CN101578943A - Composite desertification control method - Google Patents
Composite desertification control method Download PDFInfo
- Publication number
- CN101578943A CN101578943A CNA2009100847483A CN200910084748A CN101578943A CN 101578943 A CN101578943 A CN 101578943A CN A2009100847483 A CNA2009100847483 A CN A2009100847483A CN 200910084748 A CN200910084748 A CN 200910084748A CN 101578943 A CN101578943 A CN 101578943A
- Authority
- CN
- China
- Prior art keywords
- sand
- composite
- shrub
- desertification
- species
- 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
Images
Classifications
-
- 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
Landscapes
- Cultivation Of Plants (AREA)
Abstract
The invention discloses a composite desertification control method which comprises mixedly sowing annual herb tree species and perennial shrub species in the floating sand lands. In the invention, by mixedly sowing herb and shrub species in the floating sand lands, when the annual herbs wither to death, the overground deadwood and the underground root systems can retain for around 1 to 2 years and have good windbreak and sand-fixing effects, thus providing plant sand barriers for the shrubs which grow slowly and ensuring that the shrubs can grow rapidly in the second year. The composite sand consolidation structure featuring difference in growth time can effectively control soil drifting and desertification and soil erosion, reduce cost and improve desertification control efficiency dramatically.
Description
Technical field
The present invention relates to a kind of composite desertification control method of desert.
Background technology
At present, Chinese desertification land has 1,700,000 square kilometres approximately, and annual with 3400 square kilometres speed nearly in diffusion.In order to improve environment, prevent the desert migration, people have adopted the method for many sand controls, for example adopt Mechanical Method, comprise building sand-proof wall, truncheon grass etc.; Sow grass seeds for another example, fix the sand by vegetation.Though these methods have played certain sand fixation, it is not very good administering mobile bigger sand ground effect.
Summary of the invention
The technical problem to be solved in the present invention provides a kind of composite desertification control method that can control the soil wind erosion desertification effectively and be convenient to operate.
In order to address the above problem, to the invention provides a kind of composite desertification control method and be: the annual herbaceous plant kind of mixed seeding and perennial shrub species on the sand ground that flows.
Preferably, the ratio of described annual herb plant species of mixed seeding and shrub species is 1: 1~20.
Preferably, described ratio is 1: 10.
Preferably, carry out the mixed seeding of seeds, sow by latticed during mixed seeding in rainy season.
Preferably, described herbaceous plant kind comprises: wherein one or more of oat, wheat, described shrub comprises: wherein one or more of poplar bavin, caragana microphylla, sand sagebrush (Artemisia filifolia) and yellow Chinese scholartree.
Preferably, described herbaceous plant is selected oat.
Preferably, described shrub is selected the poplar bavin.
The present invention irritates careless seeds by mixed seeding on the sandy soil that flow, after annual herbaceous plant is withered, its ground deadwood and underground root system also can keep about 1~2 year, the effect of well checking winds and fixing drifting sand is arranged, this just provides plant sand block for the slow shrub (poplar bavin, caragana microphylla etc.) of growth, enables ramp in 1 year.By such composite sand consolidation structure, can control soil wind erosion desertification and water ground effectively and run off.
Description of drawings
Fig. 1 is the preceding shot picture of sowing;
Fig. 2 is after planting 1 day shot picture;
Fig. 3 is after planting 7 days shot picture;
Fig. 4 is after planting 20 days shot picture;
Fig. 5 is after planting 3 months shot picture;
Fig. 6 is after planting 10 months shot picture;
Fig. 7 is after planting 22 months shot picture;
Fig. 8 is after planting 26 months shot picture;
Fig. 9 is after planting 5 years 7 months shot picture.
Embodiment
Below the present invention will be described in detail.
