CN110089353A - A kind of hard side slope greening restoration method - Google Patents
A kind of hard side slope greening restoration method Download PDFInfo
- Publication number
- CN110089353A CN110089353A CN201910384331.2A CN201910384331A CN110089353A CN 110089353 A CN110089353 A CN 110089353A CN 201910384331 A CN201910384331 A CN 201910384331A CN 110089353 A CN110089353 A CN 110089353A
- Authority
- CN
- China
- Prior art keywords
- slope
- side slope
- soil
- hard side
- restoration method
- 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
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G13/00—Protecting plants
- A01G13/02—Protective coverings for plants; Coverings for the ground; Devices for laying-out or removing coverings
- A01G13/0206—Canopies, i.e. devices providing a roof above the plants
-
- 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
-
- 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
- A01G20/00—Cultivation of turf, lawn or the like; Apparatus or methods therefor
-
- 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
- A01G22/00—Cultivation of specific crops or plants not otherwise provided for
- A01G22/60—Flowers; Ornamental plants
-
- 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
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/10—Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material
-
- 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
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/10—Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material
- A01G24/12—Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material containing soil minerals
-
- 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
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/10—Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material
- A01G24/12—Growth substrates; Culture media; Apparatus or methods therefor based on or containing inorganic material containing soil minerals
- A01G24/15—Calcined rock, e.g. perlite, vermiculite or clay aggregates
-
- 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
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/20—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material
- A01G24/28—Growth substrates; Culture media; Apparatus or methods therefor based on or containing natural organic material containing peat, moss or sphagnum
-
- 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
- A01G24/00—Growth substrates; Culture media; Apparatus or methods therefor
- A01G24/30—Growth substrates; Culture media; Apparatus or methods therefor based on or containing synthetic organic compounds
-
- 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
- A01G25/00—Watering gardens, fields, sports grounds or the like
- A01G25/02—Watering arrangements located above the soil which make use of perforated pipe-lines or pipe-lines with dispensing fittings, e.g. for drip irrigation
-
- E—FIXED CONSTRUCTIONS
- E02—HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
- E02D—FOUNDATIONS; EXCAVATIONS; EMBANKMENTS; UNDERGROUND OR UNDERWATER STRUCTURES
- E02D17/00—Excavations; Bordering of excavations; Making embankments
- E02D17/20—Securing of slopes or inclines
-
- E—FIXED CONSTRUCTIONS
- E02—HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
- E02D—FOUNDATIONS; EXCAVATIONS; EMBANKMENTS; UNDERGROUND OR UNDERWATER STRUCTURES
- E02D17/00—Excavations; Bordering of excavations; Making embankments
- E02D17/20—Securing of slopes or inclines
- E02D17/202—Securing of slopes or inclines with flexible securing means
-
- 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
- Life Sciences & Earth Sciences (AREA)
- Environmental Sciences (AREA)
- Engineering & Computer Science (AREA)
- Mining & Mineral Resources (AREA)
- Soil Sciences (AREA)
- Inorganic Chemistry (AREA)
- Chemical & Material Sciences (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Structural Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Civil Engineering (AREA)
- Paleontology (AREA)
- Botany (AREA)
- Water Supply & Treatment (AREA)
- Health & Medical Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Toxicology (AREA)
- Cultivation Of Plants (AREA)
- Pit Excavations, Shoring, Fill Or Stabilisation Of Slopes (AREA)
Abstract
The invention discloses a kind of hard side slope greening restoration methods, it cleared up including slope surface, setting anchor pole, be laid with galvanized wire mesh sheet, Red Sandstone is modified to planting soil, is laid with geomembrane, sows, establishing automatic irrigation system and operation and maintenance, it is improved to modifying agent is mixed in the red sand rock-soil layer of different content amount containing sandstone, spray head is installed in pre-buried spray system using automatic control system simultaneously, it is planted by spray head irrigating plant, spray irrigation system can be automatically controlled according to temperature humidity.The present invention provides a kind of hard slope greening recovery technique that Red Sandstone is modified to planting soil, long term growth condition is provided for vegetation, realize the restoration of the ecosystem demand of slope of rock mass, hard slope surface, slope protection greening cultivated plant is combined with traditional plant cover concrete ecological reestablishment, revegetation carries out simultaneously with anchoring fixation, can preferably realize the growth of vegetation and the fixation of side slope in side slope.
