CN110199606A - A kind of combined type stony desertification ecological restoring method - Google Patents
A kind of combined type stony desertification ecological restoring method Download PDFInfo
- Publication number
- CN110199606A CN110199606A CN201910633466.8A CN201910633466A CN110199606A CN 110199606 A CN110199606 A CN 110199606A CN 201910633466 A CN201910633466 A CN 201910633466A CN 110199606 A CN110199606 A CN 110199606A
- Authority
- CN
- China
- Prior art keywords
- soil
- desertification
- compost
- excess sludge
- combined type
- 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
- C05D9/00—Other inorganic fertilisers
-
- 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
- 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
-
- 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
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Soil Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Biotechnology (AREA)
- Health & Medical Sciences (AREA)
- Inorganic Chemistry (AREA)
- Biochemistry (AREA)
- Pest Control & Pesticides (AREA)
- General Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Mechanical Engineering (AREA)
- Environmental Sciences (AREA)
- Fertilizers (AREA)
- Cultivation Of Plants (AREA)
Abstract
The invention discloses a kind of combined type stony desertification ecological restoring methods, include the following steps: S1, determine stony desertification place and Rock Desertification Degree, adaptation to local conditions, specify the elements such as the existing place gradient, local climate, local vegetation, unified planning designs planting groove, gutter, and soil is carried out parametrization transforming slope into terrace;S2, using organic castoff composts such as sewage treatment excess sludge, gardens pruning wastes, enable to pollute waste recycling and recycle;S3, according to different plants, according to different proportional arrangements, the good fertilizer of heap and original soil for losing fertility effect are carried out mixed processing in proportion, reach the desired effects of restoration of soil fertility;The present invention carries out compost using sewage treatment excess sludge in Rocky Desertification Control and uses zeolite powder in Rocky Desertification Control composting process, improves the passivation effect and composting efficiency of heavy metal, improves vegetation survival rate.
Description
Technical field
The invention belongs to stony desertification ecological restoration technical fields, more specifically more particularly to a kind of combined type stony desertification
Ecological restoring method.
Background technique
Such as application No. is the Chinese patents of CN102656973B, and it discloses a kind of Rocky Desertification Control and its ecosystem are extensive
Skill is established in multiple method, including Rocky Desertification Region conservation technology, surface vegetation restoration methods and the artificial succession of rock vegetation
Art, the first conservation technology of progress Rocky Desertification Control to prevent erosion and increase soil moisture self-restraint, then carry out ground
Table revegetation and ecosystem restoration is carried out using the artificial succession establishing techniques of rock vegetation, eventually forms Rocky Desertification Control
Artificial bio-membrane's Community Ecology system rebuilds Rocky Desertification Region ecological environment.Its stony desertification soil is not added with the sludge after compost, stone
The nutritional ingredient that desertization soil can be utilized by vegetation is not high, and vegetation survival rate is low, is unable to satisfy vegetation production needs.
Summary of the invention
The purpose of the present invention is to solve disadvantages existing in the prior art, and a kind of combined type stony desert metaplasia proposed
State restorative procedure.
To achieve the above object, the invention provides the following technical scheme:
A kind of combined type stony desertification ecological restoring method, includes the following steps:
S1, determine that stony desertification place and Rock Desertification Degree, adaptation to local conditions specify the existing place gradient, local climate, local vegetation
Etc. elements, unified planning design planting groove, gutter, soil is subjected to parametrization transforming slope into terrace;
S2, using organic castoff composts such as sewage treatment excess sludge, gardens pruning wastes, enable to pollute waste and provide
Sourceization recycles;
S3, according to different plants, according to different proportional arrangements, the good fertilizer of heap and original soil for losing fertility effect into
Row carries out mixed processing in proportion, reaches the desired effects of restoration of soil fertility;
S4, the soil of recovery fertility is inserted in planting groove, and selection is suitble to local growth and conducive to improvement soil property with one
Determine economic value vegetation plantation, enable the plot more preferably, restore the ecological value and economic value faster;
S5, properly maintenance, until soil fertility is thoroughly restored, Rocky Desertification disappears.
Preferably, the parametrization transforming slope into terrace in the step S1 refers to there is gradient plot in ecosystem desertification,
According to the factor designs staged slope protection such as area, flow direction for being washed landform, effectively make original ecosystem destroyed and
It is not easy to be retained, the gradient plot of fertilizer conservation, is converted to the advantageous soil layer conducive to retain water and nutrients antiscour.