On the sand ground that flows, use gramineous plants oat and shrub species poplar bavin, caragana microphylla mixed seeding afforestation.Oat is a therophytes; sand ground rainy season after planting; can become a complete individuality by development growth in very short time; after withered then; its ground deadwood and underground root system also can keep about 1~2 year; the effect of well checking winds and fixing drifting sand is arranged, and just poplar bavin, caragana microphylla provide the sand-protecting barrier protection in order to grow more slowly for this, enable ramp in 1 year.Shrub and grass mix seeding adopts 1.5 * 1.5 (rice), 2 * 2 (rice) latticed live, and filling grass seed ratio is 1: 10 (ratio can be 1: 1~20), and mu amount of broadcasting is about 22 jin, if the sand dune gradient is bigger, but the root actual conditions are dwindled grid, strengthen weather-proof ability.
Shrub and grass mix seeding afforestation time and method be specifically:
Carry out direct seeding forestation at the exposed sand ground that flows, harm direct seeding forestation the cause for the success mainly is a stream, shows as: A, make seed be difficult to sprout; B, make the seedling of firm germination,, tan by the sun and dead, or hit, cut off the seedling acrial part because of the grains of sand because of eroding naked; C, make root system delicate, the seedling that retain strength is low is all blown disconnected the disappearance.So the direct seeding forestation time generally should be avoided strong wind season, is selected in and carries out the rainy season that stream seldom occurs.
On the sand ground that flows, carry out direct seeding forestation with poplar bavin seed.For preventing that the shrub growth of seedling initial stage from suffering harm such as wind erosion, sand cut, sand buries, day burns; poplar bavin, oat seeds such as (or wheats) are mixed the back sowing in 1: 10 ratio; Avena herbaceous plant, the oat of intensive growth have formed the biological sand-protecting barrier of protection shrub seedling.Every mu of seeding quantity is 11 kilograms, uses the latticed afforestation seeding of sand control seed-sowing machine in rainy season, realizes the whole ground of trench digging, sowing, earthing one-shot forming.Mesh-density is 1 * 2~3 * 3 (m).
Shrub species can also be selected elm, caragana microphylla, sand sagebrush (Artemisia filifolia) and Huang Huai etc. except selecting above-mentioned poplar bavin.Certainly, preferred poplar bavin and caragana microphylla mainly are because select poplar bavin and caragana microphylla can also improve the biomass on grassland.Adapt to the sand ground growing plants and want palatability strong as feed, the nutrient composition content height, poplar bavin and caragana microphylla can both meet the demands well.In addition, when selecting, should also be noted that perennial Qiao, the shrub that suitable increase resistance is high, to constitute multi-level safeguard structure.
The sowing effect is specifically as Fig. 1~shown in Figure 9.Fig. 1 is the preceding shot picture of sowing; Fig. 2 is after planting 1 day shot picture; Fig. 3 is after planting 7 days shot picture; Fig. 4 is after planting 20 days shot picture; Fig. 5 is after planting 3 months shot picture; Fig. 6 is after planting 10 months shot picture; Fig. 7 is after planting 22 months shot picture; Fig. 8 is after planting 26 months shot picture; Fig. 9 is after planting 5 years 7 months shot picture.By above-mentioned desertification control method, can administer large tracts of land area sand ground every year, all kinds of sandy land vegetation cover degrees in husky district increase fast, have controlled the soil wind erosion desertification effectively, make farming and animal husbandry production obtain stable development, and ecotope obviously improves.
In sum; being preferred embodiment of the present invention only below, is not to be used to limit protection scope of the present invention, therefore; all any modifications of being done within the spirit and principles in the present invention, be equal to replacement, improvement etc., all should be included within protection scope of the present invention.
Claims (7)
1, a kind of composite desertification control method is characterized in that: the annual herbaceous plant seeds of mixed seeding and perennial shrub species on the sand ground that flows.
2, the method for claim 1 is characterized in that: the ratio of described herbaceous plant seeds of mixed seeding and shrub species is 1: 1~20.
3, method as claimed in claim 2 is characterized in that: described ratio is 1: 10.
4, the method for claim 1 is characterized in that: carry out mixed seeding in rainy season, (m) is latticed sows by 1 * 2~3 * 3 during mixed seeding.
5, as the arbitrary described method of claim 1 to 4, it is characterized in that: described herbaceous plant comprises: wherein one or more of oat, wheat, described shrub comprises: wherein one or more of poplar bavin, elm, caragana microphylla, sand sagebrush (Artemisia filifolia) and yellow Chinese scholartree.
6, method as claimed in claim 5 is characterized in that: described herbaceous plant is selected oat.
7, method as claimed in claim 5 is characterized in that: described shrub is selected the poplar bavin.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNA2009100847483A CN101578943A (en) | 2009-05-21 | 2009-05-21 | Composite desertification control method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNA2009100847483A CN101578943A (en) | 2009-05-21 | 2009-05-21 | Composite desertification control method |
Publications (1)
Publication Number | Publication Date |
---|---|
CN101578943A true CN101578943A (en) | 2009-11-18 |
Family
ID=41361371
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CNA2009100847483A Pending CN101578943A (en) | 2009-05-21 | 2009-05-21 | Composite desertification control method |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN101578943A (en) |
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102415244A (en) * | 2010-09-27 | 2012-04-18 | 深圳文科园林股份有限公司 | Planting design method for sand-binding plant community |
CN102511255A (en) * | 2011-11-15 | 2012-06-27 | 北京师范大学 | Mobile dune Salix cheilophila planting method |
CN103015397A (en) * | 2012-12-26 | 2013-04-03 | 若尔盖县综合林场 | Salix paraqplesia sand-protecting barrier for high and cold desert areas and setting method for Salix paraqplesia sand-protecting barrier |
CN103141278A (en) * | 2013-03-22 | 2013-06-12 | 西南民族大学 | Wind prevention and sand fixation greening planting technology |
CN104145671A (en) * | 2014-08-06 | 2014-11-19 | 呼伦贝尔市林业科学研究所 | Method for controlling grassland wind erosion desertification |
CN104255227A (en) * | 2014-08-29 | 2015-01-07 | 青海省农林科学院 | Method for arranging movable oat sand-protecting barrier on moving dune |
CN104365316A (en) * | 2014-09-12 | 2015-02-25 | 甘肃省治沙研究所 | Method for rapidly recovering close-to-nature sand stabilizing vegetation of shifting sandy land in semi-desert area |
CN109122074A (en) * | 2018-08-24 | 2019-01-04 | 内蒙古蒙草生态环境(集团)股份有限公司 | Hulun nur plant on sand land method |
CN109601044A (en) * | 2018-11-30 | 2019-04-12 | 环境保护部南京环境科学研究所 | A kind of type of seeding and application of valley pattern hillside flowing sand ground restoration of the ecosystem |
CN111788998A (en) * | 2020-07-29 | 2020-10-20 | 内蒙古自治区农牧业科学院 | Method for ecological restoration of desert grassland area by combining grass irrigation and grass irrigation |
-
2009
- 2009-05-21 CN CNA2009100847483A patent/CN101578943A/en active Pending
Cited By (13)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102415244A (en) * | 2010-09-27 | 2012-04-18 | 深圳文科园林股份有限公司 | Planting design method for sand-binding plant community |
CN102511255A (en) * | 2011-11-15 | 2012-06-27 | 北京师范大学 | Mobile dune Salix cheilophila planting method |
CN103015397A (en) * | 2012-12-26 | 2013-04-03 | 若尔盖县综合林场 | Salix paraqplesia sand-protecting barrier for high and cold desert areas and setting method for Salix paraqplesia sand-protecting barrier |
CN103141278B (en) * | 2013-03-22 | 2015-05-13 | 西南民族大学 | Wind prevention and sand fixation greening planting technology |
CN103141278A (en) * | 2013-03-22 | 2013-06-12 | 西南民族大学 | Wind prevention and sand fixation greening planting technology |
CN104145671A (en) * | 2014-08-06 | 2014-11-19 | 呼伦贝尔市林业科学研究所 | Method for controlling grassland wind erosion desertification |
CN104255227A (en) * | 2014-08-29 | 2015-01-07 | 青海省农林科学院 | Method for arranging movable oat sand-protecting barrier on moving dune |
CN104365316A (en) * | 2014-09-12 | 2015-02-25 | 甘肃省治沙研究所 | Method for rapidly recovering close-to-nature sand stabilizing vegetation of shifting sandy land in semi-desert area |
CN109122074A (en) * | 2018-08-24 | 2019-01-04 | 内蒙古蒙草生态环境(集团)股份有限公司 | Hulun nur plant on sand land method |
CN109122074B (en) * | 2018-08-24 | 2021-06-11 | 内蒙古蒙草生态环境(集团)股份有限公司 | Method for treating Hulun lake sand |
CN109601044A (en) * | 2018-11-30 | 2019-04-12 | 环境保护部南京环境科学研究所 | A kind of type of seeding and application of valley pattern hillside flowing sand ground restoration of the ecosystem |
CN109601044B (en) * | 2018-11-30 | 2021-09-07 | 环境保护部南京环境科学研究所 | Sowing method for ecological restoration of valley type hillside flowing sand land and application |
CN111788998A (en) * | 2020-07-29 | 2020-10-20 | 内蒙古自治区农牧业科学院 | Method for ecological restoration of desert grassland area by combining grass irrigation and grass irrigation |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN101578943A (en) | Composite desertification control method | |
US9089097B2 (en) | Method for improving survival rate of directly-planted seedling and transplanting seedling of haloxylon plant in desert or semi-desert environment | |
CN107996266B (en) | A kind of species assembly method of fast lifting extreme arid desert region vegetation coverage | |
CN102626031B (en) | Wild-simulation planting technique for multi-bud rhizoma paridis | |
CN103168585B (en) | A kind of Ammopiptanthus mongolicus container seedling culture method | |
CN101899825A (en) | Sand stabilizing method for direct-seeding plant living sand barrier | |
CN105917903B (en) | A kind of soil thin layer stony cut slope corrodes the soil and water conservation method on abrupt slope | |
CN102172133B (en) | Method for treating stony desertification in semiarid hot and warm area by applying improved pinus elliottii | |
CN105453873A (en) | Establishment method for desert steppe four-row-one-zone shrub and herb combined grassland | |
CN103733851A (en) | Method for preventing and fixing sands by using sheep manure | |
CN100344220C (en) | Sand control sand-fixation method | |
CN106804379B (en) | Method for promoting survival of transplanting anisetree bark in karst rocky mountain | |
CN104620924B (en) | Method for planting rubber trees | |
CN105103827A (en) | Sandy soil area vegetation fast construction mode | |
CN101485278A (en) | Planting method for throwing carrier containing young seedling of tree and nutrient in the air and special-purpose carrier thereof | |
CN207978291U (en) | A kind of sand prevention system of the interior plantation oat of straw checkerboard barrier | |
CN104186169B (en) | Method for arranging highland barley living sand barrier in moving dune | |
CN109463208A (en) | Desertification is checked winds and fixed drifting sand straw cord sand-protecting barrier planting administering method | |
CN117716942A (en) | Method for restoring degraded grassland in implanted mode | |
CN104145671A (en) | Method for controlling grassland wind erosion desertification | |
CN207812434U (en) | A kind of Rocky Desertification Region stock growing system | |
CN201131202Y (en) | Water conservation and maintenance soil plant breeding device | |
CN105103869A (en) | Wild gastrodia elata cultivation method | |
CN205143069U (en) | Wasteland vegetation maintenance structure | |
CN104620815B (en) | Paspalum natatum planting method for preventing water and soil loss |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C12 | Rejection of a patent application after its publication | ||
RJ01 | Rejection of invention patent application after publication |
Open date: 20091118 |