CN105493828B - A kind of method of deserted mountain quick recovering vegetation - Google Patents
A kind of method of deserted mountain quick recovering vegetation Download PDFInfo
- Publication number
- CN105493828B CN105493828B CN201510899522.4A CN201510899522A CN105493828B CN 105493828 B CN105493828 B CN 105493828B CN 201510899522 A CN201510899522 A CN 201510899522A CN 105493828 B CN105493828 B CN 105493828B
- Authority
- CN
- China
- Prior art keywords
- patch
- arbor
- plants
- species
- plant
- 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.)
- Active
Links
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
- Y02A90/00—Technologies having an indirect contribution to adaptation to climate change
- Y02A90/40—Monitoring or fighting invasive species
Abstract
A kind of method of deserted mountain quick recovering vegetation of the present invention, comprises the following steps：A. the natural forests of locality are found；B. with choosing sample and it is divided into the m of the m of size 5 × 5 patch；Investigate the common arbor in species, Individual Size and the various patch of each patch implants；C. the m of mountain waste to be restored division size 5 m × 5 grid, the type of each patch on the clear and definite deserted mountain of patch of natural forests is compareed；D. different types of plant is planted in different patch；The floristics of each patch plantation determines according to the natural forests advantage group of field investigation；E. after-culture is carried out to the seedlings or saplings of death after transplanting 23 years；After plant 6 years, the plant taller and bigger to individual is carried out cutting down branch, and space is provided for other species growths；Species non-indigenous are cut selectively, avoid alien species from destroying.It is of the invention economical, conveniently, the drawbacks of overcoming artificial forest or single Planting Patterns, the natural renovation and bio-diversity conservation for realizing forest.
Description
Technical field
The present invention relates to a kind of quick recovery method of vegetation, more particularly, to a kind of side of deserted mountain quick recovering vegetation
Method.
Background technology
Deserted mountain is very common caused by mankind's felling or forest fire, causes soil erosion, destroys woodland scenery, infringement
Economic interests, it is unfavorable for biodiversity conservation, the production and life to the mankind adversely affect.And traditional revegetation
Method uses artificial growth more, and the species planted are excessively single, pure forest are commonly formed, bio-diversity is low, survival rate of seedling
It is not high；The method of plantation uses hole tray method more, causes the distribution of species to present and is uniformly distributed, rather than natural random distribution.
The content of the invention
The technical problems to be solved by the invention are to provide economical, conveniently, are easy to forest natural renovation and bio-diversity
A kind of method of deserted mountain quick recovering vegetation of protection.
In order to solve the above technical problems, the present invention comprises the following steps：
A. local natural forests are found according to deserted mountain location；
B. size and habitat are chosen in step and sample that the deserted mountain that need to recover is basically identical, be divided into by the sample
The m of the m of size 5 × 5 patch is simultaneously distinguished with gap patches, woods window-mature forest transition patch and mature forest patch；Afterwards, investigate
Each common arbor in the species of patch implants, Individual Size, quantity and various patch；
C. on the mountain waste recovered is needed, the m of division size 5 m × 5 grid, the patch for compareing natural forests is clearly waste
The type of each patch on mountain；
D. different types of plant is planted in different patch, wherein gap patches plant 10 ~ 16 plants of arbor seedling；Woods window-
Mature forest transition patch plants 8 ~ 10 plants of arbor seedling and 8 ~ 10 plants of arbor treelets；Ripe patch plants 20 ~ 30 plants of arbor treelets；
The floristics of each patch plantation determines according to the natural forests advantage group of field investigation；
E. after-culture is carried out to dead seedlings or saplings after transplanting 2-3；After plant 6 years, the plant taller and bigger to individual enters
Row cuts down branch, and space is provided for other species growths；Species non-indigenous are cut selectively, avoid alien species from destroying.
It is of the invention economical, conveniently, it is easy to the natural renovation and bio-diversity conservation of forest.