It preferably, can be according to gross mass, the component content of waste etc. of compost during compost in the step S2
Element, adjustment mixes a certain number of zeolite powders, to improve the passivation effect and composting efficiency of heavy metal, zeolite powder rough surface
With the porous structure having, zeolite powder is acidproof, and bulk density is 1.2-1.4kg/ liter, without grease and crude fibre again without electrostatic phenomenon,
Stronger carrying capability is made it have, heavy metal can be made equably to be adsorbed on its surface, while can be appropriately extended micro in compost
The release time of composition is more advantageous to plant absorption, and compost is mixed with zeolite powder according to mass ratio 10-20:1-2, turns within every 7-9 days
Heap is primary, and fermentation discharges after 30-45 days.
Preferably, excess sludge progress compost needs to carry out engineering processing in the step S2, the specific steps are that:
A, PADS is put into excess sludge, is uniformly mixed, and continues to put into smashed sticky loess and modified attapulgite, ammonia
Nitrogen clears up bacteria preparation and mud decrement bacteria preparation and sawdust, stirs evenly, mixing speed 150-200rpm is then allowed to stand 3-
4 days, so that microbiologic population is carried out oxygenolysis to the gas chromatography in excess sludge in wet condition and be converted into class corruption
Grow matter;
B, compost treatment is carried out using static forced ventilation mode, mud mixture reaches decomposed after 28-32 days, obtains dirt
Mud composting production, by the excess sludge quality of compost is loose, cation exchange capacity (CEC) dramatically increases, bulk density is reduced, can be by plant
The nutritional ingredient utilized increases, pathogen and parasitic ovum almost all are killed.
Compared with prior art, the beneficial effects of the present invention are: a kind of combined type stony desertification ecology provided by the invention is repaired
Compound method, compared with traditional technology, this method is fairly simple, carries out heap using sewage treatment excess sludge in Rocky Desertification Control
Fertilizer and in Rocky Desertification Control composting process use zeolite powder, loose, the cationic exchange by the excess sludge quality of compost
Amount dramatically increases, bulk density is reduced, pathogen and parasitic ovum almost all are killed, and can be increased by the nutritional ingredient that plant utilizes
Add, improves vegetation survival rate;Zeolite powder rough surface and the porous structure having, zeolite powder is acidproof, bulk density 1.2-1.4kg/
It rises, without grease and crude fibre again without electrostatic phenomenon, makes it have stronger carrying capability, heavy metal can be made equably to be adsorbed on
Its surface, while the release time of microcomponent in compost can be appropriately extended, it is more advantageous to plant absorption, the addition of zeolite powder mentions
The passivation effect and composting efficiency of high heavy metal.
Specific embodiment
In order to make the objectives, technical solutions, and advantages of the present invention clearer, below in conjunction with specific embodiment, to this
Invention is further elaborated.It should be appreciated that the specific embodiments described herein are merely illustrative of the present invention, not
For limiting the present invention.Based on the embodiments of the present invention, those of ordinary skill in the art are not before making creative work
Every other embodiment obtained is put, shall fall within the protection scope of the present invention.
A kind of combined type stony desertification ecological restoring method, includes the following steps:
S1, determine that stony desertification place and Rock Desertification Degree, adaptation to local conditions specify the existing place gradient, local climate, local vegetation
Etc. elements, unified planning design planting groove, gutter, soil is subjected to parametrization transforming slope into terrace;
S2, using organic castoff composts such as sewage treatment excess sludge, gardens pruning wastes, enable to pollute waste and provide
Sourceization recycles;
S3, according to different plants, according to different proportional arrangements, the good fertilizer of heap and original soil for losing fertility effect into
Row carries out mixed processing in proportion, reaches the desired effects of restoration of soil fertility;
S4, the soil of recovery fertility is inserted in planting groove, and selection is suitble to local growth and conducive to improvement soil property with one
Determine economic value vegetation plantation, enable the plot more preferably, restore the ecological value and economic value faster;
S5, properly maintenance, until soil fertility is thoroughly restored, Rocky Desertification disappears.
Specifically, the parametrization transforming slope into terrace in the step S1 refers to there is gradient plot in ecosystem desertification,
According to the factor designs staged slope protection such as area, flow direction for being washed landform, effectively make original ecosystem destroyed and
It is not easy to be retained, the gradient plot of fertilizer conservation, is converted to the advantageous soil layer conducive to retain water and nutrients antiscour.
