CN109588190A - A kind of Sphaeroma destroyed area Mangrove restoration method - Google Patents
A kind of Sphaeroma destroyed area Mangrove restoration method Download PDFInfo
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- CN109588190A CN109588190A CN201811555383.3A CN201811555383A CN109588190A CN 109588190 A CN109588190 A CN 109588190A CN 201811555383 A CN201811555383 A CN 201811555383A CN 109588190 A CN109588190 A CN 109588190A
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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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- 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
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Abstract
The invention belongs to ecological protection technical fields, and in particular to Sphaeroma is removed in a kind of restoration methods of Sphaeroma destroyed area mangrove, including (1)；(2) site preparation；(3) it plants；(4) it reseeds and manages and protects.Sphaeroma destroyed area internal cause Sphaeroma is lived in caves, and to make mangrove in destroyed area repair difficulty big for the problems such as destroying mangrove, severe water and soil erosion, hypsography low-lying.Using this patent method, the recovery because of Sphaeroma destroyed area mangrove ecosystem can be successfully repaired.
Description
Technical field
The invention belongs to ecological protection technical fields, and in particular to a kind of restoration methods of Sphaeroma destroyed area mangrove
Background technique
Mangrove (Mangrove), which refers to, is grown in the torrid zone, subtropical zone seashore intertidal zone top, is flooded by the leaching of periodical tidewater, with
The woody biocoene of tidal beach wetland of evergreen shrubs or arbor composition based on mangrove.Mangrove is in land and ocean
Intermediate zone is ecologically criticalarea and the most sensitive region of littoral zone ecology fragility of tropical and subtropical zone littoral zone.The torrid zone and Asia heat
The mangrove biocoene of band is the basis to form mangrove ecosystem high productivity and rich biodiversity, the ecosystem
Millions of necessary goods and materials and service can be provided for the mankind.It has the function of flood control, wave resistance, storm guard, bank protection etc., is not
The coastal green screen in the alternative road head.The unique ecological environment of mangrove, which also provides for various biologies, inhabites and breeding farm
Institute, many is in imminent danger and protected species.
The ecological functions Huge value of mangrove, but pathophorous muddy wasteland was considered to be only in the past.Due to
Its ecological value is seriously underestimated, and the mangrove in the whole world is caused to be destroyed at an amazing speed.Mangrove once degenerates, sea
The water front resident that nearby height relies on mangrove ecosystem offer service will face many predicaments.In recent decades due to the mankind
Activity, almost all of mangrove suffered from serious loss.Mangrove is taken over for use by various industries, including agricultural land is such as
Rice field, bio-fuel planting, the shrimp pool is such as supported in city and residential land exploitation, aquaculture, wherein the mistake of the forest reserves
Degree exploitation is most important destruction and threat of the mankind to Mangrove resource.In addition, marine oil overflow, Petroleum Production, family and work
The heavy metal pollution of industry waste water, eutrophication, pesticide, agricultural and urban runoff flow into the toxic chemical substance of mangrove, fresh water
Diversion irrigation and land reclamation etc. are produced serious and are widely negatively affected to mangrove.
China's mangrove area also sharply declines, and falls sharply 68.7% from area at 20th century 50 to the beginning of the nineties.It is close in the past
In 50 years time, the main mangrove area in China --- Hainan Dong Zhaigang has nearly 50% natural mangrove to be destroyed.It is especially close
Several years, mangrove was dead in flakes successively in the national nature reserve Dong Zhaigang of Hainan, and Beibu Bay, guangxi mangrove is a large amount of withered and yellow dying
Trend still expanding.The mangrove about 100hm of the port Dong Zhai decline in recent years2(stockaded village Zhan Dong port mangrove 8%), wherein withered face
Product reaches 40hm2More than.These decline group's majority hairs destroy and live in caves movablely now with Sphaeroma (Sphaeroma sp.)