Further, the gap patches basis for estimation is dead and dying trees in patch be present, is grubbed up, and has substantial amounts of Qiao in patch
Wooden seedling, the mean stand height of arbor less than sample mean stand height 1/4, patch canopy density are less than 15%；The mature forest patch is sentenced
Disconnected foundation is that individual is mostly adult in patch, lacks seedling and treelet, the mean stand height of arbor mean stand height higher than sample
3/4, patch canopy density be higher than 60%；Between gap patches and mature forest patch for woods window-mature forest transition patch.
Method carries out patch species division to staff according to this, and its subsequent operation is more directly perceived, efficient；Be remarkably improved vegetation survival rate and
Diversity.
Further, the seedling of selection is 2-3 annual plants, highly in 1.2 below m；Treelet is 6-10 annual plants,
Height is in 1-3m or so.The arbor seedling or arbor treelet of corresponding plantation in patch, adaptation habitat ability is strong, survival rate is high.
Brief description of the drawings
Fig. 1 is the flow chart of the present invention；
Fig. 2 is the patch division schematic diagram of the present invention；LC is gap patches, and GD is woods window-mature forest transition patch, and CS is
Mature forest patch.
Embodiment
The present invention is further illustrated below in conjunction with the accompanying drawings.
The present invention comprises the following steps：
A. local natural forests are found according to deserted mountain location；
B. size and habitat are chosen in step and sample that the deserted mountain that need to recover is basically identical, be divided into by the sample
The m of the m of size 5 × 5 patch is simultaneously distinguished with gap patches, woods window-mature forest transition patch and mature forest patch；Afterwards, investigate
Each common arbor in the species of patch implants, Individual Size and various patch；
C. on the mountain waste recovered is needed, the m of division size 5 m × 5 grid, the patch for compareing natural forests is clearly waste
The type of each patch on mountain；
D. different types of plant is planted in different patch, wherein gap patches plant 10 ~ 16 plants of arbor seedling；Woods window-
Mature forest transition patch plants 8 ~ 10 plants of arbor seedling and 8 ~ 10 plants of arbor treelets；Ripe patch plants 20 ~ 30 plants of arbor treelets；
The floristics of each patch plantation determines according to the natural forests advantage group of field investigation；
E. after-culture is carried out to dead seedlings or saplings after transplanting 2-3；After plant 6 years, the plant taller and bigger to individual enters
Row cuts down branch, and space is provided for other species growths；Species non-indigenous are cut selectively, avoid alien species from destroying.
The gap patches basis for estimation is dead and dying trees in patch, is grubbed up, and has substantial amounts of arbor seedling in patch, arbor
Mean stand height less than sample mean stand height 1/4, patch canopy density be less than 15%；The mature forest patch basis for estimation is patch
Interior individual is mostly adult, lacks seedling and treelet, the mean stand height of arbor higher than sample mean stand height 3/4, patch is strongly fragrant
Degree of closing is higher than 60%；Between gap patches and mature forest patch for woods window-mature forest transition patch.
Selected seedling is 2-3 annual plants, highly in 1.2 below m；Treelet is 6-10 annual plants, highly in 1-
3m or so.
Embodiment
First, local natural forests are found according to deserted mountain location, selected natural forests are virgin forest, lack artificial destruction,
It is located at remote place more.System of selection is：1）Positioned at same climate zone；2）Distance is no more than 50km；3）The advantage of natural forests
Layer is tall and big arbor, and the age is typically more than 50 years.