Specifically, can be according to gross mass, the component content of waste etc. of compost during compost in the step S2
Element, adjustment mixes a certain number of zeolite powders, to improve the passivation effect and composting efficiency of heavy metal, zeolite powder rough surface
With the porous structure having, zeolite powder is acidproof, and bulk density is 1.2-1.4kg/ liter, without grease and crude fibre again without electrostatic phenomenon,
Stronger carrying capability is made it have, heavy metal can be made equably to be adsorbed on its surface, while can be appropriately extended micro in compost
The release time of composition is more advantageous to plant absorption, and compost is mixed with zeolite powder according to mass ratio 10-20:1-2, turns within every 7-9 days
Heap is primary, and fermentation discharges after 30-45 days.
Specifically, excess sludge progress compost needs to carry out engineering processing in the step S2, the specific steps are that:
A, PADS is put into excess sludge, is uniformly mixed, and continues to put into smashed sticky loess and modified attapulgite, ammonia
Nitrogen clears up bacteria preparation and mud decrement bacteria preparation and sawdust, stirs evenly, mixing speed 150-200rpm is then allowed to stand 3-
4 days, so that microbiologic population is carried out oxygenolysis to the gas chromatography in excess sludge in wet condition and be converted into class corruption
Grow matter;
Modified attapulgite is natural bed chain mineral material, and chemical property is stablized, nontoxic, cheap, and gap
Rate is high, large specific surface area, has good absorption property, can preferably adsorb heavy metal substance in plant excess sludge.
B, compost treatment is carried out using static forced ventilation mode, mud mixture reaches decomposed after 28-32 days, obtains
To sludge composting product, by the excess sludge quality of compost is loose, cation exchange capacity (CEC) dramatically increases, bulk density is reduced, can quilt
The nutritional ingredient that plant utilizes increases, pathogen and parasitic ovum almost all are killed.
In summary: a kind of combined type stony desertification ecological restoring method provided by the invention, compared with traditional technology, the party
Method is fairly simple, using sewage treatment excess sludge progress compost and in Rocky Desertification Control composting process in Rocky Desertification Control
It is middle to use zeolite powder, by the excess sludge quality of compost is loose, cation exchange capacity (CEC) dramatically increases, bulk density is reduced, can be planted
The nutritional ingredient that object utilizes increases, and improves vegetation survival rate, pathogen and parasitic ovum almost all and is killed;Zeolite powder surface
Porous structure that is coarse and having, zeolite powder is acidproof, and bulk density is 1.2-1.4kg/ liter, again existing without electrostatic without grease and crude fibre
As making it have stronger carrying capability, heavy metal can be made equably to be adsorbed on its surface, while can be appropriately extended micro- in compost
The release time for measuring composition, it is more advantageous to plant absorption, the addition of zeolite powder improves the passivation effect and composting efficiency of heavy metal.
Finally, it should be noted that the foregoing is only a preferred embodiment of the present invention, it is not intended to restrict the invention,
Although the present invention is described in detail referring to the foregoing embodiments, for those skilled in the art, still may be used
To modify the technical solutions described in the foregoing embodiments or equivalent replacement of some of the technical features,
All within the spirits and principles of the present invention, any modification, equivalent replacement, improvement and so on should be included in of the invention
Within protection scope.
Claims (4)
1. a kind of combined type stony desertification ecological restoring method, characterized by the following steps:
S1, determine that stony desertification place and Rock Desertification Degree, adaptation to local conditions specify the existing place gradient, local climate, local vegetation
Etc. elements, unified planning design planting groove, gutter, soil is subjected to parametrization transforming slope into terrace;
S2, using organic castoff composts such as sewage treatment excess sludge, gardens pruning wastes, enable to pollute waste and provide
Sourceization recycles;
S3, according to different plants, according to different proportional arrangements, the good fertilizer of heap and original soil for losing fertility effect into
Row carries out mixed processing in proportion, reaches the desired effects of restoration of soil fertility;
S4, the soil of recovery fertility is inserted in planting groove, and selection is suitble to local growth and conducive to improvement soil property with one
Determine economic value vegetation plantation, enable the plot more preferably, restore the ecological value and economic value faster;
S5, properly maintenance, until soil fertility is thoroughly restored, Rocky Desertification disappears.
2. a kind of combined type stony desertification ecological restoring method described in claim 1, it is characterised in that: the ginseng in the step S1
Numberization transforming slope into terrace, which refers to, has gradient plot in ecosystem desertification, according to factors such as area, the flow directions for being washed landform
Staged slope protection is designed, has effectively destroyed original ecosystem and is not easy to be retained, the gradient plot of fertilizer conservation, be converted to benefit
In the advantageous soil layer of retain water and nutrients antiscour.