Description
Technical field
The present invention relates to Ecological Restoration Project and afforestation project fields, and in particular to hard side slope greening restoration method.
Background technique
China is more serious for vegetation deterioration since urban construction in recent years is accelerated, and green areas is caused to significantly reduce,
Then attention of the people to environment and the ecological balance is caused.And novel ecological slope protection has begun large-scale popularization use.?
Water power, municipal administration, in mine engineering, due to construction and excavation, forms a large amount of exposed slope of rock mass, some slope surfaces are using injection at traffic
The engineering constructions such as concrete, stone masonry protect to form hard slope surface, these slope of rock mass, hard slope surface are due to lacking vegetation growth
Condition, ecological environment is poor, and slope landscape effect demand fails to be settled properly for a long time.
Some Red Sandstone in hard side slope, mainly two kinds of typical structures of fragmental texture and pureed cement structure in pelletized form
Form, because of the difference of binding material and rate of decay, the variation of intensity is big.Most Red Sandstones after excavation or explosion come out,
Effect disintegratable by atmospheric environment is broken or even argillization, thus the size of its sillar and grain composition by with drying and watering cycle when
Between process and change, physico-mechanical properties also by generate variation, in the prior art can not for the greening reparation of hard side slope
Using original Red Sandstone, need to re-lay planting soil, cost is excessively high.
Summary of the invention
There are problems for above-mentioned, and the purpose of the present invention is to provide a kind of hard edges that Red Sandstone is modified to planting soil
Recovery technique is afforested on slope, is provided long term growth condition for vegetation, is realized the restoration of the ecosystem demand of slope of rock mass, hard slope surface.Energy
It is enough effectively to keep high steep hard side slope Afforestation Landscape.
To achieve the above object, the technical solution adopted by the present invention is that: a kind of hard side slope greening restoration method, feature
It is: the following steps are included:
S1. slope surface is cleared up: on side slope slope of rock mass, being removed work surface sundries and is loosened sillar, soil block, to slope surface corner
The corner angle of place and top of the slope are modified, and are allowed to arc-shaped, and part rock outstanding and soil block should remove or carry out to cut slope processing, and
And it carries out snap the line grid division and is numbered；
S2., anchor pole is set: anchor pole being uniformly equidistantly inserted into the structure sheaf of hard side slope；
S3. lapped layup galvanized wire mesh sheet from top to bottom；
S4. incorporation modifying agent in red sand rock-soil layer and plain soil are improved, is modified to improvement plantation layer；
S5. it is laid with geomembrane, the improvement improved by Red Sandstone plantation layer is laid on geomembrane on geomembrane；
S6. improvement plantation layer made of Red Sandstone improvement is uniformly sowed, and grass-seed, nutritional agents, accelerator, takes root at flowering shrub
The uniform mixing jetting of agent is conducive to taking root for plant on scar, after planting using cotton covering and timely water seasoning, morning and evening
Each primary watering, heat and moisture preserving；Shading net is propped after emerging or heavy foliage branch carries out sunshade；
S7. cotton and shading net is raised to seedling 10CM or more to grow naturally by it；
S8. spray irrigation system is established, slope greening cultivated plant is automatically controlled according to temperature humidity and carries out spray maintenance.
S9. it runs and conserves.
Further, in the step S4, weight percentage of each component composition are as follows: Red Sandstone 70%, carragheen 15%-
17%, humus 4%-6%, plant ash 1-2%, then mix plain soil 8-10%.
Further, in the step S4, after modifying agent mixes in red sand rock-soil layer, stack is formed after making its uniform mix；
Watering, makes its moisture content reach 30%~40%；It is covered, is macerated 2~3 days using cotton.
Further, in the step S2, longitudinal pitch and horizontal spacing between the anchor pole and anchor pole are 2-3m, anchor
Pole length is 5-6m.
Further, in the step S3, the lap width of adjacent galvanized wire mesh sheet is at least 10cm, the galvanized iron
The mesh of silk netting is 10cm × 10cm.