2nd, size and habitat are chosen and sample that the deserted mountain that need to recover is basically identical.Its determination methods is：The gradient basic one
Cause, fluctuate no more than 10 degree；Slope aspect is consistent, and slope aspect is divided into east, the southeast, south, southwest, west, north, northeast, northwest；Soil class
Type is basically identical.Afterwards, patch of the size for the m of 5 m × 5 is divided into by the sample, investigates the species, individual of each patch plant
Body size, the common arbor in the type and each type patch of clearly each patch.The type of patch is with gap patches, woods
Window-mature forest transition patch, mature forest patch are distinguished；Patch partitioning standards are：Gap patches, dead and dying trees, pick in patch be present
Root, there is substantial amounts of arbor seedling in patch, the mean stand height of arbor less than sample mean stand height 1/4, patch canopy density are less than
15%.Mature forest patch, individual is mostly adult in patch, lacks seedling and treelet, the mean stand height of arbor is higher than sample Horizon
The 3/4 of the equal height of tree, patch canopy density are higher than 60%.It is then woods window-mature forest transition patch therebetween.It is determined that patch
On the basis of arbor, the title of arbor in each patch, the diameter of a cross-section of a tree trunk 1.3 meters above the ground, height and quantity are investigated, its frequency of occurrences is calculated, if specific at certain
The frequency of occurrences of patch is higher than 60%, then is common advantage arbor in the patch.
3rd, mountain waste to be restored equally divides the m of the m of size 5 × 5 grid, as shown in Fig. 2 the patch of control natural forests
Specify the type of each patch on deserted mountain；If edge size is less than the m of 5 m × 5, for transition location, without planting any plant
Thing, meeting nature grows some herbaceous plant after a period of time.
4th, different types of plant is planted in different patch, wherein：Gap patches plant 10 ~ 16 plants of arbor seedling；Woods
Window-mature forest transition patch plants 8 ~ 10 plants of arbor seedling and 8 ~ 10 plants of arbor treelets；Ripe patch plants 20 ~ 30 plants of arbor childrens
Tree.Patch interplantation species are determined with natural forests advantage group.
5th, after-culture is carried out to dead seedlings or saplings after transplanting later 2 to 3 years.It is taller and bigger to individual after plant 6 years
Plant carry out cutting down branch, provide space for other species growths；Species non-indigenous are cut selectively, avoid the broken of alien species
It is bad.
It is of the invention economical, conveniently, the drawbacks of overcoming artificial forest or single Planting Patterns, the natural renovation for realizing forest
With bio-diversity conservation.
Claims (3)
1. a kind of method of deserted mountain quick recovering vegetation, its feature comprise the following steps：
A. local natural forests are found according to deserted mountain location；
B. size and habitat are chosen in step and sample that the deserted mountain that need to recover is basically identical, is divided into size 5 by the sample
The m of m × 5 patch is simultaneously distinguished with gap patches, woods window-mature forest transition patch and mature forest patch；Afterwards, each spot is investigated
Common arbor in the species of block implants, Individual Size, quantity and various patch；
C. on the mountain waste recovered is needed, the m of division size 5 m × 5 grid, compare on the clear and definite deserted mountain of patch of natural forests
The type of each patch；
D. different types of plant is planted in different patch, wherein gap patches plant 10 ~ 16 plants of arbor seedling；Woods window-maturation
Woods transition patch plants 8 ~ 10 plants of arbor seedling and 8 ~ 10 plants of arbor treelets；Ripe patch plants 20 ~ 30 plants of arbor treelets；Each
The floristics of patch plantation determines according to the natural forests advantage group of field investigation；
E. after-culture is carried out to dead seedlings or saplings after transplanting 2-3；After plant 6 years, the plant taller and bigger to individual is cut down
Branch, space is provided for other species growths；Species non-indigenous are cut selectively, avoid alien species from destroying.
A kind of 2. method of deserted mountain quick recovering vegetation according to claim 1, it is characterised in that：The gap patches are sentenced
Disconnected foundation is dead and dying trees in patch be present, is grubbed up, and has substantial amounts of arbor seedling in patch, and the mean stand height of arbor is less than sample Horizon
The 1/4 of the equal height of tree, patch canopy density are less than 15%；The mature forest patch basis for estimation is that individual is mostly adult in patch,
Lack seedling and treelet, the mean stand height of arbor higher than sample mean stand height 3/4, patch canopy density are higher than 60%；Between woods window
Between patch and mature forest patch for woods window-mature forest transition patch.