3. a kind of combined type stony desertification ecological restoring method described in claim 1, it is characterised in that: compost in the step S2
During can mix a certain number of zeolite powders according to elements, the adjustment such as component content of the gross mass of compost, waste, with
The passivation effect and composting efficiency of heavy metal, zeolite powder rough surface and the porous structure having are improved, zeolite powder is acidproof, bulk density
Stronger carrying capability is made it have, heavy metal can be made without grease and crude fibre again without electrostatic phenomenon for 1.2-1.4kg/ liter
It is equably adsorbed on its surface, while the release time of microcomponent in compost can be appropriately extended, is more advantageous to plant absorption, heap
Fertilizer is mixed with zeolite powder according to mass ratio 10-20:1-2, and every turning in 7-9 days is primary, and fermentation discharges after 30-45 days.
4. a kind of combined type stony desertification ecological restoring method described in claim 1, it is characterised in that: remaining in the step S2
Sludge carries out compost and needs to carry out engineering processing, the specific steps are that:
A, PADS is put into excess sludge, is uniformly mixed, and continues to put into smashed sticky loess and modified attapulgite, ammonia
Nitrogen clears up bacteria preparation and mud decrement bacteria preparation and sawdust, stirs evenly, mixing speed 150-200rpm is then allowed to stand 3-
4 days, so that microbiologic population is carried out oxygenolysis to the gas chromatography in excess sludge in wet condition and be converted into class corruption
Grow matter;
B, compost treatment is carried out using static forced ventilation mode, mud mixture reaches decomposed after 28-32 days, obtains dirt
Mud composting production, by the excess sludge quality of compost is loose, cation exchange capacity (CEC) dramatically increases, bulk density is reduced, can be by plant
The nutritional ingredient utilized increases, pathogen and parasitic ovum almost all are killed.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910633466.8A CN110199606A (en) | 2019-07-15 | 2019-07-15 | A kind of combined type stony desertification ecological restoring method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910633466.8A CN110199606A (en) | 2019-07-15 | 2019-07-15 | A kind of combined type stony desertification ecological restoring method |
Publications (1)
Publication Number | Publication Date |
---|---|
CN110199606A true CN110199606A (en) | 2019-09-06 |
Family
ID=67797543
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201910633466.8A Pending CN110199606A (en) | 2019-07-15 | 2019-07-15 | A kind of combined type stony desertification ecological restoring method |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN110199606A (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN115463956A (en) * | 2022-06-24 | 2022-12-13 | 沸高生物科技有限公司 | Method for reducing heavy metal pollution of tobacco |
Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
AU2002221382A1 (en) * | 2000-12-05 | 2002-06-18 | Chui-Wen Chiu | Forestation and environment protecting method and system |
CN102656973A (en) * | 2012-05-15 | 2012-09-12 | 广西大学 | Method for controlling stony desertification and restoring ecosystem of stony desertification region |
CN105439379A (en) * | 2015-12-08 | 2016-03-30 | 浙江华庆元生物科技有限公司 | Domestic sewage treatment process |
CN105646064A (en) * | 2015-12-24 | 2016-06-08 | 北京林业大学 | Engineering method for producing biochar soil from dredging sediment |
CN106747779A (en) * | 2016-12-01 | 2017-05-31 | 宁波大学 | A kind of sludge compost improvement method |
CN107828419A (en) * | 2017-09-26 | 2018-03-23 | 湖南湘讯企业管理有限公司 | A kind of ecological restoration materials and its preparation method and application |
CN107892922A (en) * | 2017-11-29 | 2018-04-10 | 江苏源洁节能环保有限公司 | Soil conditioner and application thereof |
CN108373377A (en) * | 2018-02-13 | 2018-08-07 | 太原理工大学 | A kind of method of the Composting treatment of sludge from wastewater treatment plant |
CN109964766A (en) * | 2019-04-24 | 2019-07-05 | 鄂尔多斯市环保投资有限公司 | A kind of method of desert site preparation and rice cultivation |
-
2019
- 2019-07-15 CN CN201910633466.8A patent/CN110199606A/en active Pending
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