Further, in the step S6, according to operation side soil or scar property, local climate condition, construction season
Section, and herbaceous plant and the Qiao, shrub of various plant growth characteristics selection well developed root system are combined, and species should be with endemic plant
It is main；The seed activity of reply buying, purity are monitored before grass seeds sowing.
Further, it in the step S8, establishes spray irrigation system and is included in the spaced many places tank in top of the slope area, be used for
The rainwater collected is stored, and is supplied water using automatic sprinkling system, automatic sprinkling system and tank use flexible duct between the two
Connection, the automatic sprinkling system include main-supply, control valve are arranged in branch's water injection pipe and control system, main-supply,
Each control valve controls the main-supply and branch's water injection pipe of automatic sprinkling system, sets on the main-supply and branch's water injection pipe
There is spray head, the control system automatically controls spray head according to temperature and humidity and carries out spray maintenance.
Further, the confluence ditch and classification platform of several vertical interlaceds, the confluence ditch are additionally provided on hard side slope surface
Slope of rock mass is separated into several green belt with classification platform, convenient for planting the spraying of raw substrate, the two sides of green belt are equipped with
Waterwall, the bottom of slope are equipped with intercepting ditch, and intercepting ditch is connected with confluence ditch, and the top of the slope is equipped with pressure sheath, press sheath and position
It is poured in the waterwall top of top layer into a single integrated structure.
Further, in the step S9, after the completion of construction, spray irrigation system is run for the first time will fill in tank, kept
The water yield of system is run in maximum rating, fixed after soaking body formation and volume reaches the root zone volume for being enough to contain crop
Phase measuring soil moisture, and control valve or tank water level control spray irrigation system filling pipe water yield, make gradient soil
Humidity keeps 20~30%.
Compared with prior art, the beneficial effects of the present invention are:
1. red rock soil is modified to planting soil, after Red Sandstone improves planting soil improvement, the PH of red sand ground can be reduced, and effectively
Organic matter, humic acid, nitrogen, phosphorus, potassium equal size in red sand ground are supplemented, taking root for plant is conducive to.Long-term life is provided for vegetation
Elongate member.
2. the present invention combines slope protection greening cultivated plant with traditional plant cover concrete ecological reestablishment, revegetation
It is carried out simultaneously with anchoring fixation, can preferably realize the growth of vegetation and the fixation of side slope in side slope.One can be formed
A complete Eco-farming shelterbelt system, easy for construction, structural stability is good, and erosion resistibility is strong, and more effect solves exposed ragstone
Slope surface can not growing plant problem, so that rock slope is reached complete greening.
3. installing spray head in pre-buried spray system, is planted by spray head irrigating plant, sprayed using automatic control system
System can be automatically controlled according to temperature humidity.
Detailed description of the invention
Fig. 1 is overall structure diagram of the invention；
Fig. 2 is main view of the present invention；
Fig. 3 is galvanized wire mesh schematic diagram of the present invention；
Fig. 4 is that the present invention automatically controls spray irrigation system schematic diagram；
Fig. 5 is Red Sandstone improvement schematic diagram of the present invention；
In figure: 1- top of the slope, 2- pressure sheath, 3- bottom of slope, 4- intercepting ditch, 5- slope of rock mass, 6- galvanized wire mesh sheet, 7- geotechnique
Film, 8- improvement plantation layer, 9- anchor pole, 10- automatic irrigation system, 11- tank, 12- confluence ditch, 13- waterwall, 14- original are red
Sandstone soil layer, 15- main-supply, 16- branch water injection pipe, 17- control valve, 18- spray head.
Specific embodiment
The present invention provides a kind of hard side slope greening restoration method.Technical solution provided by the embodiment of the present invention is to solve
Above-mentioned technical problem, in order to better understand the above technical scheme, below in conjunction with Figure of description and specific embodiment party
The above described technique is demenstrated in detail for formula.