A kind of 3. method of deserted mountain quick recovering vegetation according to claim 1, it is characterised in that：Selected seedling is
2-3 annual plants, highly in below 1.2m；Treelet is 6-10 annual plants, highly in 1-3m.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510899522.4A CN105493828B (en) | 2015-12-09 | 2015-12-09 | A kind of method of deserted mountain quick recovering vegetation |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510899522.4A CN105493828B (en) | 2015-12-09 | 2015-12-09 | A kind of method of deserted mountain quick recovering vegetation |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN105493828A CN105493828A (en) | 2016-04-20 |
| CN105493828B true CN105493828B (en) | 2018-03-30 |
Family
ID=55702449
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201510899522.4A Active CN105493828B (en) | 2015-12-09 | 2015-12-09 | A kind of method of deserted mountain quick recovering vegetation |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN105493828B (en) |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106171745B (en) * | 2016-07-13 | 2019-10-11 | 安庆师范大学 | A kind of method of measurement function group seedling Niche Differentiation on light resource axis |
| CN106472242B (en) * | 2016-10-17 | 2019-08-09 | 安庆师范大学 | A method of promoting the fast quick-recovery of forest using downtree residuum |
| CN106529133B (en) * | 2016-10-25 | 2019-01-25 | 安庆师范大学 | A method of determining minimum population suitable space ecological niche and environmental ecology position |
| CN107347564A (en) * | 2017-08-22 | 2017-11-17 | 贵州省植物园 | Utilize woods window reconstruction Chinese torreya base technology |
| CN116433447B (en) * | 2023-06-12 | 2023-08-18 | 水利部牧区水利科学研究所 | Desert vegetation restoration species configuration method based on community construction mechanism |
Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101699983A (en) * | 2009-09-30 | 2010-05-05 | 甘肃省祁连山水源涵养林研究院 | Method for building drought barren mountain feed shrubbery |
| CN102405813A (en) * | 2011-08-15 | 2012-04-11 | 北京林业大学 | Loess region abrupt slope micro-landform forestation method |
| CN102499003A (en) * | 2011-10-13 | 2012-06-20 | 北京师范大学 | Method for restoring vegetation on barren mountains and sloping fields in arid and semi-arid regions |
| CN102656973A (en) * | 2012-05-15 | 2012-09-12 | 广西大学 | Method for controlling stony desertification and restoring ecosystem of stony desertification region |
| CN103636379A (en) * | 2013-11-19 | 2014-03-19 | 西北农林科技大学 | Method for shrub and grass three-dimensional configuration recovery for barren mountains of semi-arid region |
| CN104082088A (en) * | 2014-07-07 | 2014-10-08 | 孙君策 | Method for afforestation on stony desertification barren mountain |
| CN104170627A (en) * | 2014-08-19 | 2014-12-03 | 张家港市绿岩生态技术有限公司 | Biological anchoring protecting technology applicable to mountains |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2000139113A (en) * | 1998-11-11 | 2000-05-23 | Sumitomo Forestry Co Ltd | Afforestation of deserted land |
-
2015
- 2015-12-09 CN CN201510899522.4A patent/CN105493828B/en active Active
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101699983A (en) * | 2009-09-30 | 2010-05-05 | 甘肃省祁连山水源涵养林研究院 | Method for building drought barren mountain feed shrubbery |
| CN102405813A (en) * | 2011-08-15 | 2012-04-11 | 北京林业大学 | Loess region abrupt slope micro-landform forestation method |
| CN102499003A (en) * | 2011-10-13 | 2012-06-20 | 北京师范大学 | Method for restoring vegetation on barren mountains and sloping fields in arid and semi-arid regions |