Side, while the phenomenon that Drilling mangrove root a large amount of there is also Sphaeroma, such as at Bruguiera conjugata (Bruguiera gymnorrhiza)
In group, Sphaeroma concentrates its tabular root of causing harm, and forms intensive hole, so that the root system of mangrove is damaged, cause full wafer
Forest is withered.Negative effect caused by Sphaeroma is as follows: 1. under the impact of stormy waves, due to wooden at aggrieved mangrove plant rhizome
Portion is eaten hollow, eats into disconnected and lodge dead；2. being made since mangrove plant death weakens the effect of its rhizome fixation marshland mud
At Sphaeroma destroyed area under the impact of stormy waves severe water and soil erosion, be in significant low-lying land gesture；3. the mangrove branch for lodging dead
Dry and its aerial root can become the new habitat of Sphaeroma, accelerate the breeding of Sphaeroma, but such as carry out being isolated to it controllable
Make its further sprawling；4. removing withered mangrove tabular root is the work for needing a large amount of human and material resources and financial resources, clearly
Cause to carry out the new talent of mangrove ecosystem recovery again by moth erosion death, ecosystem in Sphaeroma destroyed area except being not thorough
System restores the problems such as time-consuming, difficulty is big and capital investment is huge.Therefore, the recovery side of Sphaeroma destroyed area mangrove
The establishment of method and the relevant technologies has very important effect.
Summary of the invention
The technical problem to be solved in the present invention is to provide a kind of restoration methods of Sphaeroma destroyed area mangrove.It removes broken
After the Sphaeroma of error area, which is re-used, by a kind of natural selection in such a way that artificial growth combines, i.e.,
Restore original ecological environment, hydrologic condition, the region mangrove ecosystem is enable to restore.
In order to solve the above technical problems, the technical solution used in the present invention is:
(1) the aerial root of intensive hole, trunk will be formed by a large amount of Drillings of Sphaeroma in Sphaeroma destroyed area death mangrove
It all removes, and destroys by fire, the aerial root of the dead mangrove of intensive hole will not formed by a large amount of Drillings of Sphaeroma, trunk excavates
Bait of the lodging as Sphaeroma Burst Regions, is trapped in the region 40 ± 10 days after machine is dug out, Sphaeroma Drilling to be formed it is close
It removes, and destroys by fire after collection hole, until carrying out subsequent step after launched timber does not re-form dense holes hole；
(2) control the area periphery discharge of pollutant sources, and continuously monitor the region mangrove healthy growth region water and
Tidal level；
(3), by earth work measure, the lowered zones destroyed with the padded Sphaeroma of shale soil, edge is parallel to coastline side
To the strip and block or terrace type beach face changed with continuous elevation gradient is constructed, for planting mangrove, plantation beach face is kept
Height is higher than 0.2 ± 0.05 to 0.5 ± 0.05m of mean sea level；
(4) tidal creek in building afforestation region；
(5), along beach face difference elevation gradient, planting method is transplanted using sapling, mangrove species is selected successively to plant succession
Early period tree species, mid-stage succession tree species and succession species later, planted by specified spacing in the rows；
(6) reproducing area is reseeded and is managed and protected within continuous 2 years or more after afforestation.
Wherein (1) middle dead mangrove is divided into step: being destroyed by Sphaeroma and does not destroy two classes by Sphaeroma.The former is to be rolled into a ball
The a large amount of Drillings of beach louse form the aerial root of intensive hole, trunk etc.；The latter is not form intensive hole by a large amount of Drillings of Sphaeroma
Aerial root, the trunk of dead mangrove etc..Wherein, as the bait of Sphaeroma Burst Regions after the latter uses excavator to dig out, it is detained
It collects and destroys by fire after 40 ± 10 days in the region, until after launched timber does not re-form dense holes hole, progress subsequent step.
Wherein step (2) in when continuously monitoring, water, tidal level monitoring should be at 1 month or more, to determine level-one
Tidal creek 2, the width of second level tidal creek 3, depth and high tide level 5, low tide 6 (referring to Fig. 1 b, Fig. 2 b and Fig. 3).
The wherein step lowered zones that (3) middle Sphaeroma destroys, have as removed the aerial root of dead mangrove, the group of trunk
Beach louse destroyed area.
Wherein step is (4) in the construction process on the strip and block padded according to gesture of the direction towards seawater or terrace type beach face
The width of plantation mangrove, strip and block or terrace type beach face 1 is 2 to 3m, and opening in afforestation region in the left and right sides of beach face has tide
Nighttide variation level-one tidal creek 2, width be 4 to 5m, and between beach face be arranged perpendicular to beach face width be 0.4 to 0.6m, depth
For 0.2 to 0.3m second level tidal creek 3 (referring to Fig. 1 a, 1b and 2a, 2b).
Wherein (5) the middle sapling used transplants planting method to step: being specifically that the mangrove sapling of mangrove 50 to 70cm is put into digging
Earthing after seedling cultivation is filled and led up into compacting in the plantation hole dug.
The selection of mangrove: it to be integrated according to the tree species type and soil regime of the destroyed area health mangrove
Consider.Plantation sequence should be according to elevation gradient from low to high, after successively planting tree species succession early period, mid-stage succession tree species and succession
Phase tree species.Preferably, succession front end tree species can be such as Avicennia marina (Avicennia marina (Forsk.)
Vierh.hailanci).Avicennia marina is distributed in seashore outer most edge, and this kind of resistance to water logging ability of plant is strong, is suitable as succession early period
Tree species.The succession middle-end tree species can be selected from by halogen fern (Acrostichum aureum Linn.), Aegiceras corniculatum
(Aegiceras corniculatum (L) Blanco), Rhizophora stylosa (Rhizophora stylosa), Hainan Hai Sang
(Sonneratia hainanensisKO, E.Y.Chen et W.Y. Chen), Hai Sang (Sonneratiacaseolaris
(L.)), pagatpat (Sonneratia apetala), olive Lee (Lumnitzera racemosa Willd), red olive Lee
(Lumnitzera littorea (Jack) Voigt), positive mangrove (Rhizophora apiculata Blume), autumn eggplant
The group of (Kandelia candel (Linn.) Druce/Kandelia obovata) composition.These tree species are generally grown in beach
The shale beach that middle part water and soil is easy to run off, is suitable as mid-stage succession tree species.Succession rear end tree species can be selected from by Bruguiera conjugata
(Bruguiera gymnorrhiza (L.) Poir.), Hai Lian (Bruguiera sexangula), ceriops tagal (Ceriops
Tagal (perr.) C.B.Rob.), sea paint (Excoecaria agallocha Linn.), looking glass tree (Heritiera
Littoralis Dryand.), Lao Shu le (Acanthus ilicifoliusL.), the yellow rose of Sharon (Hibiscus tiliaceus
Linn.), Hai Mangguo (Cerbera manghas), Indian beech (Pongamia pinnata (L.) Pierre) and populnea
The group of (Thespesia populnea (L.) Soland.ex Correa) composition.These tree species can be grown in mangrove inner edge
On (nearly land side) or high tide level beach, it is suitable as succession species later.The some of the above-mentioned tree species in part are shown in Fig. 3
Legend.As shown in figure 3, serial community early period 10, mid-term are successively planted in the direction along tide rises (such as seawater) from low to high
Serial community 11 and later period serial community 12.
The determination of mangrove on the spot spacing in the rows: after determining mangrove Planting Patterns, the big beach face spacing in the rows of stormy waves is 1.0 to 1.5m ×
1.0 to 1.5m, the small beach face spacing in the rows of stormy waves is 1.5 to 2.0m × 1.5 to 2.0m.
In the present invention, using biggish spacing in the rows, it is therefore an objective to follow naturally, making the Nature competing according to habitat conditions progress object
Natural selection enables that local habitat conditions growing plants is suitble to grow between the mangrove of big spacing in the rows, be mangrove self is extensive
The performance of reactivation power reserves enough spaces.
In the present invention, the side that do not plant directly using plumular axis is gnawed in order to avoid zoobenthos such as Sphaeroma, fiddler crabs
Method restores the mangrove of Sphaeroma destroyed area, but sapling is used to transplant planting method.The seedling of selection is preferably no disease and pests harm
Healthy nursery stock, the height of seedling of sapling is 50 to 70cm (for example, 50,55,60,65 or 70cm).In addition, being cut before transplanting
The root system of nutrient bag is pierced through, then nutrient bag need to protect mangrove root and conserve 15-25 days.The length, width and height of mangrove plantation hole are 0.2
To 0.3m, the mangrove sapling that nutrient bag is cut after specifically conserving 50 to 70cm root system 15-25 days is put into the kind excavated
Shale earthen backfill plantation hole will be utilized by planting after seedling cultivation in hole.Length, width and the height of plantation hole are not particularly limited, example
It such as can be 0.2m to 0.3m, no more than 10 ± 5cm of Soil Surrounding surface after the compacting of seedling wood height to earth up.
Relative to existing Mangrove restoration method, advantages of the present invention is as follows:
1, waste will not may be implemented as the bait of Sphaeroma Burst Regions by the aerial root for the dead mangrove that chisel is bitten, trunk
Using and reduce Mangrove restoration workload and difficulty of construction.
2, selection sapling transplanting planting method is easy to operate, can avoid gnawing for the zoobenthos such as Sphaeroma and fiddler crab, right and wrong
Often effective Mangrove restoration method, the survival rate of mangrove is up to 90% or more.
3, by determining plantation tree species type after mangrove autecology on the spot and synecology investigation, monitoring,
It is control with synecology under natural conditions, the selection of tree species is carried out according to natural growthing condition.And holding 1 to 2m is very big
Mangrove on the spot spacing in the rows, it is therefore an objective to needed for selecting itself by the capacity of self-regulation and self organization ability of the nature ecosystem
Number of plant there are the spaces of recovery.I.e. to meet restoration of the ecosystem theory as principle, nature is imitated, regarding nature asthis is aided with people
Work measure makes destroyed area develop to orderly direction.
4, the method for the present invention is simple, strong operability, high survival rate, be suitable for it is a wide range of promote, have it is good it is economical,
Society and ecological benefits.
Detailed description of the invention
Fig. 1 a is the schematic top plan view of mangrove strip and block beach face and tidal creek construction.
Fig. 1 b is the diagrammatic cross-section of mangrove strip and block beach face and tidal creek construction.
Fig. 2 a is the schematic top plan view of mangrove terrace type beach face and tidal creek construction.
Fig. 2 b is the diagrammatic cross-section of mangrove terrace type beach face.
Fig. 3 is Mangrove Communities anthropogenic sere schematic diagram, and which show the legends of part mangrove tree species.
Specific embodiment
The present invention can be more clearly understood by the way that specific embodiments of the present invention are given below, it is clear that embodiment is only
It is only a part of the embodiments of the present invention, is not whole.Based on the embodiment of the present invention, those of ordinary skill in the art are not having
Every other embodiment obtained under the premise of creative work is made, protection scope of the present invention is belonged to.
1. the preparation of early period:
1.1 carry out mangrove autecology and synecology investigation, hydrology and water ecological environment pollution monitoring
Influence of the increase of change or pressure factor that the hydrology is assessed on Research foundation to Mangrove restoration.With Hainan Dong Zhaigang mangrove
Mangrove ecosystem is eliminated or is reduced in control area periphery discharge of pollutant sources measure for implementing for nature reserve area
Pressure factor, including shut down, move fowl and livestock farm, such as pig farm and salt water duck farm；Remove violation eating and drinking establishment；Build village
Town sewage treatment plant and mating pipe network eliminate mangrove section sanitary sewage etc.；It carries out moving back the pool also woods in protection zone；It is protecting
Dirt preventing facility, agricultural non-point source pollution problem caused by control chemical fertilizer, pesticide, waste material etc. are built in area, agricultural land, periphery；And it is continuous
Monitor the region mangrove healthy growth region water, tidal level 1 month or more, determine the hydrology requirement of mangrove；Really
The halodrymium composition and soil types in the fixed region.
1.2 restore the original state of mud bank in Sphaeroma destroyed area using excavator and bull-dozer removing are all, and will not
The bait of the aerial root, trunk of the dead mangrove of intensive hole as Sphaeroma Burst Regions is formed by a large amount of Drillings of Sphaeroma, it is stagnant
It stays in the region to collect and destroy by fire after 40 ± 10 days, until carrying out subsequent step after launched timber does not re-form dense holes hole；
1.3 carry out earth work measure using bull-dozer and ream grab, and the padded Sphaeroma of backfill mud soil destroys low
Hollow region forms the strip and block or ladder with the variation of continuous elevation gradient according to the lowered zones that landform, topography destroy Sphaeroma
The width of field shape beach face, strip and block or terrace type beach face is 2 to 3m, restores and establish normal hydrologic condition, keeps plantation beach
Face is in 0.2 ± 0.05 to 0.5 ± 0.05m of anomaly mean level of the sea；
1.4 in the construction process in the direction towards seawater according to the padded strip and block of gesture or terrace type beach face left and right sides (rule
Fixed front side is seawater, and rear side is original healthy mangrove), opening the width with tidal fluctuations in afforestation region is 4 to 5m level-one
Tidal creek 2, and the second level tidal creek 3 being connected with level-one tidal creek 2 is opened on beach face, width are 0.4 to 0.6m, depth be 0.2 to
0.3m, make mangrove planting area in the raw under tidal flow state.
On strip and block beach face shown in Fig. 1 a and 1b along the direction far from coastline 7, construct level-one tidal creek 2 and and
The second level tidal creek 3 that level-one tidal creek 2 is connected to plants mangrove 4 in planting area.The height of the second groove 3 of extreme higher position can be low
Low tide 6 can be higher than in the height of high tide level 5, the second groove 3 of extreme lower position.Extreme higher position can also remain with can be just
The mangrove being frequently grown.
Similarly, on the terrace type beach face shown in Fig. 2 a and 2b along the direction far from coastline 7, level-one tidal creek 2 is constructed
And the second level tidal creek 3 being connected to level-one tidal creek 2, mangrove 4 is planted in planting area.The height of the second groove 3 of extreme higher position
High tide level 5 can be lower than, the height of the second groove 3 of extreme lower position can be higher than low tide 6.Likewise, extreme higher position is also protected
There are the mangroves for capableing of normal growth.
2. the plantation of mangrove
The selection of 2.1 tree species
The selection of mangrove: it to be integrated according to the tree species type and soil regime of the destroyed area health mangrove
Consider.Plantation sequence should be according to elevation gradient from low to high, after successively planting tree species succession early period, mid-stage succession tree species and succession
Phase tree species (as shown in Figure 3).In specific embodiment, bones of the dead can be successively planted from low to high on the direction of tide rises
Earth, halogen fern, Aegiceras corniculatum, Rhizophora stylosa, positive mangrove, autumn eggplant, Bruguiera conjugata, Hai Lian, ceriops tagal, looking glass tree and populnea.
The determination of 2.2 mangroves on the spot spacing in the rows
After determining mangrove Planting Patterns, in the big beach face mangrove of stormy waves, on the spot spacing in the rows is 1.0 to 1.5m × 1.0 to 1.5m,
On the spot spacing in the rows is 1.5 to 2.0m × 1.5 to 2.0m to the small beach face mangrove of stormy waves.
2.3 kinds are planted and are managed and protected
1. the afforestation season:
Mangrove implantation time is 5 to August part.
2. planting patterns:
In order to avoid the method that do not planted directly using plumular axis of gnawing of the zoobenthos such as Sphaeroma, fiddler crab restores group's water
The mangrove of lice destroyed area, but sapling is used to transplant planting method.Healthy nursery stock of the seedling selected for no disease and pests harm, height of seedling
50 to 70cm, the root system for piercing through nutrient bag is cut before transplanting, then nutrient bag need to protect mangrove root and conserve 15-25 days.It is red
The length, width and height in tree planting hole are 0.2 to 0.3m, cut nutrient bag after specifically conserving 50 to 70cm root system 15-25 days
Mangrove sapling, which is put into the plantation hole excavated, will utilize shale earthen backfill plantation hole, seedling wood height to earth up pressure after seedling cultivation
No more than 10 ± 5cm of Soil Surrounding surface after reality.
3. reinforcing maintenance and management:
Reinforce periodically carrying out after-culture, righting lodging sapling, cleaning rubbish incidental to reproducing area maintenance and management after afforestation,
It answers continuous 2 years or more.
3. Mangrove restoration effect
By changing Sphaeroma Burst Regions Mangrove Habitats, survival rate is covered up to 90% or more after the mangrove planted 2 years
40% or more capping product.
Wherein, a survival rate (November) when 3 months full after planting for the first time is united before no plantation of supplement for the first time
Meter, calculation formula: for the first time plant after survive sum/for the first time plantation sum × 100%；Survival rate is mended in second year June in 2 years
(i.e. September part) counts when filling completely 3 months after plantation, calculation formula: sum/(plantation number+supplement kind for the first time is survived after supplement plantation
Plant number) × 100%.
Claims (6)
1. a kind of restoration methods of Sphaeroma destroyed area mangrove, it is characterised in that the following steps are included:
(1) will to form the aerial root of intensive hole, trunk by a large amount of Drillings of Sphaeroma in Sphaeroma destroyed area death mangrove complete
Portion removes, and destroys by fire, will not formed aerial root, the trunk excavator of the dead mangrove of intensive hole by a large amount of Drillings of Sphaeroma
Bait after digging out as Sphaeroma Burst Regions, is trapped in the region 40 ± 10 days, the intensive hole of Sphaeroma Drilling to be formed
After remove, and destroy by fire, until after launched timber does not re-form dense holes hole, progress subsequent step；
(2) lowered zones destroyed with the padded Sphaeroma of shale soil are constructed along coastline direction is parallel to continuous elevation ladder
The width of the beach face of the strip and block or terrace type beach face of degree variation, strip and block or terrace type beach face 1 is 0.6 to 1.4m, keeps kind
It plants Mudflat altitude and is higher than 0.2 ± 0.05 to 0.5 ± 0.05m of mean sea level, open in afforestation region and have in the left and right sides of beach face
There is the tidal creek of tidal fluctuations, tidal creek width is 4 to 5m, and setting is 0.4 to 0.6m perpendicular to the width of beach face between beach face, depth
For 0.2 to 0.3m small tidal creek；
(3) from low to high along Tidal flat gradient, planting method is transplanted using sapling, mangrove species is selected successively to plant succession
Front end tree species, succession middle-end tree species and succession rear end tree species, are planted by 1.0 to 2.0m × 1.0 to 2.0m spacing in the rows；
(4) reproducing area is reseeded and is managed and protected within continuous 2 year or more after afforestation.
2. the restoration methods of Sphaeroma destroyed area mangrove according to claim 1, it is characterised in that: the step is (2)
Middle tidal creek and small tidal creek, appropriate depth can continuously monitor the region mangrove healthy growth region by one month or more
Water and tidal level determine.
3. the restoration methods of Sphaeroma destroyed area mangrove according to claim 1, it is characterised in that: the step
(3) in sapling transplant planting method, specifically by the mangrove sapling of height of seedling 50 to 70cm be put into the length, width and height excavated be 0.2 to
In the plantation hole of 0.3m, earthing after seedling cultivation is filled and led up into compacting, utilizes shale earthen backfill plantation hole, seedling wood height to earth up pressure
No more than 10 ± 5cm of Soil Surrounding surface after reality.
4. the restoration methods of Sphaeroma destroyed area mangrove according to claim 1, it is characterised in that: the step
(3) mangrove is selected in, to be comprehensively considered according to the tree species type and soil regime of the destroyed area health mangrove.
5. the restoration methods of Sphaeroma destroyed area mangrove according to claim 1, it is characterised in that: the step
(3) Mangrove Communities anthropogenic sere in is successively planted tree species succession early period from low to high specially on tide rises direction, is drilled
For mid-term tree species and succession species later；
It is further preferred that tree species succession early period are Avicennia marina, the mid-stage succession tree species are selected from by halogen fern, Aegiceras corniculatum, red
The group that Hai Lan, Hainan Hai Sang, Hai Sang, pagatpat, olive Lee, red olive Lee, positive mangrove, autumn eggplant form；The succession species later
Selected from what is be made of Bruguiera conjugata, Hai Lian, ceriops tagal, book paint, looking glass tree, old mouse le, the yellow rose of Sharon, Hai Mangguo, Indian beech and populnea
Group；Most preferably, Avicennia marina, halogen fern, Aegiceras corniculatum, Rhizophora stylosa, at prime is successively planted from low to high on tide rises direction
Tree, autumn eggplant, Bruguiera conjugata, Hai Lian, ceriops tagal, looking glass tree and populnea.
6. the restoration methods of Sphaeroma destroyed area mangrove according to claim 1, it is characterised in that: the step
(3) the big beach face spacing in the rows of the determination of spacing in the rows in, specially stormy waves is 1.0 to 1.5m × 1.0 to 1.5m, the small beach face spacing in the rows of stormy waves
It is 1.5 to 2.0m × 1.5 to 2.0m.
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| CN111616118A (en) * | 2020-05-15 | 2020-09-04 | 北京航空航天大学 | Trapping, killing and killing method for preventing and controlling water lice |
| CN112715125A (en) * | 2020-12-29 | 2021-04-30 | 中国林业科学研究院热带林业研究所 | Method for transforming coastal culture pond into mangrove forest nursery |
| CN113016480A (en) * | 2021-03-04 | 2021-06-25 | 中国科学院生态环境研究中心 | Plant configuration method for restoring mangrove wetland |
| CN114885731A (en) * | 2022-05-18 | 2022-08-12 | 中国林业科学研究院热带林业研究所 | Vegetation recovery method for typhoon-damaged mangrove forest land |
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| CN113016480A (en) * | 2021-03-04 | 2021-06-25 | 中国科学院生态环境研究中心 | Plant configuration method for restoring mangrove wetland |
| CN114885731A (en) * | 2022-05-18 | 2022-08-12 | 中国林业科学研究院热带林业研究所 | Vegetation recovery method for typhoon-damaged mangrove forest land |
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