The present invention provides a kind of hard side slope greening restoration method, comprising the following steps:
S1. slope surface is cleared up: on side slope slope of rock mass 5, being removed work surface sundries and is loosened sillar, soil block, turn to slope surface
At angle and the corner angle of top of the slope are modified, and are allowed to arc-shaped, and part rock outstanding and soil block should remove or carry out to cut slope processing,
And it carries out snap the line grid division to be numbered；
S2., anchor pole 9 is set: will be in the anchor pole 9 uniformly structure sheaf of equidistant insertion hard side slope；
S3. lapped layup galvanized wire mesh sheet 6 from top to bottom；
S4. incorporation modifying agent in red sand rock-soil layer 14 and plain soil are improved, is modified to improvement plantation layer 8；
S5. it is laid with geomembrane 7, the improvement improved by Red Sandstone plantation layer 8 is laid on geomembrane 7 on geomembrane 7；
S6. improvement plantation layer 8 made of Red Sandstone improvement is uniformly sowed, and grass-seed, nutritional agents, accelerator, takes root at flowering shrub
The uniform mixing jetting of agent is conducive to taking root for plant on scar, after planting using cotton covering and timely water seasoning, morning and evening
Each primary watering, heat and moisture preserving；Shading net is propped after emerging or heavy foliage branch carries out sunshade；
S7. cotton and shading net is raised to seedling 10CM or more to grow naturally by it；
S8. spray irrigation system is established, slope greening cultivated plant is automatically controlled according to temperature humidity and carries out spray maintenance.
S9. it runs and conserves.
In the step S4, in step S4, weight percentage of each component composition are as follows: Red Sandstone 70%, carragheen 15%-
17%, humus 4%-6%, plant ash 1-2%, then mix plain soil 8-10%.
In the above-described embodiments, Red Sandstone is in grittiness, meets water and is easy to run off, and carragheen has certain gel effect, can
The loss of soil before plant growth is prevented, plant ash has potassium, phosphoric acid and lime abundant.Humus is completely rotten warp
The plant and animal residues of microorganism decomposition, have the cohesiveness of appropriateness, and sand coheres.Containing there are many nutrients, and there is stronger suction
The property received, can improve soil fertilizer, water retention property, can also buffer soil ph variation, be conducive to microbial activities and plant is raw
It is long.
Red Sandstone to be improved as after planting soil, organic fertilizer and inorganic builder are applied when fertilising, nitrogen, phosphorus, potash fertilizer compounding application,
To improve chemical fertilizer utilization ratio, applied nitrogen can be made into ball fertilizer and apply deeply, and phosphate fertilizer wants row replacement, cave to apply, and concentrates and applies after mixing with farmyard manure,
It is needed suitably to increase potash fertilizer according to plant growth.
As shown in Fig. 2, further preferred scheme is, in the step S2, between the longitudinal direction between the anchor pole 9 and anchor pole
Away from being 2-3m, rock-bolt length 5-6m with horizontal spacing.
As shown in figure 3, further preferred scheme is in the step S3 on the basis of the above embodiments, it is adjacent zinc-plated
The lap width of iron wire mesh sheet 6 is at least 10cm, and the mesh of the galvanized wire mesh sheet is 10cm × 10cm.
In the above-described embodiments, it in step S6, according to operation side soil or scar property, local climate condition, applies
Work season, and herbaceous plant and the Qiao, shrub of various plant growth characteristics selection well developed root system are combined, and species should be planted with locality
Based on object；The seed activity of reply buying, purity are monitored before grass seeds sowing, should ensure that the density 6 of seed when grass seeds broadcasts sowing
~9kg/hm2.Undesirable seed is forbidden using can sow grass seeds by duster different patterns, and bald spot occurs in reply when late maintaining
Position repaired in time.
In the step S8, establishes spray irrigation system and be included in the spaced many places tank 11 in top of the slope area, for storing
The rainwater of collection, and supplied water using automatic sprinkling system 10, automatic sprinkling system 10 and tank 11 use flexible pipe between the two
Road connection, the automatic sprinkling system 10 on main-supply 15, branch's water injection pipe 16 and control system, main-supply 15 including setting
Set control valve 17, the main-supply and branch's water injection pipe of each control valve control automatic sprinkling system, the main-supply and point
Branch water injection pipe is equipped with spray head 18, and the control system automatically controls spray head according to temperature and humidity and carries out spray maintenance.