AU2002221382A1 (en) * | 2000-12-05 | 2002-06-18 | Chui-Wen Chiu | Forestation and environment protecting method and system |
CN102656973A (en) * | 2012-05-15 | 2012-09-12 | 广西大学 | Method for controlling stony desertification and restoring ecosystem of stony desertification region |
CN105439379A (en) * | 2015-12-08 | 2016-03-30 | 浙江华庆元生物科技有限公司 | Domestic sewage treatment process |
CN105646064A (en) * | 2015-12-24 | 2016-06-08 | 北京林业大学 | Engineering method for producing biochar soil from dredging sediment |
CN106747779A (en) * | 2016-12-01 | 2017-05-31 | 宁波大学 | A kind of sludge compost improvement method |
CN107828419A (en) * | 2017-09-26 | 2018-03-23 | 湖南湘讯企业管理有限公司 | A kind of ecological restoration materials and its preparation method and application |
CN107892922A (en) * | 2017-11-29 | 2018-04-10 | 江苏源洁节能环保有限公司 | Soil conditioner and application thereof |
CN108373377A (en) * | 2018-02-13 | 2018-08-07 | 太原理工大学 | A kind of method of the Composting treatment of sludge from wastewater treatment plant |
CN109964766A (en) * | 2019-04-24 | 2019-07-05 | 鄂尔多斯市环保投资有限公司 | A kind of method of desert site preparation and rice cultivation |
Non-Patent Citations (4)
Title |
---|
任芝军: "《固体废物处理处置与资源化技术》", 31 May 2010, 哈尔滨工业大学出版社 * |
宋立杰: "《农用地污染土壤修复技术》", 31 January 2019, 冶金工业出版社 * |
张自杰: "《废水处理理论与设计》", 31 July 2003, 中国建筑工业出版社 * |
李清宏: "《节粮饲料的科学利用》", 31 October 2005, 中国社会出版社 * |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN115463956A (en) * | 2022-06-24 | 2022-12-13 | 沸高生物科技有限公司 | Method for reducing heavy metal pollution of tobacco |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN105347933B (en) | A method of matrix of sowing grass seeds by duster and using this sow grass seeds by duster matrix carry out saline land greening | |
US11572319B2 (en) | Solid waste-based porous materials, methods for preparing the same, and methods of ecological restoration of coal gangue hills by applying the same | |
Xu et al. | Effects of organic manure application with chemical fertilizers on nutrient absorption and yield of rice in Hunan of Southern China | |
CN103650692B (en) | A kind of sandy land amelioration method in applicable height wind erosion, water erosion area | |
CN108353563A (en) | A method of using waste be soil conditioner Desert Control soil | |
CN102498778B (en) | Method for improving saline-alkali sandy loam in areas formerly flooded by Yellow River | |
CN107912098A (en) | A kind of sand sticks the modification method of loamy texture saline-alkali soil | |
CN108243650A (en) | It is a kind of that the multiple green method of abandoned mine is strengthened using stabilisation sludge | |
CN103265361A (en) | Macromolecular aggregate plant growth substrate and preparation method thereof | |
CN104663065A (en) | Method for improving saline alkali soil in use of biomass charcoal | |
Wang et al. | A sand control and development model in sandy land based on mixed experiments of arsenic sandstone and sand: A case study in Mu Us Sandy Land in China | |
US6419722B1 (en) | Recycled soil | |
US6302936B1 (en) | Recycled soil | |
CN110720371A (en) | Method for restoring green sand by coal gasification solid slag | |
CN103964968B (en) | A kind of promote vegetation repair organic fertilizer produced from sludge generated and preparation method and application | |
CN110452705A (en) | A kind of heavy metal pollution of soil renovation agent and preparation method thereof | |
CN110038885A (en) | A kind of restorative procedure of mine soil | |
CN106083246A (en) | A kind of saline land greening special fertilizer and preparation, application process | |
CN103858552B (en) | Build method and the application thereof of topsoil in coarse sand earth's surface with heavy metal polluted bed mud | |
CN107935671A (en) | Compound charcoal base manure of a kind of iron silicon humus and preparation method thereof and application method | |
Wang et al. | Impact of Alternate Drought and Flooding Stress on Water Use, and Nitrogen and Phosphorus Losses in a Paddy Field. | |
CN104969681B (en) | The method of yellow mud sand quick improvement cement solonchak is drawn in a kind of utilization | |
CN113519231A (en) | Soilless reclamation method for fine sand tailings | |
CN110199606A (en) | A kind of combined type stony desertification ecological restoring method | |
CN108002960A (en) | One kind improvement salt-soda soil fertilizer special for organic |
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 | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20190906 |