| CN102656973A (en) * | 2012-05-15 | 2012-09-12 | 广西大学 | Method for controlling stony desertification and restoring ecosystem of stony desertification region |
| CN103636379A (en) * | 2013-11-19 | 2014-03-19 | 西北农林科技大学 | Method for shrub and grass three-dimensional configuration recovery for barren mountains of semi-arid region |
| CN104082088A (en) * | 2014-07-07 | 2014-10-08 | 孙君策 | Method for afforestation on stony desertification barren mountain |
| CN104170627A (en) * | 2014-08-19 | 2014-12-03 | 张家港市绿岩生态技术有限公司 | Biological anchoring protecting technology applicable to mountains |
Non-Patent Citations (3)
| Title |
|---|
| 太白红杉林斑块结构与群落特征;段仁燕等;《植物生态学报》;20090531;第33卷(第3期);第460-468页 * |
| 林窗干扰与森林群落演替;段仁燕等;《广西植物》;20050930;第25卷(第5期);第419-423页 * |
| 林隙(GAP)干扰研究进展;臧润国;《林业科学》;19980131;第34卷(第1期);第90-98页 * |
Also Published As
| Publication number | Publication date |
|---|---|
| CN105493828A (en) | 2016-04-20 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN105493828B (en) | A kind of method of deserted mountain quick recovering vegetation | |
| CN105875178B (en) | Gastrodia elata f. glauca pseudo-wild cultivating method | |
| CN103283460B (en) | Taxus media cuttage method | |
| CN103477936B (en) | A kind of cultivation method that can make passion fruit batch maturation high yield again | |
| CN103283500B (en) | A kind of cultivation method of yulan magnolia | |
| CN105613205A (en) | Tending method for promoting western sichuan subalpine natural secondary forest to restore by utilizing reserved trees | |
| CN104813889A (en) | Method for planting olive trees in slope | |
| CN105145126A (en) | Wedge-shaped scion grafting propagation method for olea europaea L. | |
| CN104798606A (en) | Method for grafting michelia champaca in top grafting manner by using michelia chapensis dandies as parental stocks | |
| CN106386320A (en) | Early-wood-promoting cultivation method for schima superba forest | |
| Heinsoo et al. | Fine root biomass and production in a Salix viminalis and Salix dasycludos plantation. | |
| CN102318499A (en) | Multilayer tree cultivation method under condition of Zelkova serrata (Thunb.) Makino interplanting | |
| CN105613159A (en) | Planting method of ratoon rice | |
| CN104285642A (en) | Planting method of lavender | |
| CN103053379B (en) | Renewing method for man-planted forest of Chinese pine | |
| CN104221728A (en) | Male torreya grandis branch grafting and afforesting method of torreya grandis | |
| CN106718541B (en) | Method for direct seeding of Yinhua tree for forest culture and management in rocky desertification region | |
| CN109169504B (en) | Method for recovering suitable habitat of pandas | |
| CN103460917B (en) | Plantation method capable of preventing magnolia grandiflora from lodging | |
| CN104737826A (en) | Juicy peach grafting method | |
| CN105519392A (en) | Method for cultivating salt-tolerant peach seedlings | |
| CN104115652A (en) | Method for transplanting ornamental aquatic vegetation water lilies in cold regions | |
| CN106305258A (en) | Kaline soil paper mulberry tree cutting propagation method | |
| CN105284432A (en) | Grafting method for phyllanthus emblica | |
| CN104322241A (en) | Asexual yellow tea cutting seedling raising method |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| CB02 | Change of applicant information |
Address after: 246133 Anhui city of Anqing province Jixian Yixiu District Road No. 1138 Applicant after: Anqing Normal University Address before: 246133 Anhui city of Anqing province Jixian Yixiu District Road No. 1138 Applicant before: Anqing Normal University |
|
| CB02 | Change of applicant information | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant |