CN105519397A - Construction method of salix sungkianica revetment-biological habitat of river erosion bank - Google Patents
Construction method of salix sungkianica revetment-biological habitat of river erosion bank Download PDFInfo
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- CN105519397A CN105519397A CN201510869655.7A CN201510869655A CN105519397A CN 105519397 A CN105519397 A CN 105519397A CN 201510869655 A CN201510869655 A CN 201510869655A CN 105519397 A CN105519397 A CN 105519397A
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- Prior art keywords
- bank
- dryland willow
- shore protection
- willow
- dryland
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Classifications
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- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G17/00—Cultivation of hops, vines, fruit trees, or like trees
- A01G17/005—Cultivation methods
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- E—FIXED CONSTRUCTIONS
- E02—HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
- E02B—HYDRAULIC ENGINEERING
- E02B3/00—Engineering works in connection with control or use of streams, rivers, coasts, or other marine sites; Sealings or joints for engineering works in general
- E02B3/04—Structures or apparatus for, or methods of, protecting banks, coasts, or harbours
- E02B3/12—Revetment of banks, dams, watercourses, or the like, e.g. the sea-floor
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- 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
- Y02A10/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE at coastal zones; at river basins
- Y02A10/11—Hard structures, e.g. dams, dykes or breakwaters
-
- 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
- Y02A10/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE at coastal zones; at river basins
- Y02A10/30—Flood prevention; Flood or storm water management, e.g. using flood barriers
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- Engineering & Computer Science (AREA)
- General Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Botany (AREA)
- Environmental Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Ocean & Marine Engineering (AREA)
- Mechanical Engineering (AREA)
- Civil Engineering (AREA)
- Structural Engineering (AREA)
- Revetment (AREA)
Abstract
The present invention provides a construction method of a salix sungkianica revetment-biological habitat of a river erosion bank, and relates to the technical field of flood plain hygrophyte salix sungkianica revetment and biological habitat construction. The double problems that riverbank erosion is severe and biodiversity is sharply declined in the Songhua River and Heilongjiang areas are solved. The construction method comprises the following steps of (1) selecting a coastline area with the river bank eroded at bank sides of the main stream of the Songhua River or islands in the middle of the river; and (2) constructing and obtaining a salix sungkianica revetment at the erosion bank side in a manner of cutting, seedling transplanting or combination of the two modes, constructing an engineering revetment between the salix sungkianica revetment and the water for the river bank which is severely eroded, and completing construction of the salix sungkianica revetment-biological habitat of the river erosion bank. The river bank soil is fixed by means of developed roots of the salix sungkianica, erosion of river water on the river bank is reduced, the salix sungkianica can also provide aquatic birds with perch and nesting places, aquatic organisms are relatively abundant in a dense salix sungkianica system, and therefore biodiversity is improved.
Description
Technical field
The present invention relates to alluvial flat hygrophyte dryland willow shore protection and constructing technology field, biological habitat, be specifically related to a kind of construction method of channel erosion bank dryland willow shore protection-biological habitat.
Background technology
At present, downstream, Song Hua River destroys because of the mankind and water pollution causes riverine wetland to destroy seriously, and bio-diversity reduces, Function of Wetland serious degradation.Meanwhile, under Coriolis force effect, Northern Hemisphere flowing water has deflecting force to the right and then causes river right bank to occur Eroded phenomenon.Fall sharply with under the dual-pressure of bank erosion in bio-diversity, a kind of reasonable, economic and applicable riverbank recovery technique must be sought.
Dryland willow (formal name used at school: Songjiang willow Salixsungkianica, Longjiang willow Salixsachalinensis) is Heilungkiang, Songhua River Basin alluvial flat " mangrove forest " plant, growth is fast, height about 2 ~ 3 meters, stem is undeveloped, becomes Cong Zhizhuan, with luxuriant foliage and spreading branches in leafy profusion, well developed root system, have aerial root, resistance to water logging, ecological functions are strong.But, still lack the correlative study adopting dryland willow plantation to protect eroding bank and bio-diversity at present.
Summary of the invention
The object of the invention is the two fold problem fallen sharply to solve the serious and bio-diversity of Song Hua River, Heilongjiang river bank erosion, and a kind of construction method of channel erosion bank dryland willow shore protection-biological habitat is provided.
The construction method of channel erosion bank dryland willow shore protection-biological habitat of the present invention realizes according to the following steps:
One, main stream of Songhua River bank or ait is selected to there is the water front region of bank erosion as dryland willow planting site;
Two, in the method that season in the early spring adopts cuttage, seedling is planted or two kinds of modes combine dryland willow dense planting built on dryland willow planting site and obtain dryland willow shore protection, dryland willow spacing in the rows controls, at (4 ~ 10) cm × (4 ~ 10) cm, to complete the structure of channel erosion bank dryland willow shore protection-biological habitat.
The present invention is channel erosion bank plantation dryland willow, and the root system by dryland willow prosperity fixes riverbank soil, reduces river to the erosion on riverbank; Simultaneously sagging withy and exposed dense natural pond willow root system both can be fish and lay eggs and provide " attachment ", and can be again juvenile fish provides " sanctuary ", can be used as the settlement of species diversity.Aquatile relative abundance in dense dryland willow system, both can be aquatic bird and provided the environment of nesting, perching, can be again the food that aquatic bird provides certain.
In sum, the construction method of channel erosion bank dryland willow shore protection-biological habitat of the present invention, not only effectively can contain the retrogressing of caving in of downstream, Song Hua River and Heilungkiang right bank eroding bank, reduces territory loss; And exposed dryland willow root system can be fish-egg and provides " attachment ", there is the effect of " fish nest "; The root system that dryland willow is dense also can be juvenile fish and provides and perch and " taking refuge " place; Dryland willow also can be aquatic bird and provides roost and place of nesting, and contributes to the recovery of bio-diversity to a certain extent.Meanwhile, the enforcement of dryland willow shore protection ecological technique effectively can reduce engineering measures such as " T-shaped dams ", not only cost-saving, also can available protecting alluvial flat wetland.The present invention has that corrosion protection result is good, cost is low, simple to operate, easy, ecological benefits significantly, be convenient to the features such as large scale application.
Accompanying drawing explanation
Fig. 1 is that embodiment builds the structural representation of eroding bank dryland willow shore protection-biological habitat in Fujin City Song Hua River section.
Embodiment
Embodiment one: the construction method of present embodiment channel erosion bank dryland willow shore protection-biological habitat realizes according to the following steps:
One, main stream of Songhua River bank or ait is selected to there is the water front region of bank erosion as dryland willow planting site;
Two, in the method that season in the early spring adopts cuttage, seedling is planted or two kinds of modes combine dryland willow dense planting built on dryland willow planting site and obtain dryland willow shore protection, dryland willow spacing in the rows controls, at (4 ~ 10) cm × (4 ~ 10) cm, to complete the structure of channel erosion bank dryland willow shore protection-biological habitat.
Present embodiment adopts mode of drawing materials nearby, select hygrophyte Songjiang of one's native land willow, Longjiang willow, in the dense planting means that season in the early spring utilizes cuttage and seedling to plant to combine, the dryland willow of collection is inserted skewer with the segment branch of whole branch or band bud respectively and sprigging mode carries out slotting skewer and transplanting.
Embodiment two: dryland willow dense planting to build in the method that 4 ~ May adopts cuttage, seedling is planted or two kinds of modes combine unlike step 2 and obtains dryland willow shore protection by present embodiment and embodiment one on dryland willow planting site.Other step and parameter identical with embodiment one.
Embodiment three: present embodiment and embodiment one or two adopt the method for cuttage to insert skewer dense planting on dryland willow planting site by being with the whole dryland willow branch of bud unlike step 2.Other step and parameter identical with embodiment one or two.
Embodiment four: one of present embodiment and embodiment one to three adopt the method for planting by dryland willow sprigging on dryland willow planting site unlike step 2.Other step and parameter identical with one of embodiment one to three.
Embodiment five: one of present embodiment and embodiment one to four are (4 ~ 7) cm × (4 ~ 7) cm unlike the spacing in the rows controlled between dryland willow.Other step and parameter identical with one of embodiment one to four.
Embodiment six: present embodiment and embodiment five are 5cm × 5cm unlike the spacing in the rows controlling dryland willow.Other step and parameter identical with embodiment five.
Embodiment seven: one of present embodiment and embodiment one to six are 3 ~ 10m unlike the width of step 2 dryland willow shore protection.Other step and parameter identical with one of embodiment one to six.
Embodiment eight: one of present embodiment and embodiment one to seven are also provided with engineering shore protection unlike step 2 below the eroding bank of avalanche.Other step and parameter identical with one of embodiment one to seven.
Present embodiment, for corroding serious riverbank, arranges engineering shore protection between dryland willow and water body, and engineering shore protection is 0.3 ~ 0.5m apart from the distance at the edge of the close water body of dryland willow shore protection.
Embodiment nine: present embodiment and embodiment eight are 3 ~ 5m unlike the width of described engineering shore protection.Other step and parameter identical with embodiment eight.
Embodiment ten: present embodiment and embodiment eight are built, pile up sandbag or build timber in a row unlike described engineering shore protection and form by jackstone.Other step and parameter identical with embodiment eight.
The effective stop of present embodiment utilizing works shore protection to current obtains efficiently surviving of dryland willow transplant early.
Embodiment one: the construction method of the present embodiment channel erosion bank dryland willow shore protection-biological habitat realizes according to the following steps:
One, Fujin City Song Hua River, Heilongjiang Province (downstream) section is selected to there is the water front region (in Fig. 1 A place) of bank erosion as dryland willow planting site;
The segment dryland willow branch dense planting of whole dryland willow branch or band bud builds and obtains width by the method two, adopting cuttage and transplanting to combine in May on dryland willow planting site is 8m dryland willow shore protection, the spacing in the rows controlled between dryland willow is 5cm × 5cm, at dryland willow shore protection, towards water body direction, vertically extending 0.5m place builds the engineering shore protection that width is 4m, completes the structure of channel erosion bank dryland willow shore protection-biological habitat.
Embodiment two: the construction method of the present embodiment channel erosion bank dryland willow shore protection-biological habitat realizes according to the following steps:
One, Fujin City Song Hua River, Heilongjiang Province (downstream) section is selected to there is the water front region (in Fig. 1 B place) of bank erosion as dryland willow planting site;
Two, adopt the method for transplanting to be implanted in by whole dryland willow branch dryland willow planting site builds that to obtain width be 8m dryland willow shore protection in May, the spacing in the rows controlled between dryland willow is 5cm × 5cm, completes the structure of channel erosion bank dryland willow shore protection-biological habitat.
The present embodiment does not adopt engineering shore protection.It is for corroding serious riverbank that embodiment one builds shore protection, and embodiment two does not adopt engineering shore protection mainly for the lighter riverbank of erosion degree.The continuation of eroding bank effectively can be prevented to corrode by above construction method, corrode after water front no longer occurs and move phenomenon, and improve bio-diversity.
Claims (10)
1. a construction method for channel erosion bank dryland willow shore protection-biological habitat, it is characterized in that following these steps to realize:
One, main stream of Songhua River bank or ait is selected to there is the water front region of bank erosion as dryland willow planting site;
Two, in the method that season in the early spring adopts cuttage, seedling is planted or two kinds of modes combine dryland willow dense planting built on dryland willow planting site and obtain dryland willow shore protection, dryland willow spacing in the rows controls, at (4 ~ 10) cm × (4 ~ 10) cm, to complete the structure of channel erosion bank dryland willow shore protection-biological habitat.
2. the construction method of a kind of channel erosion bank dryland willow shore protection-biological habitat according to claim 1, is characterized in that dryland willow dense planting to build in the method that 4 ~ May adopts cuttage, seedling is planted or two kinds of modes combine by step 2 on dryland willow planting site and obtains dryland willow shore protection.
3. the construction method of a kind of channel erosion bank dryland willow shore protection-biological habitat according to claim 1, is characterized in that step 2 adopts the method for cuttage that the whole dryland willow branch of band bud is inserted skewer dense planting on dryland willow planting site.
4. the construction method of a kind of channel erosion bank dryland willow shore protection-biological habitat according to claim 1, is characterized in that step 2 adopts the method for planting by dryland willow sprigging on dryland willow planting site.
5. the construction method of a kind of channel erosion bank dryland willow shore protection-biological habitat according to claim 1, is characterized in that step 2 dryland willow spacing in the rows controls at (4 ~ 7) cm × (4 ~ 7) cm.
6. the construction method of a kind of channel erosion bank dryland willow shore protection-biological habitat according to claim 5, is characterized in that the spacing in the rows of step 2 control dryland willow is 5cm × 5cm.
7. the construction method of a kind of channel erosion bank dryland willow shore protection-biological habitat according to claim 1, is characterized in that the width of step 2 dryland willow shore protection is 3 ~ 10m.
8. the construction method of a kind of channel erosion bank dryland willow shore protection-biological habitat according to claim 1, is characterized in that step 2 is also provided with engineering shore protection below the eroding bank of avalanche.
9. the construction method of a kind of channel erosion bank dryland willow shore protection-biological habitat according to claim 8, is characterized in that the width of described engineering shore protection is 3 ~ 5m.
10. the construction method of a kind of channel erosion bank dryland willow shore protection-biological habitat according to claim 8, is characterized in that described engineering shore protection is built by jackstone, piled up sandbag or build timber in a row and form.
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
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CN106381837A (en) * | 2016-10-21 | 2017-02-08 | 中国电建集团中南勘测设计研究院有限公司 | Ecological restoration structural system and restoration method for lakeside zone |
CN107268521A (en) * | 2017-08-10 | 2017-10-20 | 中国环境科学研究院 | A kind of biological habitat construction method in cold area's chiltern abrupt slope |
CN107836266A (en) * | 2017-11-06 | 2018-03-27 | 广西壮族自治区环境保护对外合作交流中心 | The method that eastern ape with long arms and a black comb karst habitat is recovered |
CN115968700A (en) * | 2022-12-12 | 2023-04-18 | 中国科学院东北地理与农业生态研究所 | Planting method of cold region riverside buffer spotted blocky willow cluster |
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
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CN106381837A (en) * | 2016-10-21 | 2017-02-08 | 中国电建集团中南勘测设计研究院有限公司 | Ecological restoration structural system and restoration method for lakeside zone |
CN107268521A (en) * | 2017-08-10 | 2017-10-20 | 中国环境科学研究院 | A kind of biological habitat construction method in cold area's chiltern abrupt slope |
CN107836266A (en) * | 2017-11-06 | 2018-03-27 | 广西壮族自治区环境保护对外合作交流中心 | The method that eastern ape with long arms and a black comb karst habitat is recovered |
CN115968700A (en) * | 2022-12-12 | 2023-04-18 | 中国科学院东北地理与农业生态研究所 | Planting method of cold region riverside buffer spotted blocky willow cluster |
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