In the above-described embodiments, tank 11 can be arranged one at interval of 10m.
As shown in Figure 1, in the above-described embodiments, 12 He of confluence ditch of several vertical interlaceds is additionally provided on hard side slope surface
It is classified platform, slope of rock mass is separated into several green belt with classification platform by the confluence ditch 12, convenient for planting the injection of raw substrate
Operation, 3 bottom of slope be equipped with intercepting ditch 4, intercepting ditch 4 with confluence ditch 12 be connected, the top of the slope 1 be equipped with pressure sheath 2, press sheath 2 and
Poured positioned at 13 top of waterwall of top layer into a single integrated structure, intercepting ditch 4 passed through and collects rainwater and make in the season that rainfall is plentiful
For the water supply source of tank 11, when rainwater deficiency and artificial recharge is can be used as tank in plant recovery initial stage
Resource of water supply.Pouring and the drainage problem of slope greening are can effectively solve.
In the above-described embodiments, in step S9, after the completion of construction, spray irrigation system is run for the first time will fill in tank,
The water yield of holding system is run in maximum rating, when wetting body is formed and volume reaches and is enough to contain the root zone volume of crop
Afterwards, results of regular determination soil moisture, and control valve or tank water level control spray irrigation system filling pipe water yield keep the gradient native
The humidity of earth keeps 20~30%.It is conserved according to related requirement specification, the particular content of maintenance includes watering, applying fertilizer, repairing
It cuts, sunshade, a series of activities measure such as disease pest and weed.Planting nursery stock is poured with natural water, must water within 48 hours later
A time water, second time water then carries out, and notices that watering must be watered with and irrigates, is carried out in time with puggaree under burning sun after having poured
Sunshade, to keep moisture in planting medium.
It is suitable for shrub, Climbing Plant that vegetation, which is selected, can be effectively improved the vegetative coverage of slope surface.When vegetation growth, root system
Substantially it is limited in soil grid, in addition the effect of outer layer filling compressible material, reducing root system spalling may be to slope surface
Adverse effect.
Specific embodiments of the present invention are described in detail above, but it is intended only as one such embodiment,
The present invention is not restricted to particular embodiments described above.To those skilled in the art, any couple of present invention carries out
Equivalent modifications and substitution also all among scope of the invention.Therefore, made without departing from the spirit and scope of the invention
Equal transformation and modification, all should be contained within the scope of the invention.
Claims (9)
1. a kind of hard side slope greening restoration method, it is characterised in that: the following steps are included:
S1. slope surface is cleared up: on side slope slope of rock mass, remove work surface sundries and loosen sillar, soil block, to slope surface corner and
The corner angle of top of the slope are modified, and are allowed to arc-shaped, and part rock outstanding and soil block should remove or carry out to cut slope processing, and into
Row snap the line grid division is numbered；
S2., anchor pole is set: anchor pole being uniformly equidistantly inserted into the structure sheaf of hard side slope；
S3. lapped layup galvanized wire mesh sheet from top to bottom；
S4. incorporation modifying agent in red sand rock-soil layer and plain soil are improved, is modified to improvement plantation layer；
S5. it is laid with geomembrane, the improvement improved by Red Sandstone plantation layer is laid on geomembrane on geomembrane；
S6. improvement plantation layer made of Red Sandstone improvement is uniformly sowed, and grass-seed, flowering shrub, nutritional agents, accelerator, root-growing agent are equal
Even mixing jetting is conducive to taking root for plant on scar, after planting using cotton covering and timely water seasoning, morning and evening each one
Secondary watering, heat and moisture preserving；Shading net is propped after emerging or heavy foliage branch carries out sunshade；
S7. cotton and shading net is raised to seedling 10CM or more to grow naturally by it；
S8. spray irrigation system is established, slope greening cultivated plant is automatically controlled according to temperature humidity and carries out spray maintenance；
S9. it runs and conserves.
2. a kind of hard side slope greening restoration method according to claim 1, it is characterised in that: in the step S4, respectively
Weight percentages of components composition are as follows: Red Sandstone 70%, carragheen 15%-17%, humus 4%-6%, plant ash 1-2%, then
Mix plain soil 8-10%.
