CN108834463A (en) * | 2018-07-06 | 2018-11-20 | 水利部交通运输部国家能源局南京水利科学研究院 | A kind of coastal saline soil administering method significantly reducing crop Salt Strees Condition |
CN108999157A (en) * | 2018-07-05 | 2018-12-14 | 水利部交通运输部国家能源局南京水利科学研究院 | A kind of processing method significantly improving coastal saline soil physical property |
CN110122428A (en) * | 2019-06-13 | 2019-08-16 | 上海市农业科学院 | A kind of crop rotation cultural method |
-
2022
- 2022-11-10 CN CN202211406481.7A patent/CN115643993A/en active Pending
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20120234244A1 (en) * | 2010-12-23 | 2012-09-20 | Miguel Jardine | System and method for continuous vermiculture cycle |
CN104335731A (en) * | 2013-08-06 | 2015-02-11 | 天津贾立明蚯蚓养殖有限公司 | Method for improving saline-alkali land by earthworms |
EP3105198A1 (en) * | 2014-02-10 | 2016-12-21 | Biofil Mikrobiológiai, Géntechnológiai És Biokémiai KFT. | Soil bacteria for inoculating stress soils |
KR20160086595A (en) * | 2015-01-12 | 2016-07-20 | 김재인 | Rice cultivation complex soil implovent methods using of earth worm as faundmental resources |
CN106900197A (en) * | 2017-03-01 | 2017-06-30 | 天津海林生态建设股份公司 | A kind of sustainable synthesis improvement method of marine solonchak ecological circulation |
CN107912097A (en) * | 2017-10-20 | 2018-04-17 | 宁夏三度生态农业科技有限公司 | A kind of saline-alkali soil improvement method |
CN108999157A (en) * | 2018-07-05 | 2018-12-14 | 水利部交通运输部国家能源局南京水利科学研究院 | A kind of processing method significantly improving coastal saline soil physical property |
CN108834463A (en) * | 2018-07-06 | 2018-11-20 | 水利部交通运输部国家能源局南京水利科学研究院 | A kind of coastal saline soil administering method significantly reducing crop Salt Strees Condition |
CN110122428A (en) * | 2019-06-13 | 2019-08-16 | 上海市农业科学院 | A kind of crop rotation cultural method |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN104987269A (en) | Biological organic fertilizer special for apples and preparation method thereof | |
CN103238447A (en) | High-quality high-efficiency high-yield blueberry cultivation method | |
CN110122023B (en) | Method for biotransformation of cow breeding manure waste liquid by combining earthworm and edible fungus residue and compounding synergistic fertilizer | |
CN107162739A (en) | The production method of earthworm excrement base biological organic fertilizer | |
CN110024642B (en) | Method for planting selenium-rich rice by utilizing plant source humic acid organic fertilizer | |
CN111296367B (en) | Industrial earthworm cultivation method in facility greenhouse | |
CN110073758A (en) | The method for butchering the mushy stage biological organic fertilizer improvement salt-soda soil with breeding waste sewage and the production of dead livestock and poultry straw biogas residue biogas slurry | |
CN106433676A (en) | Soil conditioner and application thereof in organic agriculture fertilizing for newly cultivated coastal beach saline-alkali soil | |
CN107801574A (en) | The implantation methods of slender bamboo shoot | |
CN108651180B (en) | Ecological cultivation technology for promoting fast growth of newly-built bamboo forest | |
CN108738442B (en) | Tea-oil camellia forest soil curing system and manufacturing method thereof | |
CN108990702B (en) | Facility cultivation method for crop rotation of stropharia rugoso-annulata and cowpea | |
CN113039989A (en) | Intelligent ecological planting method for changing selenium-rich orchard into soil and controlling grass in hilly and mountainous areas | |
CN108191504B (en) | Preparation method and use method of special fertilizer for konjak | |
CN110615700A (en) | Degraded soil 'ecological simulation' soil cultivation and restoration method | |
CN107926481B (en) | Pure straw cultivation method for straw mushrooms | |
CN110583415A (en) | Method for ecologically regulating and controlling tobacco continuous cropping obstacles by interplanting coprinus comatus in tobacco field | |
CN105777426B (en) | A kind of ecological type soil modifying agent for gardens | |
CN108002901A (en) | Stropharia rugoso-annulata plantation base-material and preparation method thereof | |
CN115643993A (en) | Salt-reducing and fertilizing method for coastal saline soil | |
CN113943182A (en) | Turning and throwing strip stacking and composting process | |
CN108967366B (en) | Method for preparing wormcast neutral fertilizer | |
CN113647317A (en) | Comprehensive fruit and vegetable planting method based on soilless culture | |
CN113557814A (en) | Cultivation method for returning straw to field | |
CN108668837B (en) | Flower nutrient soil and preparation method thereof |
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 |