3. a kind of hard side slope greening restoration method according to claim 2, it is characterised in that: in the step S4, change
After in good dose of incorporation red sand rock-soil layer, stack is formed after making its uniform mix；Watering, makes its moisture content reach 30%~40%；
It is covered, is macerated 2~3 days using cotton.
4. a kind of hard side slope greening restoration method according to claim 1, it is characterised in that: in the step S2, institute
Stating longitudinal pitch and horizontal spacing between anchor pole and anchor pole is 2-3m, rock-bolt length 5-6m.
5. a kind of hard side slope greening restoration method according to claim 1, it is characterised in that: in the step S3, phase
The lap width of adjacent galvanized wire mesh sheet is at least 10cm, and the mesh of the galvanized wire mesh sheet is 10cm × 10cm.
6. a kind of hard side slope greening restoration method according to claim 1, it is characterised in that: in the step S6, root
According to operation side soil or scar property, local climate condition, construction seasons, and various plant growth characteristics is combined to select root
It is flourishing herbaceous plant and Qiao, shrub, and species should be based on endemic plant；The seed of reply buying is living before grass seeds sowing
Property, purity are monitored, and should ensure that 6~9kg/hm of density of seed when grass seeds broadcasts sowing2。
7. a kind of hard side slope greening restoration method according to claim 1, it is characterised in that: in the step S8, build
Vertical spray irrigation system is included in the spaced many places tank in top of the slope area, for storing the rainwater collected, and uses automatic irrigation
System water supply, automatic sprinkling system are connect with flexible duct between the two with tank, and the automatic sprinkling system includes main confession
Control valve, the master of each control valve control automatic sprinkling system are set in water pipe, branch's water injection pipe and control system, main-supply
Water supplying pipe and branch's water injection pipe, the main-supply and branch's water injection pipe are equipped with spray head, the control system according to temperature and
Humidity Automatic Control spray head carries out spray maintenance.
8. a kind of hard side slope greening restoration method according to claim 1, it is characterised in that: on hard side slope surface also
Slope of rock mass is separated into several green by confluence ditch and classification platform equipped with several vertical interlaceds, the confluence ditch with classification platform
Change area, convenient for planting the spraying of raw substrate, the two sides of green belt are equipped with waterwall, and the bottom of slope is equipped with intercepting ditch, intercepting ditch
It is connected with confluence ditch, the top of the slope is equipped with pressure sheath, and pressure sheath pours integral knot with the waterwall top for being located at top layer
Structure.
9. a kind of hard side slope greening restoration method according to claim 1, it is characterised in that: in the step S9, apply
After the completion of work, spray irrigation system is run for the first time will fill in tank, kept the water yield of system to run in maximum rating, worked as profit
After wet body formation and volume reach the root zone volume for being enough to contain crop, results of regular determination soil moisture, and control valve or water storage
Pool water level controls spray irrigation system filling pipe water yield, and the humidity of gradient soil is made to keep 20~30%.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201910384331.2A CN110089353A (en) | 2019-05-09 | 2019-05-09 | A kind of hard side slope greening restoration method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201910384331.2A CN110089353A (en) | 2019-05-09 | 2019-05-09 | A kind of hard side slope greening restoration method |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN110089353A true CN110089353A (en) | 2019-08-06 |
Family
ID=67447428
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201910384331.2A Pending CN110089353A (en) | 2019-05-09 | 2019-05-09 | A kind of hard side slope greening restoration method |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN110089353A (en) |
Cited By (12)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110512628A (en) * | 2019-08-26 | 2019-11-29 | 中国水利水电科学研究院 | A kind of side slope ecological renovation method |
| CN110604038A (en) * | 2019-10-17 | 2019-12-24 | 林进国 | Ecological slope protection greening water supply system |
| CN110714469A (en) * | 2019-09-12 | 2020-01-21 | 中国一冶集团有限公司 | Red sandstone hard slope ecological greening system and construction method thereof |
| CN111887138A (en) * | 2020-08-31 | 2020-11-06 | 甘肃省科学院地质自然灾害防治研究所 | Water distribution method for intercepting type slope green plant irrigation |
| CN111887139A (en) * | 2020-08-31 | 2020-11-06 | 甘肃省科学院地质自然灾害防治研究所 | Automatic water supply irrigation method for controlling slope green plants |
| CN111990185A (en) * | 2020-08-31 | 2020-11-27 | 长江师范学院 | Rock slope ecological restoration system |
| CN113062332A (en) * | 2021-03-30 | 2021-07-02 | 广西北投交通养护科技集团有限公司 | Vegetation concrete ecological slope protection and automatic maintenance method |
| CN114215075A (en) * | 2021-11-10 | 2022-03-22 | 武汉景天园林有限公司 | Slope greening restoration method |
| CN115007633A (en) * | 2022-06-14 | 2022-09-06 | 贵州大学 | In-situ repair method for lead-zinc waste residue storage yard |
| CN115130163A (en) * | 2021-03-26 | 2022-09-30 | 安徽轩鸣新材料有限公司 | Mountain greening construction scheme making system, making method and construction method |
| CN116235659A (en) * | 2023-01-10 | 2023-06-09 | 陈广宇 | River side slope soil fixing device and soil fixing method |
| CN116856432A (en) * | 2023-05-26 | 2023-10-10 | 海南大学 | Ecological slope protection system under combined action of vegetation and microorganism and construction method |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102763535A (en) * | 2012-06-26 | 2012-11-07 | 巫少芬 | Side slope greening method |
| CN102992826A (en) * | 2012-11-20 | 2013-03-27 | 厦门日懋城建园林建设有限公司 | New improved substrate of slope, preparation method and application thereof |
| CN103641648A (en) * | 2013-12-16 | 2014-03-19 | 北京东方园林股份有限公司 | Sludge plant growth substrate and side slope sludge soil replacement greening method |
| CN104805845A (en) * | 2015-04-21 | 2015-07-29 | 安徽农业大学 | Flexible slope protection method for soft sandstone natural side slope |
-
2019
- 2019-05-09 CN CN201910384331.2A patent/CN110089353A/en active Pending
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102763535A (en) * | 2012-06-26 | 2012-11-07 | 巫少芬 | Side slope greening method |
| CN102992826A (en) * | 2012-11-20 | 2013-03-27 | 厦门日懋城建园林建设有限公司 | New improved substrate of slope, preparation method and application thereof |
| CN103641648A (en) * | 2013-12-16 | 2014-03-19 | 北京东方园林股份有限公司 | Sludge plant growth substrate and side slope sludge soil replacement greening method |
| CN104805845A (en) * | 2015-04-21 | 2015-07-29 | 安徽农业大学 | Flexible slope protection method for soft sandstone natural side slope |
Cited By (20)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110512628A (en) * | 2019-08-26 | 2019-11-29 | 中国水利水电科学研究院 | A kind of side slope ecological renovation method |
| CN110714469A (en) * | 2019-09-12 | 2020-01-21 | 中国一冶集团有限公司 | Red sandstone hard slope ecological greening system and construction method thereof |
| CN110604038B (en) * | 2019-10-17 | 2021-07-16 | 绍兴市魏达机械有限公司 | Ecological slope protection greening water supply system |
| CN110604038A (en) * | 2019-10-17 | 2019-12-24 | 林进国 | Ecological slope protection greening water supply system |
| CN111990185B (en) * | 2020-08-31 | 2022-09-23 | 长江师范学院 | Rock slope ecological remediation system |
| CN111887138B (en) * | 2020-08-31 | 2022-11-01 | 甘肃省科学院地质自然灾害防治研究所 | Water distribution method for intercepting type slope green plant irrigation |
| CN111887139A (en) * | 2020-08-31 | 2020-11-06 | 甘肃省科学院地质自然灾害防治研究所 | Automatic water supply irrigation method for controlling slope green plants |
| CN111990185A (en) * | 2020-08-31 | 2020-11-27 | 长江师范学院 | Rock slope ecological restoration system |
| CN115152595B (en) * | 2020-08-31 | 2023-10-31 | 甘肃省科学院地质自然灾害防治研究所 | Uniform water distribution type side slope green planting system |
| CN111887138A (en) * | 2020-08-31 | 2020-11-06 | 甘肃省科学院地质自然灾害防治研究所 | Water distribution method for intercepting type slope green plant irrigation |
| CN115152595A (en) * | 2020-08-31 | 2022-10-11 | 甘肃省科学院地质自然灾害防治研究所 | Uniform water distribution type slope green planting system |
| CN115130163A (en) * | 2021-03-26 | 2022-09-30 | 安徽轩鸣新材料有限公司 | Mountain greening construction scheme making system, making method and construction method |
| CN113062332A (en) * | 2021-03-30 | 2021-07-02 | 广西北投交通养护科技集团有限公司 | Vegetation concrete ecological slope protection and automatic maintenance method |
| CN114215075A (en) * | 2021-11-10 | 2022-03-22 | 武汉景天园林有限公司 | Slope greening restoration method |
| CN115007633B (en) * | 2022-06-14 | 2023-03-14 | 贵州大学 | In-situ repair method for lead-zinc waste residue storage yard |
| CN115007633A (en) * | 2022-06-14 | 2022-09-06 | 贵州大学 | In-situ repair method for lead-zinc waste residue storage yard |
| US11858018B1 (en) | 2022-06-14 | 2024-01-02 | Guizhou University | In-situ remediation method for lead-zinc slag dump |
| CN116235659A (en) * | 2023-01-10 | 2023-06-09 | 陈广宇 | River side slope soil fixing device and soil fixing method |
| CN116235659B (en) * | 2023-01-10 | 2024-06-14 | 陈广宇 | River side slope soil fixing device and soil fixing method |
| CN116856432A (en) * | 2023-05-26 | 2023-10-10 | 海南大学 | Ecological slope protection system under combined action of vegetation and microorganism and construction method |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN110089353A (en) | A kind of hard side slope greening restoration method | |
| CN104255280B (en) | A kind of high precipitous rock slope vegetation implantation methods | |
| CN103931371B (en) | A kind of biological control method of rock side-slope | |
| CN101904261B (en) | Method for restoring side slope ecology by adopting AB (Acinetobacter baumannii) bacterium plant growing bags | |
| WO2015101295A1 (en) | Water and soil conservation and ecological restoration method of high and steep, abandoned slag piles at high elevation with large temperature differential in dry, hot valley | |
| CN103609303B (en) | A kind of hillock near-nature forest ecological system reconstruction method | |
| CN105981539A (en) | Side slope greening method | |
| CN208266847U (en) | Quickly repair structure in Gullied suitable for Canal in Loess Area | |
| CN101507391B (en) | Rock slope-surface ecology treatment method | |
| CN112064655A (en) | Rapid restoration and greening method for limestone bare high and steep slope | |
| CN105340507B (en) | Sedum lineare roof greening planting method and roof greening planting structure | |
| CN108547307A (en) | Protecting slope ecology method based on artificial loam | |
| CN108476649A (en) | A kind of gardens abrupt slope plant landscape method | |
| CN105210770B (en) | Dust storm forward position Desert Regions sacsaoul Ecology method of forestation | |
| CN109392582A (en) | A kind of massif slope surface implantation methods | |
| CN110447448A (en) | A kind of beach saline land garden landscape plant cultivation method | |
| CN106576474A (en) | Efficient ecological restoration method for slope in South China | |
| CN109328808A (en) | A kind of the Northwest's ecological treatment of slope method | |
| CN110506554A (en) | A kind of Landscape Construction method | |
| CN210946834U (en) | Immersed net type ecological slope protection structure for mine restoration | |
| CN1122183A (en) | Sand land mulching film cultivation method for rice | |
| CN109328805A (en) | A kind of Rocky Desertification Region ecological treatment of slope method | |
| CN106718607B (en) | A method of directly repairing metal abandoned mine slag muck field using wet-land pine tree container seedling | |
| CN111512840A (en) | Moss plant block and method for establishing ecology by using moss plant block on concrete surface | |
| CN101457525B (en) | Loess slope heavy layer flaking diseases treatment method |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| RJ01 | Rejection of invention patent application after publication |
Application publication date: 20190806 |
|
| RJ01 | Rejection of invention patent application after publication |